PMID-sentid Pub_year Sent_text comp_official_name comp_offsetprotein_name organism prot_offset 23887961-4 2013 Tap water was used as the amniotic fluid. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23732748-0 2013 Highly reactive (<1 min) ratiometric "naked eye" detection of hypochlorite with real application in tap water. Water 107-112 nuclear RNA export factor 1 Homo sapiens 103-106 23732748-3 2013 The chemosensor also showed excellent performance in tap water and the "dip-stick" method. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 23790991-0 2013 Sociodemographic characteristics and beverage intake of children who drink tap water. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 23790991-1 2013 BACKGROUND: Tap water provides a calorie-free, no-cost, environmentally friendly beverage option, yet only some youth drink it. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 23790991-2 2013 PURPOSE: To examine sociodemographic characteristics, weight status, and beverage intake of those aged 1-19 years who drink tap water. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 23790991-3 2013 METHODS: National Health and Nutrition Examination Survey data (2005-2010) were used to examine factors associated with tap water consumption. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 23790991-5 2013 RESULTS: Tap water consumption was more prevalent among school-aged children (OR=1.85, 95% CI=1.47, 2.33, for those aged 6-11 years; OR=1.85, 95% CI=1.32, 2.59, for those aged 12-19 years) as compared to those aged 1-2 years. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 23790991-7 2013 Tap water consumers drank more fluid (52.5 vs 48.0 ounces, p<0.01); more plain water (20.1 vs 15.2 ounces, p<0.01); and less juice (3.6 vs 5.2 ounces, p<0.01) than nonconsumers. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23790991-7 2013 Tap water consumers drank more fluid (52.5 vs 48.0 ounces, p<0.01); more plain water (20.1 vs 15.2 ounces, p<0.01); and less juice (3.6 vs 5.2 ounces, p<0.01) than nonconsumers. Water 82-87 nuclear RNA export factor 1 Homo sapiens 0-3 23980306-0 2013 Tap water iontophoresis versus glycopyrrolate iontophoresis. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23980307-0 2013 Tap water iontophoresis versus glycopyrrolate iontophoresis. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23665928-0 2013 Pharmaceuticals in tap water: human health risk assessment and proposed monitoring framework in China. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 23665928-1 2013 BACKGROUND: Pharmaceuticals are known to contaminate tap water worldwide, but the relevant human health risks have not been assessed in China. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 23665928-2 2013 OBJECTIVES: We monitored 32 pharmaceuticals in Chinese tap water and evaluated the life-long human health risks of exposure in order to provide information for future prioritization and risk management. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 23665928-9 2013 CONCLUSION: Chinese tap water is an additional route of human exposure to pharmaceuticals, particularly for dimetridazole, although the risk to human health is low based on current toxicity data. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 23702591-0 2013 Bacterial community of iron tubercles from a drinking water distribution system and its occurrence in stagnant tap water. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 23702591-3 2013 Comparison of the bacterial community composition of pipe tubercles with that of stagnant tap water samples based on a denaturing gradient gel electrophoresis analysis of the 16S rRNA gene revealed that the communities were related. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 23702591-8 2013 Inorganic contaminants at low levels, including Al, Mn, Zn, Pb, Cr, Cu, and Ni, were detected in tubercles and were concentrated in particulates from tap water following the release of iron during stagnation. Water 154-159 nuclear RNA export factor 1 Homo sapiens 150-153 23321855-8 2013 In households with tap water As <=10 p.p.b., over 93% of total arsenic exposure was attributable to diet. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 23853479-7 2013 The tap water was the only common exposure of the patients. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 23853479-12 2013 It is presumed that the tap water was contaminated by a sewage leak from the aged pipelines. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 23503193-0 2013 Clostridium difficile contamination of public tap water distribution system during a waterborne outbreak in Finland. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 23503193-10 2013 CONCLUSIONS: Our findings demonstrate for the first time C. difficile contamination of a tap water distribution system and waterborne transmission of toxigenic C. difficile seems possible. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 23684468-7 2013 Finally, the system was applied to an extended automated analysis of Hobart Southern Water tap water for a period of 48 h. The overall repeatability of the migration times of a 14 analyte standard sample was less than 0.74% under laboratory conditions. Water 85-90 nuclear RNA export factor 1 Homo sapiens 91-94 23684468-7 2013 Finally, the system was applied to an extended automated analysis of Hobart Southern Water tap water for a period of 48 h. The overall repeatability of the migration times of a 14 analyte standard sample was less than 0.74% under laboratory conditions. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 23597372-9 2013 Those with lower levels of education were significantly less likely to drink tap water, as were their children, and significantly less likely to have had a dental appointment in the preceding past 12 months. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 21794921-10 2013 Meanwhile, a three-week test of using polycarbonate bottles and ceramic cups to drink bottled water and boiled tap-water was carried out among 12 graduate students of 25 years old. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 23782914-10 2013 In general, tap water represented 60% of drinking water volume whereas bottled water represented 40%. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 23782914-12 2013 Plain water consumption (bottled and tap) tended to be associated with higher incomes. Water 6-11 nuclear RNA export factor 1 Homo sapiens 37-40 22968229-7 2013 We conclude that prolonged contact with lead plumbing can increase the lead content in tap water with subsequent increase in lead burden in infant fed formula and infant blood. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 22968229-10 2013 Capsule: Prolonged contact with lead plumbing can increase the lead content in tap water with subsequent increase in lead burden in infant fed formula and infant blood. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 23305757-9 2013 In contrast, tap water use in households was a protective factor against any helminth infection (i.e. T. trichiura OR=0.6, 95% CI 0.4-0.9). Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 23555172-7 2013 RESULTS: By univariate analysis, the variables predictive of UC included feeling stress, light and heavy alcoholic drinking, spicy food, sugar consumption and infectious diarrhea, while heavy tea intake and tap water consumption were protective against UC. Water 211-216 nuclear RNA export factor 1 Homo sapiens 207-210 23552011-2 2013 Tap water iontophoresis has long been known to inhibit sweat production. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23552011-8 2013 In conclusion, tap water iontophoresis is a safe and effective treatment of palmar and plantar hyperhidrosis when used on Monday, Wednesday, and Friday for 4 weeks. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 23361354-6 2013 The change from distilled water to tap or simulated sea water results in a lower hydrogen evolution rate of about 50%. Water 26-31 nuclear RNA export factor 1 Homo sapiens 35-38 23392300-0 2013 Acanthamoeba keratitis associated with tap water use during contact lens cleaning: manufacturer guidelines need to change. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 24003692-2 2013 Since "tthe middle of 2007 the concentration of chloroform and other TGM in tests of tap water were established to be defined at levels steadily below hygienic maximum concentration limits. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 23485542-0 2013 Rapid self-infusion of tap water. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 23485542-1 2013 Intravenous self-infusion of tap water has never been reported in the literature.&nbsp; We present a 24-year-old healthy man who self-administered 2.5 L of tap water over 2 hours and developed acute illness including fever, change of mental status, acute hemolysis, low-grade disseminated intravascular coagulation, and acute kidney injury.&nbsp;&nbsp; Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 23485542-1 2013 Intravenous self-infusion of tap water has never been reported in the literature.&nbsp; We present a 24-year-old healthy man who self-administered 2.5 L of tap water over 2 hours and developed acute illness including fever, change of mental status, acute hemolysis, low-grade disseminated intravascular coagulation, and acute kidney injury.&nbsp;&nbsp; Water 33-38 nuclear RNA export factor 1 Homo sapiens 160-163 23485542-1 2013 Intravenous self-infusion of tap water has never been reported in the literature.&nbsp; We present a 24-year-old healthy man who self-administered 2.5 L of tap water over 2 hours and developed acute illness including fever, change of mental status, acute hemolysis, low-grade disseminated intravascular coagulation, and acute kidney injury.&nbsp;&nbsp; Water 164-169 nuclear RNA export factor 1 Homo sapiens 29-32 23485542-1 2013 Intravenous self-infusion of tap water has never been reported in the literature.&nbsp; We present a 24-year-old healthy man who self-administered 2.5 L of tap water over 2 hours and developed acute illness including fever, change of mental status, acute hemolysis, low-grade disseminated intravascular coagulation, and acute kidney injury.&nbsp;&nbsp; Water 164-169 nuclear RNA export factor 1 Homo sapiens 160-163 23514985-0 2013 Incidence of hot tap water scalds after the introduction of regulations in Ontario. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 23514985-7 2013 There were a total of 6952 hot tap water scald cases in Ontario, including 408 hospitalizations in the 8-year period. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 23618141-3 2013 Thus, we built a flow-through calibration system containing tap water spiked with 56 organic micropollutants (alkylphenols and phenols, hormones, pesticides, pharmaceuticals, UV filter). Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 23618141-5 2013 Tap water micropollutant concentrations and additional parameters (temperature, pH, conductivity, dissolved organic carbon, flow velocities) were kept constant and controlled throughout the calibration experiment. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23618152-2 2013 Municipal tap water was used instead of conventional phosphate buffer as blank solution to avoid phosphate pollution. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 23618152-3 2013 The background organic compounds in municipal tap water were taken into account and they were validated to result in negative deviation to accuracy. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 23618152-4 2013 The microbial endogenous respiration was experimentally validated to be sensitive to salt ionic strength, and municipal tap water as blank was thought to generate positive deviation to accuracy. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 23487180-6 2013 As a possible application of the acetate probes, hydrazine signaling in tap water was tested. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 23687491-2 2013 Although the pathophysiology of PPH remains unknown, some treatments, including topical aluminum chloride (AC) and tap water iontophoresis (TWI), are effective at suppressing the perspiration. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 23348716-1 2013 Nanoaggregates of a supramolecular ensemble of triphenylene derivative 3 and Cu(2+) ions exhibit "turn-on" response towards CN(-) ions in an aqueous medium and can detect the trace amount of inorganic cyanide ions (NaCN) in tap water and blood serum milieu. Water 228-233 nuclear RNA export factor 1 Homo sapiens 224-227 23521454-2 2013 The water flush consists of having patients drink tap water at end esophagography in an attempt to clear the standing barium column. Water 4-9 nuclear RNA export factor 1 Homo sapiens 50-53 23408641-11 2013 Tap water, seawater, and river water samples were successfully analyzed for the existence of CPs using the proposed method and satisfactory results were obtained. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 24159533-5 2013 RESULTS: To prevent typhoid fever in the community, it is necessary to provide clean tap water service to 35.5% of the population, with an individual requiring 173 L of clean water daily. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 23398240-7 2013 For a 0.6 M NaCl solution and tap water, the water flux and corresponding maximum power density were 3.7 L m(-2)h(-1) and 1.0 W/m(2) respectively at a hydraulic pressure difference of 9.8 bar. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 23398240-7 2013 For a 0.6 M NaCl solution and tap water, the water flux and corresponding maximum power density were 3.7 L m(-2)h(-1) and 1.0 W/m(2) respectively at a hydraulic pressure difference of 9.8 bar. Water 45-50 nuclear RNA export factor 1 Homo sapiens 30-33 23510408-7 2013 Based on the results of the multivariate analysis, consumption of tap water was the only statistically significant independent risk factor of gastroenteritis (RR = 2.34, 95% C.I. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 23188481-7 2013 Water sources such as tap, mobile stations (explained in a following section), and well water contributed to 24%, 14%, and 2% of an individual"s daily water consumption pattern, respectively. Water 0-5 nuclear RNA export factor 1 Homo sapiens 22-25 23188481-8 2013 Average daily potable water use of both bottled and tap water by individuals consisted of 65% drinking-water, while the remaining 35% was water used for preparing cold and hot beverages, such as, tea, coffee, and juices. Water 22-27 nuclear RNA export factor 1 Homo sapiens 52-55 23188481-8 2013 Average daily potable water use of both bottled and tap water by individuals consisted of 65% drinking-water, while the remaining 35% was water used for preparing cold and hot beverages, such as, tea, coffee, and juices. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 23188481-8 2013 Average daily potable water use of both bottled and tap water by individuals consisted of 65% drinking-water, while the remaining 35% was water used for preparing cold and hot beverages, such as, tea, coffee, and juices. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 23188481-8 2013 Average daily potable water use of both bottled and tap water by individuals consisted of 65% drinking-water, while the remaining 35% was water used for preparing cold and hot beverages, such as, tea, coffee, and juices. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 23188482-10 2013 Three food groups were negatively associated with urinary perchlorate: grain products for children; sugars, sweets, and beverages for adolescents; and home tap water for adults. Water 160-165 nuclear RNA export factor 1 Homo sapiens 156-159 23188482-11 2013 In a separate model, however, perchlorate consumed via home tap water contributed significantly to adult urinary perchlorate: 2.11E-4 ng ClO(4)(-)/ml per ng perchlorate in tap water consumed. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 23188482-11 2013 In a separate model, however, perchlorate consumed via home tap water contributed significantly to adult urinary perchlorate: 2.11E-4 ng ClO(4)(-)/ml per ng perchlorate in tap water consumed. Water 64-69 nuclear RNA export factor 1 Homo sapiens 172-175 23188482-11 2013 In a separate model, however, perchlorate consumed via home tap water contributed significantly to adult urinary perchlorate: 2.11E-4 ng ClO(4)(-)/ml per ng perchlorate in tap water consumed. Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 23188482-12 2013 In a nationally representative sample of the United States 6-84 YO, diet and tap water contributed significantly to urinary perchlorate, with diet contributing substantially more than tap water. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 23188482-12 2013 In a nationally representative sample of the United States 6-84 YO, diet and tap water contributed significantly to urinary perchlorate, with diet contributing substantially more than tap water. Water 188-193 nuclear RNA export factor 1 Homo sapiens 184-187 23427143-3 2013 Polycyclic aromatic hydrocarbons are well known for strong carcinogenicity and thus a severe concentration control is required for drinking water and/or river water, which is the main resource of tap water. Water 140-145 nuclear RNA export factor 1 Homo sapiens 196-199 23428553-4 2013 Results of raw water samples from the study area showed deterioration in bacteriological quality of water moved from source to the household; from 3 to 36 cfu/100 mL for tap water and 75 to 126 cfu/100 mL for spring water, using thermotolerant coliforms (TTCs) as indicator microorganisms. Water 15-20 nuclear RNA export factor 1 Homo sapiens 170-173 23428553-4 2013 Results of raw water samples from the study area showed deterioration in bacteriological quality of water moved from source to the household; from 3 to 36 cfu/100 mL for tap water and 75 to 126 cfu/100 mL for spring water, using thermotolerant coliforms (TTCs) as indicator microorganisms. Water 100-105 nuclear RNA export factor 1 Homo sapiens 170-173 23428553-4 2013 Results of raw water samples from the study area showed deterioration in bacteriological quality of water moved from source to the household; from 3 to 36 cfu/100 mL for tap water and 75 to 126 cfu/100 mL for spring water, using thermotolerant coliforms (TTCs) as indicator microorganisms. Water 100-105 nuclear RNA export factor 1 Homo sapiens 170-173 23428553-4 2013 Results of raw water samples from the study area showed deterioration in bacteriological quality of water moved from source to the household; from 3 to 36 cfu/100 mL for tap water and 75 to 126 cfu/100 mL for spring water, using thermotolerant coliforms (TTCs) as indicator microorganisms. Water 100-105 nuclear RNA export factor 1 Homo sapiens 170-173 23391895-6 2013 A majority of residents believed that dioxins can be found in river water that has been filtered to completely remove all particulates, well water, and even city tap water, beliefs which are incongruous with the hydrophobic nature of dioxins. Water 68-73 nuclear RNA export factor 1 Homo sapiens 162-165 23167710-8 2013 CONCLUSIONS: This study successfully developed and tested a microarray-based assay that can specifically detect faecal indicator bacteria and human pathogens in tap water. Water 165-170 nuclear RNA export factor 1 Homo sapiens 161-164 23590030-8 2013 All surfaces cleaned with tap water or tap water containing detergent revealed presence of both MRSA and XDR A. baumannii. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 23193539-2 2013 It was used successfully for the amperometric detection of iodide in aqueous solution and tap water after a pre-concentration step, with a detection limit of 1.5 x 10(-7) M. This electrode has an excellent stability. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 22986031-5 2013 Glycerin diluted with tap water followed by a tap water flush is our preferred irrigation protocol. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 22986031-9 2013 Patients using glycerin instilled a median of 30 ml (mean 29) glycerin and 50 ml (131) tap water. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 23590030-11 2013 However the amounts of bacteria on the surfaces cleaned with PAL disinfectant wipes were less than those cleaned with tap water containing detergent. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 23590030-13 2013 CONCLUSION: Virusolve+ disinfectant wipes were more effective than tap water; tap water containing detergent and PAL disinfectant wipes for decontamination of bacteria inoculated on patients environmental and medical equipment surfaces at Siriraj Hospital. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 23697178-7 2013 This method was applied to the analysis of the surface water samples from the Dalian tap water and the Liaohe River estuary. Water 55-60 nuclear RNA export factor 1 Homo sapiens 85-88 23697178-7 2013 This method was applied to the analysis of the surface water samples from the Dalian tap water and the Liaohe River estuary. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 23312321-5 2013 The AMPAs could be determined in tap water with limits of detection of 0.01-0.07 mug L(-1) with the [M-H](-) ions extracted at an accuracy of +-5 mDa. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 23273631-9 2013 The method was applied to the analysis of thirteen water samples from Tianjin, China, including wastewater, tap water, surface water, and groundwater. Water 51-56 nuclear RNA export factor 1 Homo sapiens 108-111 24069842-10 2013 However, tap water in some areas also seems to have a high content of endotoxin, and this too should be considered when deliberating the protection of the airways of workers. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 23200507-0 2013 Influence of minerals on the taste of bottled and tap water: a chemometric approach. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 23200507-8 2013 The preferred bottled and tap water samples were associated with moderate (relatively to the parameters mean values) contents of total dissolved solids and with relatively high concentrations of HCO3-, SO42-, Ca2+ and Mg2+ as well as with relatively high pH values. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 24334980-7 2013 Spike tests with 2 mug (10 mug L(-1)) of DPAA, PAA, and iAs in 200 mL of tap water and bottled drinking water showed good recoveries (96.1-103.8%). Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 23186671-4 2013 The concentration of total organic carbon in the reactor discharge was very similar to the content of organic matter in tap water. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 23476675-0 2013 The effect of different boiling and filtering devices on the concentration of disinfection by-products in tap water. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 22939265-0 2013 Presence and sources of anthropogenic perfluoroalkyl acids in high-consumption tap-water based beverages. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 22939265-1 2013 This study investigates the presence and sources of perfluorinated alkyl acids (PFAAs) in tap water and corresponding tap-water based beverages such as coffee and cola collected in the city of Amsterdam, The Netherlands. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 22939265-1 2013 This study investigates the presence and sources of perfluorinated alkyl acids (PFAAs) in tap water and corresponding tap-water based beverages such as coffee and cola collected in the city of Amsterdam, The Netherlands. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 22939265-2 2013 Exposure pathways studies have shown that low concentrations of PFAA in tap water already may pose a high contribution to daily human exposure. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 22939265-3 2013 Tap water samples (n=4) had higher concentrations of PFAAs than the corresponding post-mixed cola (n=4). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 22939265-4 2013 The lower PFAA levels in the cola were attributed to the pre-treatment of tap water in the mixing machines and dilution with cola syrup. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 22939265-6 2013 The concentrations of PFHpA, PFOA and non branched PFOS were found to be significantly higher in manually (self) brewed coffee than in the corresponding tap water (n=4). Water 157-162 nuclear RNA export factor 1 Homo sapiens 153-156 22939265-13 2013 Tap-water based beverages will possibly be an additional source of human exposure to PFAAs and need to be considered in exposure modeling. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23805697-1 2013 Due to intensive anthropogenic pollution of water environment generally accepted indicators of epidemic security of water bodies--common bacteria (CB) and thermotolerant coliform bacteria (TCB) do not always permit to obtain an objective characterization of bacterial contamination of tap water. Water 44-49 nuclear RNA export factor 1 Homo sapiens 285-288 23805697-3 2013 In monitoring for bacterial quality of tap water it is advisable to determine glucose positive coliform bacteria, that will provide the relevance of estimation of the epidemiological safety of water use. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 23805697-4 2013 According to the method developed by the authors the calculation of the index of population risk of acute intestinal infections (AHI) occurrence in dependence on the quality of tap water in Azov and Tsimlyansk towns. Water 181-186 nuclear RNA export factor 1 Homo sapiens 177-180 23486733-8 2013 The least concentration was seen in tap water. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 23043333-0 2013 Perfluoroalkyl and polyfluoroalkyl substances (PFASs) in mineral water and tap water. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 23476675-2 2013 Filtering and boiling tap water can lead to changes in the DBP concentrations and modify the exposure through ingestion. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 23416590-4 2013 Moreover, NB water retains its effectiveness even after storage for 7 d. Finally, NB water produced onsite from tap water was found to be effective for removal of radioactive Cs from gravel conglomerate in Fukushima, Japan. Water 13-18 nuclear RNA export factor 1 Homo sapiens 112-115 23994849-2 2013 It was found out that Moscow tap water contains little fluoride, the difference between districts and okrugs is of no consequence. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 23416590-4 2013 Moreover, NB water retains its effectiveness even after storage for 7 d. Finally, NB water produced onsite from tap water was found to be effective for removal of radioactive Cs from gravel conglomerate in Fukushima, Japan. Water 85-90 nuclear RNA export factor 1 Homo sapiens 112-115 23416590-4 2013 Moreover, NB water retains its effectiveness even after storage for 7 d. Finally, NB water produced onsite from tap water was found to be effective for removal of radioactive Cs from gravel conglomerate in Fukushima, Japan. Water 85-90 nuclear RNA export factor 1 Homo sapiens 112-115 23128290-5 2012 Among children in an urban slum, rate of diarrhea/1,000 child-days varied significantly by primary water source: 8.13 for tap water, 3.60 for bottled water, and 3.97 for water kiosks. Water 99-104 nuclear RNA export factor 1 Homo sapiens 122-125 22980895-1 2012 Mineral, spring and tap water samples of different geographical origins (7 classes) were distinguished by various methods, such as sensory evaluation, electronic tongue measurement, inductively coupled plasma atomic emission spectroscopy and ion chromatography. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 23128290-6 2012 In multivariable Poisson regression analysis, diarrhea risk remained significantly lower among water kiosk users (adjusted rate ratio [RR] = 0.49, 95% confidence interval [CI] = 0.29-0.83) and bottled water users (adjusted RR = 0.45, 95% CI = 0.21-0.97), compared with tap water users. Water 95-100 nuclear RNA export factor 1 Homo sapiens 269-272 23231900-8 2012 The LIBS spectra of tap water were recorded using the pre-concentration method and are discussed in comparison with the results from inductively coupled plasma atomic emission spectroscopy (ICP-AES). Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 23231900-9 2012 We could observe strong emission lines of Ca, Mg, K, Cu, and Sr in the tap water, of which concentrations were determined to be 6.3, 1.3, 1.1, 0.64, and 0.046 ppm, respectively, by ICP-AES. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 22928956-8 2012 Bivariate analyses pointed to significantly increased nickel excretion with increasing age, ingestion of dietary supplements, drinking of stagnant tap water, and consumption of nickel-rich food. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 22928956-14 2012 The use of stagnant tap water and consumption of nickel-rich food contribute to the total load. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 23241465-6 2012 RESULTS: Following an order to boil water, 87.5% of respondents refrained from drinking unboiled tap water. Water 36-41 nuclear RNA export factor 1 Homo sapiens 97-100 23021792-6 2012 Ground and tap water samples analyzed were also contaminated with pharmaceuticals. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 23040562-0 2012 Comparison of the rates of phenol advanced oxidation in deionized and tap water within a dielectric barrier discharge reactor. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 23040562-3 2012 Interestingly, a significant rate increase was found in tap with respect to milliQ water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 56-59 23040562-5 2012 The same increase in efficiency as observed in tap water was instead obtained when phenol was treated in solutions containing bicarbonate anions in the same concentration as present in tap water, an effect attributed to buffering of the solution pH. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 23040562-5 2012 The same increase in efficiency as observed in tap water was instead obtained when phenol was treated in solutions containing bicarbonate anions in the same concentration as present in tap water, an effect attributed to buffering of the solution pH. Water 189-194 nuclear RNA export factor 1 Homo sapiens 47-50 23040562-5 2012 The same increase in efficiency as observed in tap water was instead obtained when phenol was treated in solutions containing bicarbonate anions in the same concentration as present in tap water, an effect attributed to buffering of the solution pH. Water 189-194 nuclear RNA export factor 1 Homo sapiens 185-188 23270054-0 2012 [Tap water for wound cleansing. Water 5-10 nuclear RNA export factor 1 Homo sapiens 1-4 23176729-3 2012 Residual ethanolamine was subsequently quantified by absorbance at 420 nm after reaction with 2,4,6-trinitrobenzenesulfonic acid (TNBS) at pH 9.2 for 15 min at 55 C followed by cooling with tap water. Water 194-199 nuclear RNA export factor 1 Homo sapiens 190-193 22944202-9 2012 A quantitative microbial risk assessment (QMRA) model with Monte Carlo simulations adopted by the World Health Organization (WHO) found the use of tap water and treated wastewater to be associated with risks that exceed permissible limits as proposed by the WHO (1.0 x 10(-3) disease risk per person per year) for the accidental ingestion of irrigated soil by farmers (Crete: 0.67 pppy and Italy: 1.0 pppy). Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 22805349-5 2012 In both the experiments, treated animals were exposed to a 10% ethanol solution as the single drinking source for 4 weeks, while untreated animals were exposed to tap water over the same period. Water 167-172 nuclear RNA export factor 1 Homo sapiens 163-166 23026855-3 2012 The proposed method is very specific to Cu(ii), with tolerance against at least 100-fold amounts of other environmentally relevant metal ions except for Hg(ii) (25-fold), and was successfully applied to the detection of trace Cu(ii) in tap water, river water, and treated wastewater, and results agreed well with that determined by inductively coupled plasma-mass spectrometry (ICP-MS). Water 240-245 nuclear RNA export factor 1 Homo sapiens 236-239 23026855-3 2012 The proposed method is very specific to Cu(ii), with tolerance against at least 100-fold amounts of other environmentally relevant metal ions except for Hg(ii) (25-fold), and was successfully applied to the detection of trace Cu(ii) in tap water, river water, and treated wastewater, and results agreed well with that determined by inductively coupled plasma-mass spectrometry (ICP-MS). Water 253-258 nuclear RNA export factor 1 Homo sapiens 236-239 23458011-3 2012 In monitoring for bacterial quality of tap water it is advisable to determine glucose positive coliform bacteria, that will provide the relevance of estimation of the epidemiological safety of water use. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 23229609-2 2012 An optimal water treatment system includes tap water pretreatment and a double reverse osmosis process. Water 11-16 nuclear RNA export factor 1 Homo sapiens 43-46 23458011-4 2012 According to the method developed by the authors the calculation of the index of population risk of acute intestinal infections occurrence in dependence on the quality of tap water in Azov and Tsimlyansk towns. Water 175-180 nuclear RNA export factor 1 Homo sapiens 171-174 22297087-11 2012 After rinsing with tap water, the YM decreased to 95% of the fresh condition value (377.4N/mm(2), SD 144.5N/mm(2), non-significant change from fresh). Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 23041812-12 2012 None of the environmental cultures grew M. mucogenicum except for the tap water from 2 rooms, 1 of which had a faucet aerator. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 23041812-13 2012 The 4 patient isolates and the tap water isolate from the room with the aerator were found to have greater than 98.5% similarity. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 23041812-15 2012 CONCLUSION: The source of the M. mucogenicum bacteremia outbreak was identified by genotyping analysis as the clinic tap water supply. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 23064864-8 2012 At the same time, out of 50, total aerobic mesophilic bacteria were isolated in 34 (68 %), fungi were isolated in 15 (30 %) and free living amoebae were isolated in 15 (30 %) domestic tap water samples. Water 188-193 nuclear RNA export factor 1 Homo sapiens 184-187 23006249-13 2012 Tap water users also had higher-quality source water, suggesting that disuse is not necessarily negative and monitoring of water quality can aid decision-making about continued use. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23006249-13 2012 Tap water users also had higher-quality source water, suggesting that disuse is not necessarily negative and monitoring of water quality can aid decision-making about continued use. Water 47-52 nuclear RNA export factor 1 Homo sapiens 0-3 23006249-13 2012 Tap water users also had higher-quality source water, suggesting that disuse is not necessarily negative and monitoring of water quality can aid decision-making about continued use. Water 47-52 nuclear RNA export factor 1 Homo sapiens 0-3 22794084-7 2012 In typical conditions, the use of public network water directly from the tap results in the best scenario, while if water is withdrawn from public fountains, its further transportation by private car can involve significant impacts. Water 49-54 nuclear RNA export factor 1 Homo sapiens 73-76 22863027-0 2012 Impact of water treatment on the contribution of faucets to dissolved and particulate lead release at the tap. Water 10-15 nuclear RNA export factor 1 Homo sapiens 106-109 22840474-6 2012 Common invertebrates in treated water and in tap water were Rotifera (<1 mm) and nematode worms (Nematoda, <2 mm). Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 22863027-1 2012 A field study was performed in a building complex to investigate the extent and sources of lead (Pb) release in tap water and brass material was found to be the main contributor in the very first draw (250 mL). Water 116-121 nuclear RNA export factor 1 Homo sapiens 112-115 22198003-6 2012 32% washed their hands before attending each client, 59% cleaned instruments with disinfectant between clients, 96.1% washed razors with tap water before use on a new client, 92.6% also washed their razors with an antiseptic solution after every use, 87% used a new blade on new clients and 55% used disinfectants for skin cuts. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 22882826-6 2012 The detection limit of the method was 0.08 mug L(-1) HCB for a tap-water sample. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 23487846-0 2012 Unknown quantity: regulating radionuclides in tap water. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 22967539-0 2012 Portable mercury sensor for tap water using surface plasmon resonance of immobilized gold nanorods. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 22967539-1 2012 The surface plasmon resonance of surface immobilized gold nanorods (Au NRs) was used to quantify mercury in tap water. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 22967539-5 2012 The possibility to using glass substrates with immobilized Au NRs is a significant step towards the analysis of mercury in tap water flows at this low concentration level. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 22270589-5 2012 This study showed that measured endotoxin concentrations in tap drinking water varied from 2.4 to 33.8 EU/ml with the average endotoxin concentration of 14.2 EU/ml. Water 73-78 nuclear RNA export factor 1 Homo sapiens 60-63 22270589-7 2012 The average concentration of endotoxin in bottled water is 13.5 % of the average concentration of endotoxin in tap drinking water. Water 124-129 nuclear RNA export factor 1 Homo sapiens 111-114 22270589-8 2012 This experimental investigation has proved that drinking bottled water has less endotoxin as compared to tap water in Kuwait. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 22898169-0 2012 Getting back on tap: the policy context and cost of ensuring access to low-cost drinking water in Massachusetts schools. Water 89-94 nuclear RNA export factor 1 Homo sapiens 16-19 22898169-10 2012 Water-provision strategies relying on tap water are more economical than bottled water in the long term. Water 0-5 nuclear RNA export factor 1 Homo sapiens 38-41 22898169-10 2012 Water-provision strategies relying on tap water are more economical than bottled water in the long term. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 22038315-4 2012 Leptin levels significantly increased immediately after WWB with tap water and ISCO(2) (both P < 0.05), and remained significantly higher than those at baseline even 30 minutes after WWB with tap water (P < 0.05). Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 22038315-4 2012 Leptin levels significantly increased immediately after WWB with tap water and ISCO(2) (both P < 0.05), and remained significantly higher than those at baseline even 30 minutes after WWB with tap water (P < 0.05). Water 199-204 nuclear RNA export factor 1 Homo sapiens 195-198 22038315-7 2012 The sublingual temperature rose significantly after 10 minutes of WWB with tap water (0.96 +- 0.16 C relative to baseline, P < 0.01) and after the same duration of WWB with ISCO(2) (1.24 +- 0.34 C relative to baseline, P < 0.01). Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 22402780-0 2012 National screening study on 10 perfluorinated compounds in raw and treated tap water in France. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 22119284-3 2012 We collected daily samples of air, fallout deposition, and tap water starting directly after the incident and measured their radioactivity. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 22119284-8 2012 Radioactivity in tap water caused by the accident was detected several days after detection of radioactivity in fallout in the area. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 22960489-9 2012 Although males reported higher daily tap-water consumption rates than females, these differences were insignificant, so separate consumption distributions are not considered necessary. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 22960489-10 2012 A log-normal distribution provides the most adequate fit for daily tap-water intake (ml day(-1)) within both datasets. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 22939141-7 2012 The electrode was tested on real samples (tap water spiked with Zn(2+), food supplement) with a good recovery by applying the standard addition method. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 22677052-6 2012 Filters with deposited Ag/Al(OH)(3) mesoporous nanocomposite film have great potential for application as antimicrobial filters for tap water purification, wastewater treatment, and other bio-related applications. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 22706888-0 2012 Determination of fluoride in tap water in Morocco using a direct electrochemical method. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 22706888-1 2012 This study aimed to analyze the fluoride concentration in tap drinking water in different cities of Morocco using an electrochemical ion-selective method. Water 71-76 nuclear RNA export factor 1 Homo sapiens 58-61 22883355-11 2012 Tap water was the main source of water consumed at home by the majority of children (77.8%). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 22883355-11 2012 Tap water was the main source of water consumed at home by the majority of children (77.8%). Water 33-38 nuclear RNA export factor 1 Homo sapiens 0-3 22658390-3 2012 DESIGN: Prospective feasibility study of immediate colonoscopy after tap-water enema without oral bowel preparation, aided by water-jet pumps and mechanical suction devices in patients admitted to the intensive care unit with a primary diagnosis of severe lower GI bleeding. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 26523086-4 2012 For Cryptosporidum, oocyst recovery in tap water was significantly higher for ultrafiltration (68%) versus the capsule filter (37%); ultrafiltration recovered 65% of oocysts in surface water versus 61% for the capsule filter. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 22385125-8 2012 During the outbreak investigation a water boiling order was enforced, as tap water was considered a potential source. Water 36-41 nuclear RNA export factor 1 Homo sapiens 73-76 22385125-12 2012 Among these patients, the development of diarrhoea was associated with drinking tap water with a dose-response pattern (linear increase by 2 glasses: odds ratio 1.40, 95% confidence interval 1.16-1.70). Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 22385125-14 2012 CONCLUSIONS: These findings indicated a point source contamination of tap water with a single clone of C. jejuni which likely occurred on 12-13 May. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 22411733-10 2012 Of the patients using bottled, distilled, or boiled tap water, 65% described the process as "mildly" or "moderately" inconvenient. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 22551852-11 2012 The GM of lead concentrations in tap water was below 1 mug/L; 58% of concentrations were lower than 1 mug/L and 2.9% were higher than or equal to 10 mug/L. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 22411733-0 2012 Tap water or "sterile" water for sinus irrigations: what are our patients using? Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 22411733-2 2012 Due to potential concerns regarding infection, patients are commonly recommended to use distilled, bottled, or boiled tap water when mixing these solutions. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 22411733-12 2012 CONCLUSION: Despite standardized instructions for the preparation of saline irrigation solutions, many patients use untreated tap water. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 22411733-3 2012 Anecdotally, patients frequently inform otolaryngologists that they use tap water for irrigation preparation. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 22411733-9 2012 However, tap water was used by 48% and the most common reason cited for using tap water was convenience. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 22708830-9 2012 RESULTS: The percentage of tap water consumption remained relatively stable and a preferred choice, with 58.99% in 2001 and 58.25% in 2011. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 22339887-5 2012 RESULTS: The estimate for the percentage of individuals who reported total drinking water in 2005-2006 was significantly (P < 0 0000) smaller (76 9 %) than that for 2003-2004 (87 1 %), attributable to a lower percentage reporting tap water (54 1 % in 2005-2006 v. 67 0 % in 2003-2004; P = 0 0001). Water 84-89 nuclear RNA export factor 1 Homo sapiens 233-236 21649853-7 2012 The results of this review indicate that patients who underwent irrigation with tap water immediately following alkali burns at the scene of injury had significantly better clinical and ocular outcomes. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 21649853-12 2012 IMPLICATIONS AND CONCLUSIONS: As prompt eye irrigation with tap water immediately after alkali burns had better outcomes, it would be important to commence eye irrigation immediately after burns are sustained. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 22708830-15 2012 CONCLUSIONS: Personal health belief, housing condition, age, personal income, education, taste and if worm ever founded in tap water affected domestic drinking water choices in Shanghai. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 22537920-2 2012 The photocatalytic activity and the dissolution of Ag(+) from different catalysts were investigated during the photodegradation of 2-chlorophenol (2-CP) and phenol in ultrapure water and tap water with visible-light irradiation. Water 191-196 nuclear RNA export factor 1 Homo sapiens 187-190 22537920-4 2012 Ag-AgBr/MA-Ti1 was considered the better catalyst for practical applications because its Ag(+) dissolution was minimal (0.4 mg L(-1) in ultrapure water and 5 mug L(-1) in tap water), although its photoactivity was slightly less than that of Ag-AgBr/MA. Water 175-180 nuclear RNA export factor 1 Homo sapiens 171-174 22540891-0 2012 Pb particles from tap water: bioaccessibility and contribution to child exposure. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 22100424-3 2012 Evidence suggests that reducing tap water temperatures in social (public) housing through "passive" means is effective in reducing risk. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 22483878-5 2012 The modified electrode was applied to detection hydroxylamine in the tap water, and the average recovery for the standards added was 96.0%. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 22660258-0 2012 [Tap water iontophoresis]. Water 5-10 nuclear RNA export factor 1 Homo sapiens 1-4 22660258-1 2012 Since 1968, tap water iontophoresis has been employed as the method of choice for treating palmoplantar hyperhidrosis. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 22660258-3 2012 Tap water iontophoresis also can extend symptom -free intervals in dyshidrotic palmar eczema. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 22717747-0 2012 A time series study of drug sales and turbidity of tap water in Le Havre, France. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 22306426-6 2012 Traces of methadone and ephedrine were detected in some samples of tap water. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 22434272-7 2012 Tap water and river water were selected for evaluating the application to real water samples. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 22494481-4 2012 Compared with the tap water condition, tissue oxygenation index was 3.5% +- 1.3% higher in feet treated for 30 min with O(2)-infused water. Water 133-138 nuclear RNA export factor 1 Homo sapiens 18-21 22494481-6 2012 When blood flow to the foot was occluded for 5 min, feet resting in O(2)-infused water maintained a 3-fold higher O(2) consumption rate than feet treated with tap water (9.1 +- 1.4 vs. 3.0 +- 1.0 microL 100 g(-1) min(-1)). Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 22349296-2 2012 We found hand washing with tap water after touching the flesh of fruit, rather than using alcohol swabs, to be very important for accurate SMBG. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 22281753-7 2012 Noningestion water activities contributed more to the total exposure metric than did ingestion, but tap water THM concentrations were more predictive of blood THM levels than were metrics that incorporated water use. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 22281753-7 2012 Noningestion water activities contributed more to the total exposure metric than did ingestion, but tap water THM concentrations were more predictive of blood THM levels than were metrics that incorporated water use. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 22994033-4 2012 RESULTS: The bacterial count was statistically significantly about three times higher in the samples of the first burst tap water in comparison with the group of samples after letting the tap water run for two minutes 98.7, 78.5, 60.5-120.0 vs. 29.1, 25.8, 16.6-33.2 CFU/ml. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 22487003-5 2012 RESULTS: An (131) I content of 210 Bq/kg in the tap water in Tokyo, which is located 230 km south of the FNP, on March 22 and of 3500 Bq/kg in spinach sampled in a city located 140 km southwest of the FNP on March 19 decreased over time to <21 Bq/kg on March 27 and 12 Bq/kg on April 26, respectively. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 22326245-1 2012 A simple method with high efficiency for generating high pure hydrogen by hydrolysis in tap water of highly activated aluminum dross is established. Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 22356867-10 2012 The developed methodology has been tested with spiked tap water and effluent water of a wastewater treatment plant (WWTP) obtaining recoveries in the range of 91.5-114.1% for a 20 mg P L(-1) spike concentration. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 22439773-6 2012 RESULTS: 94% of families were from the poorest communes of the city, 40% lacked sewage and 11% tap-water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 22139469-0 2012 Analysis of UV filters in tap water and other clean waters in Spain. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 22139469-4 2012 The optimized methodology was applied to perform the first survey of UV absorbing compounds in tap water from the metropolitan area and the city of Barcelona (Catalonia, Spain). Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 22139469-8 2012 Maximum concentrations reached in tap water were 290 (BP3), 35 (4MBC), 110 (OD-PABA), 260 (EHMC), and 170 ng/L (OC). Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 22139469-9 2012 This study constitutes the first evidence of the presence of UV filter residues in tap water in Europe. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 22169679-5 2012 In order to make the correlation between radon and radium concentrations in the tap water and in the water from public drinking fountain, the gamma-spectrometric measurements were performed. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 22381982-11 2012 Moreover, experiments conducted with real water matrices, tap and surface water, showed that reaction, and formation of by-products, can take place both at the emission source point (household) and during drinking water production. Water 42-47 nuclear RNA export factor 1 Homo sapiens 58-61 21892761-0 2012 Occurrence and sources of bromate in chlorinated tap drinking water in Metropolitan Manila, Philippines. Water 62-67 nuclear RNA export factor 1 Homo sapiens 49-52 21892761-1 2012 Significant levels of potentially carcinogenic bromate were measured in chlorinated tap drinking water in Metropolitan Manila, Philippines, using an optimized ion-chromatographic method. Water 97-102 nuclear RNA export factor 1 Homo sapiens 84-87 21892761-3 2012 The concentration of bromate in tap drinking water samples collected from 21 locations in cities and municipalities within the 9-month study period ranged from 7 to 138 mug l-1. Water 45-50 nuclear RNA export factor 1 Homo sapiens 32-35 21892761-4 2012 The average bromate concentration of all tap drinking water samples was 66 mug l-1 (n = 567), almost seven times greater than the current regulatory limit in the country. Water 54-59 nuclear RNA export factor 1 Homo sapiens 41-44 21892761-9 2012 Bromate presence in tap drinking water can be linked to pollution in natural water bodies and the practice of using hypochlorite chemicals in addition to gaseous chlorine for water disinfection. Water 33-38 nuclear RNA export factor 1 Homo sapiens 20-23 21892761-9 2012 Bromate presence in tap drinking water can be linked to pollution in natural water bodies and the practice of using hypochlorite chemicals in addition to gaseous chlorine for water disinfection. Water 77-82 nuclear RNA export factor 1 Homo sapiens 20-23 21895970-6 2012 Tap water cannot keep cells viable as well as other solutions. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 21939365-0 2012 Determination of parathion, aldicarb, and thiobencarb in tap water and bottled mineral water in Mashhad, Iran. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 21939365-6 2012 In this study, we determined the concentration of three pesticides (aldicarb, parathion, and thiobencarb) in 13 tap-water samples collected from 13 different urban areas and 10 samples of bottled mineral water in Mashhad, a major city in northeast Iran. Water 116-121 nuclear RNA export factor 1 Homo sapiens 112-115 21939365-8 2012 Results showed that 2 of 13 tap-water samples and 2 of 10 bottled mineral water trademarks were contaminated either by parathion or by thiobencarb or both, with concentrations ranging between 0.6 and 0.8 ppb. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 22730938-3 2012 The objective of the study was to estimate the proportion of Perth metropolitan year two public primary school children drinking tap water at home, school and play. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 22730938-4 2012 It also aimed to explore knowledge and attitudes that children and parents have towards drinking tap water, bottled water, fruit juices and soft drinks. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 22730938-7 2012 RESULTS: Forty-two per cent of the children in our study reported if thirsty they drank tap (fluoridated) water at home whereas parents stated 60% of children drank tap water at home. Water 169-174 nuclear RNA export factor 1 Homo sapiens 165-168 22177529-5 2012 In 2 units of one hospital site, 100% of the samples of tap-water were positive, with high concentrations of Fusarium spp. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 22994033-4 2012 RESULTS: The bacterial count was statistically significantly about three times higher in the samples of the first burst tap water in comparison with the group of samples after letting the tap water run for two minutes 98.7, 78.5, 60.5-120.0 vs. 29.1, 25.8, 16.6-33.2 CFU/ml. Water 192-197 nuclear RNA export factor 1 Homo sapiens 188-191 22994033-5 2012 CONCLUSION: Two minutes running tap water contains about three times less bacterial count than first burst tap water Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 22994033-5 2012 CONCLUSION: Two minutes running tap water contains about three times less bacterial count than first burst tap water Water 111-116 nuclear RNA export factor 1 Homo sapiens 32-35 22994033-5 2012 CONCLUSION: Two minutes running tap water contains about three times less bacterial count than first burst tap water Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 22331819-0 2012 Dummy molecularly imprinted polymers as the coating of stir bar for sorptive extraction of bisphenol A in tap water. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 22331819-9 2012 The method was applied to the determination of trace bisphenol A in tap water. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 22285091-9 2012 Nickel exposure via drinking water was derived from databases on Ni tap water quality. Water 29-34 nuclear RNA export factor 1 Homo sapiens 68-71 22361702-0 2012 Defensive spending on tap water substitutes: the value of reducing perceived health risks. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 22361702-1 2012 We examine factors that explain consumer spending on tap water substitutes using information from a national survey undertaken with a representative set of Canadian respondents. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 22361703-2 2012 The mean volume of tap water consumed was 1.2 L/day, with a large range (0.03 to 9.0 L/day). Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 22361703-3 2012 In-home water treatment and interactions between age and gender and age and bottled water use were significantly associated with the volume of tap water consumed in multivariable analyses. Water 8-13 nuclear RNA export factor 1 Homo sapiens 143-146 22361703-3 2012 In-home water treatment and interactions between age and gender and age and bottled water use were significantly associated with the volume of tap water consumed in multivariable analyses. Water 84-89 nuclear RNA export factor 1 Homo sapiens 143-146 22285091-10 2012 A small proportion of the EU population (<5%) is likely to be exposed to tap water exceeding the EU standard (20 mug Ni/l). Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 22227358-6 2012 The accuracy was in a range of 102-106% and the precision of the assay was less than 6% in chlorinated and ozonated tap water, ozonated mineral water, and sea water. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 24520528-5 2012 RESULTS: Volume depletion (P < 0.001) and tap water (P < 0.03) both affected thirst by 13 mm per L of fluid, whereas spontaneous diuresis and infusion of Ringer"s acetate did not significantly change the thirst rating (multiple regressions). Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 24520528-8 2012 Similarly, hydration with tap water decreased thirst (by 24 mm, P < 0.04) in those who were thirsty (> 60 mm) while the others reported no change. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 24520528-9 2012 CONCLUSION: The change in thirst rating during volume depletion, administration of Ringer"s acetate, and ingestion of tap water were all dependent on the thirst rating obtained when the manipulation of the body fluid volume was initiated. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 22196879-5 2012 Good linearity for all calibration curves was obtained, and the limit of detection (LOD) for BPA was 0.4 ng/mL in tap water. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 22336796-14 2012 For chronic wounds, the relative risk of developing an infection when cleansed with tap water compared with normal saline was 0.16, (95% CI 0.01 to 2.96). Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 22336796-15 2012 Tap water was more effective than saline in reducing the infection rate in adults with acute wounds (RR 0.63, 95% CI 0.40 to 0.99). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 22191625-11 2012 Boiling water effectively removed phthalate esters from tap water. Water 8-13 nuclear RNA export factor 1 Homo sapiens 56-59 22191625-11 2012 Boiling water effectively removed phthalate esters from tap water. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 22305388-0 2012 Nontuberculous mycobacteria in tap water. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 21643824-1 2012 The last decade has seen an increasing trend in consumer preference of bottled water over tap water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 21670987-6 2012 Toyama ground, spring, and tap water were all the same type of water mass, called Ca-HCO(3). Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 21670987-8 2012 Trace levels of As, Cd, Cr, Co, Cu, Fe, Pb, Mn, Mo, Ni, V, Zn, Sr, and Hg were detected in ground, spring, and tap water sources using inductively coupled plasma atomic emission spectrometry, and their levels were below WHO and Japanese water quality standard limits. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 21670987-10 2012 Total trihalomethanes (THMs) were the major contaminant detected in all natural drinking water sources, but the concentration was highest in tap water (37.27 +- 0.05 mug/L). Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 21643824-8 2012 Ratings for taste, clarity, purity and safety were significantly higher for bottled water than tap water (P < 0.001). Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 21643824-2 2012 Little is known what type of water children and adolescents prefer for drinking and what their parents think of their community tap water. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 21845446-2 2012 To approach this question we combined propidium iodide/SYTO9 staining ("live/dead staining" indicating membrane integrity), fluorescence-activated cell sorting (FACS) and community fingerprinting for the analysis of a set of tap water samples. Water 229-234 nuclear RNA export factor 1 Homo sapiens 225-228 21717208-7 2012 The survey results showed high overall scores for perception of tap water quality and safety, and a preference for tap water over bottled water. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 21717208-7 2012 The survey results showed high overall scores for perception of tap water quality and safety, and a preference for tap water over bottled water. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 21717208-7 2012 The survey results showed high overall scores for perception of tap water quality and safety, and a preference for tap water over bottled water. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 21845446-3 2012 Live/dead staining revealed that about half of the bacteria in the tap water had intact membranes. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 22243625-11 2012 For the residential tap water in the 7 regions, the results of the mean (range) concentration values were found to be 1.0 (0.9-1.3) Bq/L. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 22243625-14 2012 The level was much lower for tap water. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 22957282-12 2012 Interestingly, the patient admitted using tap water occasionally for mixing heroin when her sterile water ran out, which we thought was the likely source of M. fortuitum. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 22957282-12 2012 Interestingly, the patient admitted using tap water occasionally for mixing heroin when her sterile water ran out, which we thought was the likely source of M. fortuitum. Water 100-105 nuclear RNA export factor 1 Homo sapiens 42-45 21937340-7 2012 The results show that the Debye model algorithm is of most importance in the tap water for a bandwidth of more than 1.5 GHz. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 22248201-4 2012 Radioactive iodine was detected at levels between 13 and 15 Bq/kg in tap water from the three facilities, but was not detected by reverse osmosis membrane at any of the facilities. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 23022848-3 2012 METHODS: We studied blood samples collected from 36 consecutive patients diagnosed with pesticides poisoning and 36 tap drinking water (surface and ground). Water 129-134 nuclear RNA export factor 1 Homo sapiens 116-119 21932005-7 2012 The proposed method has been successfully used for the determination of homocysteine in the real sample (blood serum and tap water) matrix. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 22174728-2 2012 In this proof-of-principle study, we sought to measure the release of potentially toxic elements from ionic footbaths into distilled and tap water with and without feet. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 23339938-0 2012 The prevalence, isolation and morphotyping of potentially pathogenic free-living amoebae from tap water and environmental water sources in Sivas. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 22642069-7 2012 Contribution of tap water in the intake of calcium and magnesium depended on the contents of these minerals in water, and amounted from 6,0% (< or = 68,3 mg calcium on dm3 water--1st quartile) to 14,8% (> 112 mg/dm3--4th quartile) for calcium and from 2,9% (< or = 10,9 mg/dm3) to 4,7% (> 15,4 mg/dm3) for magnesium. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 22642069-7 2012 Contribution of tap water in the intake of calcium and magnesium depended on the contents of these minerals in water, and amounted from 6,0% (< or = 68,3 mg calcium on dm3 water--1st quartile) to 14,8% (> 112 mg/dm3--4th quartile) for calcium and from 2,9% (< or = 10,9 mg/dm3) to 4,7% (> 15,4 mg/dm3) for magnesium. Water 111-116 nuclear RNA export factor 1 Homo sapiens 16-19 22642069-7 2012 Contribution of tap water in the intake of calcium and magnesium depended on the contents of these minerals in water, and amounted from 6,0% (< or = 68,3 mg calcium on dm3 water--1st quartile) to 14,8% (> 112 mg/dm3--4th quartile) for calcium and from 2,9% (< or = 10,9 mg/dm3) to 4,7% (> 15,4 mg/dm3) for magnesium. Water 111-116 nuclear RNA export factor 1 Homo sapiens 16-19 22642069-9 2012 Comparing the average content of minerals in non-boiled and boiled tap water the cooking process influenced the levels of calcium (95,8 +/- 31,8 vs 89,7 +/- 31,1 mg/dm3), magnesium (12,1 +/- 3,24 vs. 12,7 +/- 3,04 mg/dm3), zinc (0,35 +/- 0,87 vs. 0,17 +/- 0,89 mg/dm3), potassium (3,31 +/- 2,67 vs. 3,66 +/- 4,18 mg/dm3) and sodium (23,2 +/- 15,4 vs. 25,9 +/- 17,2 mg/dm3). Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 22377992-3 2012 The research work was performed using a laboratory-scale pilot plant that was filled with tap water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 22123226-12 2012 In subgroup analysis, significantly lower ORs for fever onset were observed for children who gargled with green tea (OR = 0.32), functional water (OR = 0.46), or tap water (OR = 0.70). Water 166-171 nuclear RNA export factor 1 Homo sapiens 162-165 22649292-4 2012 Most of the selected minerals found in the tap water samples were below the international standard limits, except for iron and manganese. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 22649292-5 2012 The concentrations of iron and manganese in the tap water samples were higher than the standard limits, which were obtained from one and three of the studied locations, respectively. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 21967193-6 2012 RESULTS: All samples sank in tap water but floated in a saturated salt solution, consistent with naphthalene. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 22457989-8 2011 The Tlemcen tap water contains acceptable fluorine content, but the mineral water, with an excessive contribution, can cause fluorose. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 22027901-0 2011 Colorimetric detection of copper ions in tap water during the synthesis of silver/dopamine nanoparticles. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 22027901-2 2011 The sensor shows excellent sensitivity and selectivity toward Cu(2+) in the range of 3.2-512 ppb and can be applied for Cu(2+) detection in tap water. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 22048438-1 2011 We tested the association of common events in drinking water distribution systems with contamination of household tap water with human enteric viruses. Water 55-60 nuclear RNA export factor 1 Homo sapiens 114-117 21967647-3 2011 Due to the formation of a Meisenheimer complex between DNAN and the modifier, the modified AgNPs can detect 20 mug/L (0.2 ng) and 0.1 mg/L (1 ng) DNAN in deionized water and aged tap water, respectively. Water 183-188 nuclear RNA export factor 1 Homo sapiens 179-182 22304190-3 2011 In this study, the interaction between two oscillating differently sized bubbles (generated in tap water) is studied using high speed photography. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 23109596-3 2012 They have been found in surface water and tap water in both developed and developing countries around the world including in North America, Europe and Asia. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 23109596-4 2012 In most countries, rivers are the source of tap water, which is one of the important pathways in which PFCs reach humans. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 21904798-8 2011 In tap water, the fluorescence of bisphenol A increases linearly versus its concentration and, its determination by direct laser photo-induced fluorescence permits to obtain a low limit of detection of 17 mug L(-1). Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 22023861-10 2011 In the final experiment, the developed method has been successfully applied to the determination of organophosphorus pesticides in wine and tap water samples and the obtained recoveries were between 83.8% and 101.3%. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 22276499-3 2011 This study aimed to compare lead levels between untreated ground water and treated surface (tap) water in 18 different districts. Water 97-102 nuclear RNA export factor 1 Homo sapiens 92-95 21962848-5 2011 The biofilm cultures were investigated under controlled turbulent flowing conditions and nutrients were provided using a synthetic medium (tap water supplemented with nitrate, phosphate and silica) to favour the biofilm growth. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 21967647-3 2011 Due to the formation of a Meisenheimer complex between DNAN and the modifier, the modified AgNPs can detect 20 mug/L (0.2 ng) and 0.1 mg/L (1 ng) DNAN in deionized water and aged tap water, respectively. Water 164-169 nuclear RNA export factor 1 Homo sapiens 179-182 22000761-8 2011 Estimated "dose" of atrazine and chlorotriazine from tap water was inversely related to mean mid-luteal estradiol metabolite. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 21879743-7 2011 The results of this study confirm that sucralose will function well as an indicator compound for anthropogenic influence on source, finished drinking and distribution system (i.e., tap) water, as well as an indicator compound for the presence of other recalcitrant compounds in finished drinking water in the U.S. Water 186-191 nuclear RNA export factor 1 Homo sapiens 181-184 21858362-7 2011 The efficacy of this new type of pH sensor has been tested using tap water as a typical real sample. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 21741755-7 2011 In particular, a volume of 1.50 L of PET-bottled water required an extra virtual volume of 1.93 L of water while an extra 2.13 L was necessary to supply the same volume of tap water. Water 49-54 nuclear RNA export factor 1 Homo sapiens 172-175 22108422-1 2011 OBJECTIVE: This paper aims to investigate the impact of anthracene addition on microbial community in agricultural soil irrigated with tap water or reclaimed wastewater. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 21227735-6 2011 Most patients cleaned their lens case with hot or cold tap water (72%). Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 22251740-6 2011 Light microscopy of B. pseudofea larvae revealed small air pockets in and around the spiracles when submerged in tap water; these air pockets disappeared when exposed to detergent solution. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 22586241-6 2011 In this study, dilution of the tap water sample by adding 4% MeOH (v/v) was observed to be adequate to compensate for the signal suppression. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 21741755-9 2011 The WF of tap water was mainly due to losses of water during pipeline distribution and usage, while WF of bottled water was greatly influenced by the production of plastic materials. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 21741755-9 2011 The WF of tap water was mainly due to losses of water during pipeline distribution and usage, while WF of bottled water was greatly influenced by the production of plastic materials. Water 48-53 nuclear RNA export factor 1 Homo sapiens 10-13 21741755-9 2011 The WF of tap water was mainly due to losses of water during pipeline distribution and usage, while WF of bottled water was greatly influenced by the production of plastic materials. Water 48-53 nuclear RNA export factor 1 Homo sapiens 10-13 21872294-0 2011 Hypertension incidence after tap-water implementation: a 13-year follow-up study in the arseniasis-endemic area of southwestern Taiwan. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 22991622-10 2011 There was a significant difference between the mean fluoride level of tap water (0.229 +- 0.079 ppm) and bottled water (0.111 +- 0.122 ppm) (P < 0.001). Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 22991622-12 2011 CONCLUSION: Our findings revealed that the mean fluoride level of both bottled and tap water samples evaluated is con-siderably lower than accepted standards. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 21976197-3 2011 Water samples were processed in such a way as to simulate real life conditions for drinking filtered water or hot water drinks prepared from tap water drawn from public water supply systems. Water 0-5 nuclear RNA export factor 1 Homo sapiens 141-144 21976197-7 2011 CONCLUSION: This study suggests that different methods of processing tap water can change DBP concentration to an extent that would have a meaningful impact on exposure assessment in epidemiological studies. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 21999747-11 2011 In contrast, only one sample (out of six) of urban tap water from Budapest city was found to contain stanozolol, at a concentration of 1.19 pg/mL. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 21643837-3 2011 The survey assessed current behaviors as well as perceived barriers and benefits to drinking tap water versus bottled water. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 21643837-8 2011 Important barriers to drinking tap water at Purdue include: perceived risks from tap water and the perceived safety of bottled water, preferring the taste of bottled water, and the convenience of drinking bottled water. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 21643837-8 2011 Important barriers to drinking tap water at Purdue include: perceived risks from tap water and the perceived safety of bottled water, preferring the taste of bottled water, and the convenience of drinking bottled water. Water 35-40 nuclear RNA export factor 1 Homo sapiens 81-84 21643837-8 2011 Important barriers to drinking tap water at Purdue include: perceived risks from tap water and the perceived safety of bottled water, preferring the taste of bottled water, and the convenience of drinking bottled water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 31-34 21643837-8 2011 Important barriers to drinking tap water at Purdue include: perceived risks from tap water and the perceived safety of bottled water, preferring the taste of bottled water, and the convenience of drinking bottled water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 31-34 21643837-8 2011 Important barriers to drinking tap water at Purdue include: perceived risks from tap water and the perceived safety of bottled water, preferring the taste of bottled water, and the convenience of drinking bottled water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 31-34 21643837-8 2011 Important barriers to drinking tap water at Purdue include: perceived risks from tap water and the perceived safety of bottled water, preferring the taste of bottled water, and the convenience of drinking bottled water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 31-34 21643837-9 2011 The qualitative interviews revealed that drinking water choices can be influenced by several factors-especially whether individuals trust tap water to be clean-but involve varying levels of complexity. Water 50-55 nuclear RNA export factor 1 Homo sapiens 138-141 21643837-10 2011 The implications of these results for social marketing strategies to promote tap water are discussed. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 21728895-15 2011 Scenario analyses with a higher consumption of vegetables or a higher nitrate concentration in tap water showed a significant higher intake of nitrate. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 21796783-7 2011 A series of tap water samples were subjected to analysis, fortunately giving negative results. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 21705522-7 2011 In tap water and in water from dental chairs, antibiotic resistance was more prevalent than in the other samples, mainly due to the predominance of isolates of the genera Sphingomonas and Sphingobium. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 21700315-2 2011 Iodine-131 concentrations in tap water higher than 100 BqL(-1) were reported by several local governments in Japan following the Fukushima Daiichi Nuclear Power Plant accident. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 21766475-8 2011 The applicability of the SPE-FASI-CZE method was evaluated by analyzing drinking tap water from Barcelona where seven HAAs were found at concentration levels between 3 and 13 mug/L. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 21748816-6 2011 The simultaneous and selective elimination of target toxicants is successfully performed for tap-water samples containing toxicant mixtures. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 21301855-4 2011 METHODS: Based on a large Japanese observational cohort, we have used weighted regression analysis to identify putative effects of tap water-derived lithium uptake on overall mortality. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 21700315-3 2011 Some individuals in the emergency-response community recommended the boiling of tap water to remove iodine-131. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 21700315-4 2011 However, the tap water boiling tests in this study showed no iodine-131 loss from the tap water with either short-term boiling (1-10 min) or prolonged boiling (up to 30 min) resulting in up to 3-fold volume reductions. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 22303580-0 2011 Major inorganic elements in tap water samples in Peninsular Malaysia. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 22303580-6 2011 Iron concentration of tap water from one of the locations was higher than the standard limit. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 22303580-7 2011 CONCLUSION: In general, tap water from different parts of Peninsular Malaysia had low concentrations of heavy metals and inorganic elements. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 20843387-1 2011 An inappropriate cross-connection between sewage- and drinking-water pipelines contaminated tap water in a Finnish town, resulting in an extensive waterborne gastroenteritis outbreak in this developed country. Water 63-68 nuclear RNA export factor 1 Homo sapiens 92-95 20843387-1 2011 An inappropriate cross-connection between sewage- and drinking-water pipelines contaminated tap water in a Finnish town, resulting in an extensive waterborne gastroenteritis outbreak in this developed country. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 20571527-5 2011 By subtracting daily food doses of perchlorate from the oral reference dose (RfD), we derive an allowances for perchlorate in tap water for several populations. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 21712603-6 2011 The production of hydrogen gas from POME during EC was also compared with hydrogen gas production by electrolysis of tap water at pH 4 and tap water without pH adjustment under the same conditions. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 21712603-6 2011 The production of hydrogen gas from POME during EC was also compared with hydrogen gas production by electrolysis of tap water at pH 4 and tap water without pH adjustment under the same conditions. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 21376440-3 2011 The daily intakes through tap water consumption ranged from <0.01 to 0.73 ng kg(-1) d(-1) for perfluorooctanoate (PFOA) and <0.01 to 0.08 ng kg(-1) d(-1) for perfluorooctanesulfonate (PFOS). Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 22128736-6 2011 The developed method was successfully applied for the analysis of tap water, bottle drinking water and lake water, and none of the 13 PAEs was detected. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 21784314-10 2011 CONCLUSION: The outbreak reported here was caused by drinking tap water contaminated with sewage at the source. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 21300396-0 2011 Leaching of Cu and Zn from discarded boat paint particles into tap water and rain water. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 21300396-2 2011 Leaching rates appeared to be diffusion-controlled and were greater in rain water than in tap water and were greater for Zn than for Cu. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 20952554-5 2011 Tap water samples were collected in representative mother homes on the basis of detailed water distribution patterns, and were analysed for major DBPs including trihalomethanes (THMs). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 21334835-3 2011 Temporal variation in tap water delta(18)O was correlated with water-supply type, and was related to geographic patterns of precipitation delta(18)O seasonality and water residence time. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 21334835-3 2011 Temporal variation in tap water delta(18)O was correlated with water-supply type, and was related to geographic patterns of precipitation delta(18)O seasonality and water residence time. Water 63-68 nuclear RNA export factor 1 Homo sapiens 22-25 21334835-6 2011 Incorporation of tap water delta(18)O seasonality in the analysis reduces the precision of geographic assignments, but other sources of uncertainty (e.g., spatial interpolation uncertainty) have an equal or larger effect. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 21456602-6 2011 Furthermore, in a fluoride concentration typical for tap water (10 muM), we observed roughening of individual step lines, resulting in the formation of scalloped morphologies. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 21376440-2 2011 The tap water reflected the contamination pattern and levels in their corresponding source water basins. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 21376440-2 2011 The tap water reflected the contamination pattern and levels in their corresponding source water basins. Water 91-96 nuclear RNA export factor 1 Homo sapiens 4-7 21918642-2 2011 We analysed the interaction between human population density and lack of tap water as a cause of dengue fever outbreaks with the aim of identifying geographic areas at highest risk. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 21640375-13 2011 Tap water iodine concentrations were low or undetectable and were not positively associated with urinary iodine concentrations. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 21429555-5 2011 In comparison to organisms cultured for the same period of time in artificial sea water prepared by filtered tap water, the expression of the alkaline isoenzyme decreased by 62% while that of the neutral isoenzyme increased by 58%. Water 82-87 nuclear RNA export factor 1 Homo sapiens 109-112 21376440-4 2011 Tap water intake-derived exposure accounted for 8.6%-101% (for PFOA) and while <10% (for PFOS) of total daily exposure, which was estimated from Korean serum concentrations using a pharmacokinetic model. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 21376440-5 2011 Our findings indicate that tap water intake could be an important contributor to PFOA exposure in Korean populations; accordingly, additional efforts are necessary to improve the removal efficiency of perfluorinated compounds (PFCs) in the water purification process. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 21376440-5 2011 Our findings indicate that tap water intake could be an important contributor to PFOA exposure in Korean populations; accordingly, additional efforts are necessary to improve the removal efficiency of perfluorinated compounds (PFCs) in the water purification process. Water 240-245 nuclear RNA export factor 1 Homo sapiens 27-30 20084436-7 2011 Good detection limits have been obtained, i.e.: 0.35 microg.L(-1) of chlorophenol in tap water, which are always lower than the reported Predictive Non Efficient Concentration (PNEC). Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 21411104-7 2011 Finally, the proposed method was applied to the analysis of water samples of different origin (tap, river and sea). Water 60-65 nuclear RNA export factor 1 Homo sapiens 95-98 21389011-6 2011 Individual exposure to THMs was calculated combining information on residential history, estimates of the average total THMs (TTHM) level in tap water at the successive residences and personal water consumption. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 21331487-0 2011 Development of a new three-phase membrane-assisted liquid-phase microextraction method: determination of nitrite in tap water samples as model analytical application. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 21331487-4 2011 The device has been tested for the determination of nitrite in tap water samples, which is extensively carried out in routine analysis, as model analytical application. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 21331487-7 2011 The method has been applied to four tap water samples of different origins, and accurate and precise results were achieved. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 21551998-3 2011 Patients in the experimental group drank carbonated water and those in the control group drank tap water for two weeks. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 20084436-6 2011 In a second part, to avoid the time consuming solvent extraction step, an analytical application to evaluate the performance of a direct analysis by laser induced fluorescence spectroscopy of ECDs traces in tap water and in raw water is presented. Water 211-216 nuclear RNA export factor 1 Homo sapiens 207-210 21247614-3 2011 Laboratory experiments were conducted with dechlorinated tap water over a pH range of 3, 7 and 9. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 21247614-11 2011 However, uptake rates in different aqueous matrixes declined in the order of deionized water>Plastic Lake water>dechlorinated tap water, so other parameters must affect uptake into POCIS, although this influence will be minor. Water 87-92 nuclear RNA export factor 1 Homo sapiens 132-135 21247614-11 2011 However, uptake rates in different aqueous matrixes declined in the order of deionized water>Plastic Lake water>dechlorinated tap water, so other parameters must affect uptake into POCIS, although this influence will be minor. Water 109-114 nuclear RNA export factor 1 Homo sapiens 132-135 21247614-11 2011 However, uptake rates in different aqueous matrixes declined in the order of deionized water>Plastic Lake water>dechlorinated tap water, so other parameters must affect uptake into POCIS, although this influence will be minor. Water 109-114 nuclear RNA export factor 1 Homo sapiens 132-135 21256669-0 2011 Irrigation of continent catheterizable ileal pouches: tap water can replace sterile solutions because it is safe, easy, and economical. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 21256669-2 2011 OBJECTIVE: Our aim was to compare the UTI rate, patient friendliness, and costs of standard sterile irrigation versus irrigation with tap water. Water 138-143 nuclear RNA export factor 1 Homo sapiens 134-137 21256669-5 2011 INTERVENTION: Patients underwent daily pouch irrigations with NaCl 0.9% solution or tap water. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 21256669-13 2011 CONCLUSIONS: Pouch irrigation with sterile NaCl 0.9% solution and tap water had comparable rates of positive UC. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 21256669-14 2011 Irrigation with tap water significantly lowered the incidence of nitrite-positive study days and was substantially less costly and more patient friendly than NaCl irrigation. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 21256669-15 2011 We therefore recommend the use of tap water (or bottled water) instead of sterile NaCl 0.9% solution for daily irrigation of continent catheterizable ileal pouches. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 21421769-0 2011 European tap water position statement released. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 21286625-0 2011 A highly specific rhodamine-based colorimetric probe for hypochlorites: a new sensing strategy and real application in tap water. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 21410938-2 2011 Exposure occurs from consumption of tap water, inhalation and dermal absorption. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 21338763-8 2011 Apparent recoveries obtained by the proposed method in tap water and tea extracts were (82-103)% and (89-99)%, respectively. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 21374812-6 2011 The utility of the column was demonstrated for the determination of UV-absorbing anions in saliva and tap water. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 22066282-3 2011 150 houses in two different areas, one supplied by bore well and other by tap water was selected by modified cluster sampling. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 21282342-0 2011 Glucose monitoring after fruit peeling: pseudohyperglycemia when neglecting hand washing before fingertip blood sampling: wash your hands with tap water before you check blood glucose level. Water 147-152 nuclear RNA export factor 1 Homo sapiens 143-146 22434982-8 2011 Twenty (57.1%) household water samples and 9 (25.7%) of the tap water samples had no residual free chlorine. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 22434982-10 2011 Eight (22.9%) tap water samples had low risk score for total coliforms whereas 21(60%) tap water had very low risk score for thermotolerant coliforms. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 22434982-10 2011 Eight (22.9%) tap water samples had low risk score for total coliforms whereas 21(60%) tap water had very low risk score for thermotolerant coliforms. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 22434982-12 2011 CONCLUSION: Water supplies at tap and household water containers were contaminated with bacteria. Water 12-17 nuclear RNA export factor 1 Homo sapiens 30-33 21257342-5 2011 The proposed sensor was then applied for the determination of zinc in tap water and hair samples with satisfactory results. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 21083571-7 2011 From 24 to 120 h, Save, industrialized coconut water and tap water were the worst storage media. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 21298782-7 2011 The method was successfully applied to analyses of lake and tap water samples, and the relative recoveries of target analytes from the spiked lake and tap water samples were 92.8-106.3 and 93.6-105.6%, respectively. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 21298782-7 2011 The method was successfully applied to analyses of lake and tap water samples, and the relative recoveries of target analytes from the spiked lake and tap water samples were 92.8-106.3 and 93.6-105.6%, respectively. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 21135743-4 2011 Tap water was infused via a metal trocar for approximately 60 minutes. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 21220402-9 2011 Factors that influence maternal water consumption or other contaminants in tap or bottled water might explain this finding. Water 32-37 nuclear RNA export factor 1 Homo sapiens 75-78 21185056-2 2011 Biofouling was stimulated by the use of tap water enriched with acetate at a range of concentrations (1-1000 mugCl(-1)). Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 21128590-1 2011 A low-abundance form of water, H(2)(17)O, was enriched from 0.04% to ~90% by slow evaporation and fractional distillation of tap water. Water 24-29 nuclear RNA export factor 1 Homo sapiens 125-128 21128590-1 2011 A low-abundance form of water, H(2)(17)O, was enriched from 0.04% to ~90% by slow evaporation and fractional distillation of tap water. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 21666364-0 2011 Oxidation of chromium(III) by free chlorine in tap water during the chlorination process studied by an improved solid-phase spectrometry. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 21666364-1 2011 The oxidation of Cr(III) at naturally-occurring concentration levels, i.e., microg dm(-3) or lower levels, by free chlorine during the chlorination process of tap water was studied using an improved solid-phase spectrophotometric method, which can be directly applicable to the specific determination of Cr(VI) at microg dm(-3) or lower levels. Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 20855239-8 2011 RESULTS: The median MnW in children"s home tap water was 34 microg/L (range, 1-2,700 microg/L). Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 20864894-4 2011 She wore extended wear soft contact lenses and frequently rinsed her eyes with tap water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 22022303-6 2011 RESULTS: Simulating the replacement of SSBs with tap water at 25, 50, and 100% levels resulted in 1-, 2.3-, and 3.8-point increases, respectively, in the HEI-2005 total score. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 22022303-7 2011 Based on a mean daily intake of 2,011 kcal, 100% substitution of SSBs with tap water would result in 11% reduction in energy intake. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 22163171-0 2011 Evaluation of biochemical urinary stone composition and its relationship to tap water hardness in Qom province, central Iran. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 21747732-0 2011 An environmental friendly procedure for photometric determination of hypochlorite in tap water employing a miniaturized multicommuted flow analysis setup. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 21747732-1 2011 A photometric procedure for the determination of ClO(-) in tap water employing a miniaturized multicommuted flow analysis setup and an LED-based photometer is described. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 22403982-4 2011 Source tap water was cycled through the lines at 1.4 mL/minute, five minutes on and 25 minutes off, eight hours/day, five days/week. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 22403982-11 2011 Further research on N-halamine tubing using a pure water source is recommended, as T effluent bacterial levels reflected the source tap water quality and proliferation of planktonic bacteria with no biofilm activity. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 21698155-8 2011 The present guidelines for fluoridated tap water might be reconsidered accordingly, particularly around Mt Vesuvius and in other fluoride hazard areas with high natural fluoride levels. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 21046080-7 2011 The feasibility of the method for the determination of analytes in water samples was checked in tap water and untreated and treated wastewater. Water 67-72 nuclear RNA export factor 1 Homo sapiens 96-99 22432265-5 2011 The water quality also impacted the inactivation efficiencies, and rotaviruses have a relatively higher resistant in secondary effluents than in the tap water under the same chlorine disinfection treatments. Water 153-158 nuclear RNA export factor 1 Homo sapiens 149-152 21697964-7 2011 Tap water at a flow rate of 10 L/h was infused through the arterial tubings. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 21090606-3 2010 This study investigates the intake of perchlorate, nitrate, and iodide attributable to direct and indirect tap water consumption. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 21411934-4 2011 Composting toilets and low-flow tap fittings further reduce the water demand. Water 64-69 nuclear RNA export factor 1 Homo sapiens 32-35 21090606-8 2010 On the basis of 24 h recall, 47% of the study participants reported drinking tap water; 89% reported either direct or indirect consumption of tap water. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 21090606-0 2010 Perchlorate, nitrate, and iodide intake through tap water. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 21090606-8 2010 On the basis of 24 h recall, 47% of the study participants reported drinking tap water; 89% reported either direct or indirect consumption of tap water. Water 146-151 nuclear RNA export factor 1 Homo sapiens 142-145 21090606-9 2010 For the adult population (age >= 20 yrs) the median tap water consumption rate was 11.6 mL/kg-day. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 21090606-10 2010 Using individual tap water consumption data and body weight, we estimated the median perchlorate, nitrate, and iodide dose attributable to tap water as 9.11, 11300, and 43.3 ng/kg-day, respectively, for U.S. adults. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 21090606-11 2010 This perchlorate exposure dose from tap water is relatively small compared to the total perchlorate exposure dose previously characterized for the U.S. adults (median 64 ng/kg-day) and the U.S. EPA reference dose (700 ng/kg-day). Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 20875670-4 2010 A single-pass flow-through experiment was run in a 100-liter column: bioremediation for 1year followed by infiltration of tap water (2.5years) saturated with oxygen, sufficient to oxidize the precipitated uraninite in two months. Water 126-131 nuclear RNA export factor 1 Homo sapiens 122-125 20705979-4 2010 A series of one-way analysis of variance (ANOVA) tests suggest that the presence of children in a household and self-reported concern that tap water causes health problems lead to significantly greater consumption of bottled water or filtered water and significantly less tap water consumption. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 20705979-4 2010 A series of one-way analysis of variance (ANOVA) tests suggest that the presence of children in a household and self-reported concern that tap water causes health problems lead to significantly greater consumption of bottled water or filtered water and significantly less tap water consumption. Water 143-148 nuclear RNA export factor 1 Homo sapiens 272-275 20705979-4 2010 A series of one-way analysis of variance (ANOVA) tests suggest that the presence of children in a household and self-reported concern that tap water causes health problems lead to significantly greater consumption of bottled water or filtered water and significantly less tap water consumption. Water 225-230 nuclear RNA export factor 1 Homo sapiens 139-142 20705979-4 2010 A series of one-way analysis of variance (ANOVA) tests suggest that the presence of children in a household and self-reported concern that tap water causes health problems lead to significantly greater consumption of bottled water or filtered water and significantly less tap water consumption. Water 225-230 nuclear RNA export factor 1 Homo sapiens 139-142 20705979-4 2010 A series of one-way analysis of variance (ANOVA) tests suggest that the presence of children in a household and self-reported concern that tap water causes health problems lead to significantly greater consumption of bottled water or filtered water and significantly less tap water consumption. Water 225-230 nuclear RNA export factor 1 Homo sapiens 139-142 20705979-6 2010 Factors yielding higher probabilities of a respondent being primarily a bottled water drinker (relative to the choice of tap water) include: higher income, unpleasant taste experiences with tap water, non-French-speaking, and being a male with children in one"s household. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 20705979-6 2010 Factors yielding higher probabilities of a respondent being primarily a bottled water drinker (relative to the choice of tap water) include: higher income, unpleasant taste experiences with tap water, non-French-speaking, and being a male with children in one"s household. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 20705979-7 2010 Similar factors yield higher probabilities of a respondent being primarily a filtered tap water drinker. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 178-181 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 178-181 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 182-187 nuclear RNA export factor 1 Homo sapiens 95-98 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 182-187 nuclear RNA export factor 1 Homo sapiens 95-98 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 20705979-8 2010 An important finding is that two key variables linking a person"s health perceptions regarding tap water quality are significant factors leading to the choice of either filtered tap water or bottled water over tap water. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 21438377-0 2010 [Application of solid phase extraction disk in the determination of acrylamide in tap water]. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 21438377-10 2010 The recovery for acrylamide spiked into a tap water sample was 79. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 21438377-12 2010 The method is simple, fast, sensitive and suitable for the determination of acrylamide in tap water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 20968297-5 2010 Special attention was given to adjusting for the coincidence of virus presence and use of tap water, as independently occurring short-term events within the longer interval that the virus is predicted to travel in any branch of the distribution system. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 21111143-6 2010 The developed method was applied for the analysis of tap water, mineral water, Pearl River water and honey. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 20817699-1 2010 BACKGROUND: Households in dual reticulation developments are supplied with recycled water from sewage effluent for some non-potable purposes, and conventional tap water for other uses. Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 20973517-6 2010 The electrode was applicable for the analysis of spiked arsenic in tap water containing a significant amount of various other ion elements. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 20692763-0 2010 Biological and photocatalytic treatment integrated with separation and reuse of titanium dioxide on the removal of chlorophenols in tap water. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 20692763-6 2010 Since titanium dioxide particles in tap water spontaneously sedimented on standing after the photocatalytic treatment, the combined treatment can be operated by integrating with the titanium dioxide separation and reuse. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 21250464-5 2010 Composting leachate processing with biological stabilization and dilution showed a fertilizer efficiency, and dry weight of impatiens irrigated with composting leachate was 1.46-2.49 times of tap water irrigation. Water 196-201 nuclear RNA export factor 1 Homo sapiens 192-195 21044941-3 2010 We present a typical case, where orthostatic hemodynamic response was significantly improved by ingestion of 500 ml tap water. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 21060670-6 2010 The patients were all contact lens wearers who had washed their lens storage cases with tap water. Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 20864897-1 2010 Excessively hot tap water results in an estimated 1500 hospital admissions and up to 50 deaths in the United States every year. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 20864897-4 2010 Model building and plumbing codes related to tap water temperature regulation and their subsequent adoption by state legislatures vary widely across the United States. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 20864897-7 2010 A broader and more uniform application of codes for regulating tap water temperature in both institutional and residential settings can be achieved through input from affected users, government agencies, legislators, advocacy organizations, and the general public. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 20591562-5 2010 The emergency treatment process removed the odor from the tap water and solved the crisis successfully in several days. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 20875589-8 2010 Tap water, sea water and mineral water samples were successfully analyzed for the existence of chlorophenols using the proposed method. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 20850122-3 2010 The limits of quantifications (LOQs) were lowest in tap water, where they ranged from 1.1 to 13.3 ng L(-1), and highest in raw wastewater (10.5-84.9 ng L(-1)). Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 20735717-7 2010 RESULTS: The vast majority of participants (n = 46) avoided drinking unfiltered tap water based on perceptions that it had poor taste, smell, and color, bolstered by a historically justified and collectively transmitted belief that the public water supply is unsafe. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 20840409-12 2010 Wetting surgical wounds with clean tap water does not increase, and may even reduce, wound infection rate. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 20701302-0 2010 Preparation of surface imprinting polymer capped Mn-doped ZnS quantum dots and their application for chemiluminescence detection of 4-nitrophenol in tap water. Water 153-158 nuclear RNA export factor 1 Homo sapiens 149-152 19942644-0 2010 Nano-porous pottery using calcined waste sediment from tap water production as an additive. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 20045595-4 2010 Hot tap water scald cases for 1999-2007 were identified from hospitalisation data for all public and private hospitals in NSW. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 20045595-5 2010 To investigate hot tap water scald hospitalisations over time, negative binomial regression analysis was performed. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 20045595-6 2010 There were 845 hospitalisations for hot tap water scalds in NSW over the period of the study. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 20045595-7 2010 Hospital admission rates for hot tap water scalds decreased by an estimated 6% (3.2-8.5, 95%CI) per year since the introduction of regulations. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 19995560-1 2010 in domestic tap water in houses of contact lens wearers in the metropolitan area of Mexico City. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 19995560-9 2010 Most Acanthamoeba isolates were non-pathogenic, however, their presence in tap water is a potential hazard since some species can cause Acanthamoeba keratitis and granulomatous amoebic encephalitis. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 20663510-7 2010 Under optimum conditions, the range of enrichment factors and extraction recoveries of tap water samples are ranging 372-1308 and 87-105%, respectively. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 20663510-9 2010 The relative standard deviations (RSD) for 0.01microgL(-1) of PAHs in tap water were in the range of 5.1-10.0%. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 20452023-8 2010 Estimated daily intakes of 4-NP, BPA and TCS for infants were 705, 1340 and 5 ng/day, respectively, by drinking 1L of tap water from a baby bottle at 40 degrees C. This study showed that the exposure to the three compounds from drinking water is unlikely to pose a health risk. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 20452023-0 2010 Simultaneous determination and assessment of 4-nonylphenol, bisphenol A and triclosan in tap water, bottled water and baby bottles. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 20452023-1 2010 This study investigated the levels of 4-nonylphenol (4-NP), bisphenol A (BPA) and triclosan (TCS) in bottled water and tap water in Guangzhou and release of these chemicals from baby bottles using gas chromatography-mass spectrometry with negative chemical ionization. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 20452023-4 2010 Five of the tap water samples from six drinking water plants were found to contain 4-NP and BPA both in June and December, while TCS was detected in the same five plants only in June. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 20452023-5 2010 The highest concentrations in tap water for 4-NP, BPA and TCS were 1987, 317 and 14.5ng/L, respectively. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 20452023-6 2010 Daily intakes of 4-NP, BPA and TCS of adults by drinking 2L of tap water were estimated to be 1410, 148 and 10 ng/day, respectively. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 20554274-9 2010 Brominated THM predominated in the tap water (84% of total THM) and chloroform predominated in the swimming pool (84% of total THM). Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 20107809-3 2010 PATIENTS AND METHOD: For a total of 100 patients a routine examination glove was filled with 350 ml of warm tap water and after injection placed for 10 min on the eye scheduled for surgery. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 20650003-13 2010 CONCLUSION: Replacement of the RDT kit"s dedicated buffer by saline, distilled water and tap water can cause false-positive test results. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 20434248-0 2010 Determination of four fluoroquinolone antibiotics in tap water in Guangzhou and Macao. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 20434248-1 2010 Four fluoroquinolone antibiotics (norfloxacin, ciprofloxacin, lomefloxacin, and enrofloxacin) in tap water in Guangzhou and Macao were analyzed using high performance liquid chromatography fluorescence detection. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 20434248-3 2010 The fluoroquinolone antibiotics pollution in tap water widely distributes in Guangzhou and Macao. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 20434248-5 2010 Our result indicates that the antibiotic concentration in tap water in Guangzhou tends to obviously reduce at the beginning of rainy season, even decreases below the limit of quantification immediately. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 20444965-2 2010 We describe a pseudo-outbreak in which multiple strains that were associated with moistening of culturette swabs with tap water were isolated from a single clinic before collecting the patient specimen. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 20499933-3 2010 Tap water delta(2)H and delta(18)O values were strongly correlated with the stable isotope ratios of bottled water and soda purchased in the same location. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 20499933-3 2010 Tap water delta(2)H and delta(18)O values were strongly correlated with the stable isotope ratios of bottled water and soda purchased in the same location. Water 109-114 nuclear RNA export factor 1 Homo sapiens 0-3 20499933-4 2010 Beer water delta(2)H and delta(18)O values were also correlated with tap water, although not as strongly. Water 5-10 nuclear RNA export factor 1 Homo sapiens 69-72 20499933-6 2010 It was concluded that the isotopic composition of local tap water is a reasonable proxy for consumers" fluid intake in most U.S. cities. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 20441944-8 2010 Validation of the analytical system has been performed by the successful determination of free chlorine in tap water and swimming pools water samples. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 20685419-6 2010 Based on a signal to noise ratio of 3, the detection limits were 0.75 nM for the tap water and 12.0 nmol kg(-1) for the soil. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 20685419-7 2010 The method showed good recoveries and precision, 93.4% (RSD 1.5%, n=3) for 100 mL of tap water spiked with 2.0 nmol and 81.3% (RSD 2.6%, n=3) for 10 g of soil spiked with 0.80 nmol, suggesting that the imprinted stir bar can be successfully applied to the preconcentration of nicosulfuron in real samples. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 20233016-4 2010 For pH normalization, 17 times more tap water than Diphoterine was required. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 20494396-3 2010 The benefits produced by using ozone were appreciable even visually since the final effluent of the process looked like tap water. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 22347240-3 2010 The aim of this study was to investigate the prevalence of Acanthamoeba in tap-water samples in Iran. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 22347240-4 2010 METHOD: In this descriptive cross-sectional study, 94 samples of cold and warm tap-water were collected from different wards of hospitals in 13 cities of Iran in 2007-2008. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 20237946-2 2010 Therefore, we conducted a prospective study to assess whether tap water from the domestic environment of neutropenic patients poses a risk for infections from the waterborne pathogens nontuberculous mycobacteria (NTM), Legionella spp., and Pseudomonas aeruginosa. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 20237946-3 2010 MATERIALS AND METHODS: Tap water samples were taken in the homes of 65 hemato-oncologic patients who were discharged from the hospital whilst neutropenic and had a suspected period of neutropenia of a minimum of 10 days. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 20494397-2 2010 Water samples with different calcium hardness were prepared by continuous evaporation of tap water using a laboratory cooling tower. Water 0-5 nuclear RNA export factor 1 Homo sapiens 89-92 20174984-9 2010 Recovery studies applied to the determination of mercuric ions in bottled and tap water samples were in the 92-104% range. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 19725837-0 2010 Recommendations for tap water iontophoresis. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 20486565-3 2010 In addition, sterilized water used for handwashing when performing operations has no scientific basis and use of tap water is considered sufficient. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 20812627-5 2010 The results showed that the average recoveries of antibiotics in tap water and wastewater were 54.9%-130% and 57.4%-138%, respectively, and the corresponding relative standard deviations (RSD, n=3) were 2.85%-28.6% and 2.02%-23.2%, respectively. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 20546838-0 2010 Source and occurrence of particulate lead in tap water. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 21787604-2 2010 From the results of the study, the hazard quotient for oral ingestion of mercury in tap water in Obuasi is 7.4 and 15 respectively via both central tendency exposure (CTE) and reasonable maximum exposure (RME) parameters, respectively. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 19937457-9 2010 Balneotherapy with the thermal water from Hajduszoboszlo spa had a more pronounced physiological effect compared to that seen in the control group treated with tap water in a 3 month period. Water 164-169 nuclear RNA export factor 1 Homo sapiens 160-163 19926298-2 2010 Artificial mixing of tap water with channeled spring water were found causing temperature decrease, lowering Ra(2+) concentration and inhibiting hokutolite crystallization. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 20141152-0 2010 Fluorescent carrier ampholytes assay for portable, label-free detection of chemical toxins in tap water. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 20141152-8 2010 We then present the integration of the technique into a self-contained hand-held device and demonstrate detection of chemical toxins (2-nitrophenol and 2,4,6-trichlorophenol) in tap water, with no sample preparation steps. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 20064792-0 2010 Relationship between tap water hardness, magnesium, and calcium concentration and mortality due to ischemic heart disease or stroke in The Netherlands. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 20064792-9 2010 For men with the 20% lowest dietary magnesium intake, an inverse association was observed between tap water magnesium intake and stroke mortality (HR per 1 mg/L intake = 0.75; 95% CI, 0.610.91), whereas for women with the 20% lowest dietary magnesium intake, the opposite was observed. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 20223084-0 2010 Comparative study of sample preparation techniques coupled to GC for the analysis of halogenated acetic acids (HAAs) acids in tap water. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 20034631-9 2010 The proposed method was successfully applied to the quantitative analysis of the phenols in tap water, and proved to be a simple, convenient and reliable sample preconcentration and determination method for volatile analytes in water samples. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 20034631-9 2010 The proposed method was successfully applied to the quantitative analysis of the phenols in tap water, and proved to be a simple, convenient and reliable sample preconcentration and determination method for volatile analytes in water samples. Water 228-233 nuclear RNA export factor 1 Homo sapiens 92-95 19937002-1 2010 A commercially available screen-printed carbon electrode coated with an ex situ deposited bismuth film (BiSPCE) has been applied to the determination of Pb(II) and Zn(II) ions in tap water (Barcelona water distribution network) by means of stripping voltammetry (SV) and stripping chronopotentiometry (SCP). Water 183-188 nuclear RNA export factor 1 Homo sapiens 179-182 19937002-1 2010 A commercially available screen-printed carbon electrode coated with an ex situ deposited bismuth film (BiSPCE) has been applied to the determination of Pb(II) and Zn(II) ions in tap water (Barcelona water distribution network) by means of stripping voltammetry (SV) and stripping chronopotentiometry (SCP). Water 200-205 nuclear RNA export factor 1 Homo sapiens 179-182 19751538-4 2010 Consuming tap water was significantly associated with illness (risk ratio 4.7, 95% confidence interval 1.5-14.4). Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 19796094-9 2010 count in tap water was about 10(4) GU l(-1). Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 19926298-2 2010 Artificial mixing of tap water with channeled spring water were found causing temperature decrease, lowering Ra(2+) concentration and inhibiting hokutolite crystallization. Water 53-58 nuclear RNA export factor 1 Homo sapiens 21-24 20123629-0 2010 Exposure on tap: drinking water as an overlooked source of lead. Water 26-31 nuclear RNA export factor 1 Homo sapiens 12-15 19858133-0 2010 Strategies to screen and reduce vascular risk--putting statins in the tap water is not the answer. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 19896690-0 2010 Tap water consumers differ from non-consumers in chlorine flavor acceptability but not sensitivity. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 19937002-0 2010 Stripping analysis of heavy metals in tap water using the bismuth film electrode. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 19896690-2 2010 As a consequence, the putative link between sensitivity to chlorine flavor and tap water consumption is an issue in drinking water habits studies. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 19896690-2 2010 As a consequence, the putative link between sensitivity to chlorine flavor and tap water consumption is an issue in drinking water habits studies. Water 125-130 nuclear RNA export factor 1 Homo sapiens 79-82 19896690-5 2010 In a first experiment, we used the constant stimuli procedure to evaluate the chlorine flavor detection threshold of a group of 20 tap water consumers and a group of 20 non-consumers. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 19896690-8 2010 Nevertheless, tap water consumers showed a higher liking score for chlorinated solutions and were found to be more inclined to accept these solutions as drinking water. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 19896690-8 2010 Nevertheless, tap water consumers showed a higher liking score for chlorinated solutions and were found to be more inclined to accept these solutions as drinking water. Water 162-167 nuclear RNA export factor 1 Homo sapiens 14-17 19896690-9 2010 Taken together these findings suggested that consumers may disparage chlorine flavor in drinking water on the basis of their tap water cognitive representation. Water 97-102 nuclear RNA export factor 1 Homo sapiens 125-128 19896690-9 2010 Taken together these findings suggested that consumers may disparage chlorine flavor in drinking water on the basis of their tap water cognitive representation. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 19457500-0 2010 [Is tap water the same as mineral water? Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 20009334-3 2009 This method was applied to the recovery tests of copper(II) in human urine, bovine serum and tap water; the results were satisfactory. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 20109206-0 2010 Water quality monitoring records for estimating tap water arsenic and nitrate: a validation study. Water 0-5 nuclear RNA export factor 1 Homo sapiens 48-51 20109206-0 2010 Water quality monitoring records for estimating tap water arsenic and nitrate: a validation study. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 20109206-1 2010 BACKGROUND: Tap water may be an important source of exposure to arsenic and nitrate. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 19931118-4 2010 Because limited information is available on the water intake rate in Asian countries, we carried out a nationwide survey using an online questionnaire to assess the direct tap water and beverage consumption within the general Korean population. Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 19931118-8 2010 Indirect tap water intake through the consumption of water-rich dishes occupies 18.5% of average total water intake. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 19931118-8 2010 Indirect tap water intake through the consumption of water-rich dishes occupies 18.5% of average total water intake. Water 53-58 nuclear RNA export factor 1 Homo sapiens 9-12 19931118-8 2010 Indirect tap water intake through the consumption of water-rich dishes occupies 18.5% of average total water intake. Water 53-58 nuclear RNA export factor 1 Homo sapiens 9-12 19931118-9 2010 In the summer, the average consumption of direct tap water and beverages increased by up to 19.7 and 7.6%, respectively. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 19945145-0 2010 Quantitative risk assessment of Cryptosporidium in tap water in Ireland. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 19945145-9 2010 The model indicates a reduced risk of infection from tap water that has undergone microfiltration, as this treatment is more robust in the event of high contamination loads. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 20356213-3 2010 Here, we demonstrate the spontaneous generation of hydrogen gas from ordinary room-temperature tap water when combined with aluminum-oleic acid core-shell nanoparticles obtained via sonochemistry. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 19234753-9 2010 In several instances, tap water samples collected at the consumers" end of the distribution system did not reflect on the true quality of the treated water. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 22808388-3 2010 In the present study, the degradation of the carbaryl pesticide was investigated in the laboratory synthetic samples of tap water, in the effect of sonolysis and photolysis processes. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 20512722-6 2010 More than 99% of bacterial cells in the tap water was retained by the RO membranes, leaving <50 cells/mL in the permeate water. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 20512722-6 2010 More than 99% of bacterial cells in the tap water was retained by the RO membranes, leaving <50 cells/mL in the permeate water. Water 124-129 nuclear RNA export factor 1 Homo sapiens 40-43 20512722-8 2010 In quasi-steady state, the total cell numbers in the biofilm and bulk water were of order 10(3) cells/cm(2) and 10(3) cells/mL, respectively, which were about 2 orders of magnitude lower than those grown in the tap water produced from conventional water treatment. Water 215-220 nuclear RNA export factor 1 Homo sapiens 211-214 27820507-29 2010 CONCLUSIONS: Current RCT evidence suggests the use of a surgical sterile catheterisation technique is not required, and that tap water is sufficient for cleaning genitalia. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 19184627-6 2010 The TII concentration for tap water was close to that of Lake Mead (approximately 90 nM); however, tap water contained no detectable iodide as a result of ozonation and chlorine treatment which converts all of the iodide to iodate. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 19184627-6 2010 The TII concentration for tap water was close to that of Lake Mead (approximately 90 nM); however, tap water contained no detectable iodide as a result of ozonation and chlorine treatment which converts all of the iodide to iodate. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 20082002-1 2010 New techniques enable a shift in monitoring chemicals that affect water quality from mainly at the end product, tap water, towards monitoring during the whole process along the production chain. Water 66-71 nuclear RNA export factor 1 Homo sapiens 112-115 27819881-16 2010 One study determined the effects of prompt irrigation of the eyes with tap water immediately after alkali burns had been suffered at the scene of injury. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 20102592-5 2009 RESULTS: Mean total tap water intake was 1.8 l/day, and women on average spent 146 minutes per week showering and bathing. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 20102592-6 2009 Most tap water intake occurred at home (100% for unemployed, 71.8% for employed). Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 20102592-7 2009 Differences between age groups were observed for total tap water intake overall (p = 0.02) and at home (p = 0.01), and for bottled water intake (p = 0.05). Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 20102592-8 2009 There were differences between ethnic groups for tap water intake at home (p = 0.02) and total tap water intake at work (p = 0.02). Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 20102592-8 2009 There were differences between ethnic groups for tap water intake at home (p = 0.02) and total tap water intake at work (p = 0.02). Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 20102592-9 2009 Total tap water intake at work differed by income category (p = 0.001). Water 10-15 nuclear RNA export factor 1 Homo sapiens 6-9 19660937-4 2009 Using acidified or tap water caused considerable biogas losses and should therefore be avoided where biogas is stored before measurement. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 19837845-0 2009 Temporal and spatial diversity of the tap water microbiota in a Norwegian hospital. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 20055218-2 2009 In Japan, because the majority of HPC bacteria are supposed to be harmless and all tap water should maintain residual chlorine, there are few studies of the virulence of HPC bacteria. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 19691418-8 2009 If they were to escape into tap water, then the highest predicted concentrations would still be a factor of between 25 and 40 below the current recommended daily doses of concern. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 19011982-6 2009 Similarly, physicochemical analysis shows the persistent quality of tap water. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 19664809-9 2009 Tap water infusion at a flow rate of 10 L/h was infused through the arterial tubings controlled with a drip regulator filling the arterial tree and leaking into the interstitial and cisternal space. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 19011982-7 2009 Based on hardness analysis, bottled and tap water are categorized as soft water. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 19011982-9 2009 It is also important to note that the tap water distribution network in MAYS is a high-pressure recirculation network and there is no chance to grow bacteria in stagnant water in pipe lines or houses. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 19011982-13 2009 Hence, it is the responsibility of the Royal Commission to encourage the peoples in the city to drink tap water as it is as good as bottled water even better than some of the brands and is monitored regularly. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 19011982-15 2009 Preference for tap water over bottled water will also reduce the production of bottled water that has flooded the market, the enormous strain on the environment, and the pollution due to used empty plastic bottles in the landfill area and will help to keep the city clean. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 19590130-2 2009 Therefore, since the margin between healthy intake and toxic intake is narrow, the selenium concentration of tap water is a parameter that must be monitored because of its potential for increased intake. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 20016436-1 2009 A patient developed a prolonged respiratory illness after a single overnight use of tap water to humidify air supplied by a constant positive airway pressure (CPAP) device, which she had previously used for six years without difficulty. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 19771382-3 2009 Relatively low levels of these pollutants were observed, with mean concentrations ranging between 0.51-315.8 lg/kg and 0.05-74.6 ng/L in soil and tap water, respectively. Water 150-155 nuclear RNA export factor 1 Homo sapiens 146-149 19925915-8 2009 The proposed method was applied to the analysis of four different sources water samples (tap, well, rain and Yellow River water) and the relative recoveries of spiked water samples are 99.9-115.4%, 101.8-113.7% and 87.3-117.6% at three different concentration levels of 75, 200 and 1000 microg L(-1), respectively. Water 74-79 nuclear RNA export factor 1 Homo sapiens 89-92 19570607-0 2009 Continuous flow photocatalytic treatment integrated with separation of titanium dioxide on the removal of phenol in tap water. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 19570607-1 2009 We studied the continuous flow photocatalytic treatment integrated with separation/reuse of titanium dioxide on the removal of phenol (20 mg l(-1)) in electrolytes containing tap water. Water 179-184 nuclear RNA export factor 1 Homo sapiens 175-178 19804887-13 2009 The DLLLME technique shows good linearity (r(2)>or=0.999), good repeatability (RSD: 4.0-12.2% for tap water; 5.7-8.5% for river water) and high sensitivity (LODs: 0.10-0.60microg/L for tap water; 0.11-0.95microg/L for river water). Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 20182069-2 2010 A simulated brine wastewater was prepared from tap water and contained a nitrate concentration of 125 mg/l as N and a total salt concentration of about 1%. Water 23-28 nuclear RNA export factor 1 Homo sapiens 47-50 19648106-4 2009 Tap water was implicated in the outbreak. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 19944392-3 2009 METHODS: All patients received standard oral hydration: 2000mL of tap water within the 24 hours after coronary angiography. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 19775722-2 2009 In the present study, therefore, environmental or tap water samples collected from various regions of China were assayed for PFOS and PFOA by solid phase extraction and liquid chromatography-mass spectrometry technique. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 19457619-2 2009 Some epidemiological studies suggest that even very low lithium levels induced by routine consumption of lithium from tap water may have anti-suicidal effects both in patients with mood disorders and in the general population. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 19457619-4 2009 If this is the case, increasing lithium levels of drinking water could potentially reduce the risk of suicide, and justify administering lithium to tap water. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 19886947-5 2009 We then integrated the distribution of estimated leaching rates into an exposure model that estimated the probability distribution of OT concentrations in tap waters and the resulting potential human OT exposures via tap water consumption. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 19625070-0 2009 Surveying the mutagenicity of tap water to elicit the effects of purification processes on Japanese tap water. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 19625070-2 2009 Tap water samples (179) were collected at 17 sampling sites located from the northern tip (Hokkaido) to the southern tip (Kagoshima Prefecture). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 19625070-7 2009 The highest positive ratios of the Ames test and the umu test were 92% under the condition TA100-S9 and 9% under the condition NM2009-S9, respectively, which indicated that the Ames test has higher sensitivity for the test of tap water than the umu test. Water 230-235 nuclear RNA export factor 1 Homo sapiens 226-229 19775722-8 2009 Many cities provided tap water with low levels of PFOS and PFOA, however, tap water in Guangzhou and Shenzhen exceeded 10ngL(-1) for both chemicals. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 19775722-8 2009 Many cities provided tap water with low levels of PFOS and PFOA, however, tap water in Guangzhou and Shenzhen exceeded 10ngL(-1) for both chemicals. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 19691274-10 2009 The analytical method was applied to triplicate 1 L samples of a chlorinated tap water and a chlorinated indoor pool water. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 19691274-11 2009 For the tap water, the digestion efficiency was 47.2% (+/-11.1% relative standard deviation), and the lysine nitrile concentration was 104.6 ng/L (+/-6.8 ng/L standard deviation). Water 12-17 nuclear RNA export factor 1 Homo sapiens 8-11 19615509-8 2009 The procedure was applied to tap water, well water, and sea water; and accuracy was assessed through recovery experiment and independent analysis by graphite atomic absorption spectrometry. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 18830235-1 2009 Disinfection by-products in tap water have been found in some studies to be associated with adverse pregnancy outcomes, but little is known about how water use and consumption might change during early pregnancy. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 19581476-3 2009 We found ARGs and heterotrophic ARB in all finished water and tap water tested, although the amounts were small. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 19581476-4 2009 The quantities of most ARGs were greater in tap water than in finished water and source water. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 19486431-2 2009 METHODS AND RESULTS: Published degenerate PCR primers were used to determine that 54% of tap water samples (7/13) were positive for a deh gene, indicating that drinking water distribution systems may harbour bacteria capable of HAA degradation. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 19486431-2 2009 METHODS AND RESULTS: Published degenerate PCR primers were used to determine that 54% of tap water samples (7/13) were positive for a deh gene, indicating that drinking water distribution systems may harbour bacteria capable of HAA degradation. Water 169-174 nuclear RNA export factor 1 Homo sapiens 89-92 18830235-5 2009 Changes were detected between early and mid-pregnancy for ingested cold tap water and showering. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 18830235-7 2009 Increases in cold tap water intake were associated with age >35 years, income < $40,000, and non-Hispanic white ethnicity. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 18830235-8 2009 We also found that the proportion of the total variation due to within-subject variability was 62% for hot tap water ingestion but only 35% for showering and approximately 50% for cold tap water, bottled water and bathing. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 18830235-8 2009 We also found that the proportion of the total variation due to within-subject variability was 62% for hot tap water ingestion but only 35% for showering and approximately 50% for cold tap water, bottled water and bathing. Water 189-194 nuclear RNA export factor 1 Homo sapiens 185-188 19701266-0 2009 When the tap is turned down--restricted water flow increases bacterial contamination after handwashing. Water 40-45 nuclear RNA export factor 1 Homo sapiens 9-12 19475327-0 2009 Episodic trihalomethane species and levels in tap water at a start of operation of advanced treatment in Osaka Prefectural water supplies. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 19475327-0 2009 Episodic trihalomethane species and levels in tap water at a start of operation of advanced treatment in Osaka Prefectural water supplies. Water 123-128 nuclear RNA export factor 1 Homo sapiens 46-49 19475327-1 2009 Dramatic changes in trihalomethanes of tap water caused by decreasing the chlorine dose from to break-point to zero at a pre-chlorination could be found during several years from starting the advanced treatment in Osaka Prefectural water utilities (from 1998 to 2002). Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 19576540-7 2009 Risk was not specific for cKS on the limbs, but it was elevated approximately four- to five-fold with frequent bathing or tap water drinking in communities with high luvisols. Water 126-131 nuclear RNA export factor 1 Homo sapiens 122-125 19634207-10 2009 have a beneficial role in suppressing the concentrations of haloacetic acids in tap water, which contrasts the historical (albeit erroneous) association of Afipia sp. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 19117672-6 2009 The procedure was applied to tap water, well water, river water and sea water, and accuracy was assessed through the analysis of certified reference water or recovery experiments. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 19124200-0 2009 Octadecyl bonded silica membrane disk modified with Cyanex302 for separation and flame atomic absorption spectrometric determination of nickel from tap water and industrial effluent. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 19124200-4 2009 The method applied for detection of nickel in tap water and effluent sample had a relative standard deviation (R.S.D.) Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 19467769-3 2009 A preliminary experiment demonstrated that chitosan was more efficient at color removal in tap water than in demineralized water, and that a substantially lower concentration of chitosan could be used with tap water. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 19722439-5 2009 RESULTS: Of 194 parents, 134 (69%) gave their children bottled water either exclusively or with tap water. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 19722439-7 2009 Reasons for giving children bottled water included: fear of contaminants in tap water; taste and/or smell of tap water; and convenience of bottled water. Water 36-41 nuclear RNA export factor 1 Homo sapiens 76-79 19722439-7 2009 Reasons for giving children bottled water included: fear of contaminants in tap water; taste and/or smell of tap water; and convenience of bottled water. Water 36-41 nuclear RNA export factor 1 Homo sapiens 109-112 19487996-4 2009 Concentrations of radon in tap water were up to nearly three-fold the recommended limit. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 19523663-0 2009 Composition and particle size of superparamagnetic corrosion products in tap water. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 19757655-0 2009 [Editorial comment on the analysis of bottled and tap water in Spain and the impact of its consumption on urinary lithiasis]. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 19757664-0 2009 [Spanish bottled and tap water analysis and their relation with urinary lithiasis]. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 19757664-4 2009 RESULTS: Information about composition from tap water of most of the main Spanish cities and 85 bottled water brands was found. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 19556578-3 2009 Rinsing with soapy water followed by tap water was the most effective cleaning method and reduced pathogen load by 3.7 and 3.1 log(10)s at the low and high inoculum levels, respectively. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 19721966-1 2009 The objective of this study was to analyze the fluoride concentration on the water that flows of the tap in the urban area of the city of Campo Grande (MS). Water 77-82 nuclear RNA export factor 1 Homo sapiens 101-104 19673271-0 2009 Perfluorinated compounds in tap water from China and several other countries. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 19543414-0 2009 Fluoride intake through consumption of tap water and bottled water in Belgium. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 20120163-8 2009 Good sanitation and safe tap water are major contributors to human health and well-being Major efforts and investments are needed, based on rigorous, objective assessments of risks for the environment and public health. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 19386853-2 2009 Epidemiological studies and molecular comparisons of Mycobacterium chelonae strains from different patients and the environment suggested that contamination may be associated with inappropriate cleaning of the multiple-injection device with tap water. Water 245-250 nuclear RNA export factor 1 Homo sapiens 241-244 19240354-3 2009 In addition, we investigated the daily volume of cold tap water consumed by those respondents who consumed no bottled water and the factors that influence this consumption. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 19240354-5 2009 The mean volume of water consumed in a day (including bottled and tap water) was 1.39 l. Among those who reported to exclusively consume tap water, the mean daily volume of tap water consumed was 1.45 l. The daily amount of cold water consumed in a day was lower for older respondents, more markedly for men than women. Water 19-24 nuclear RNA export factor 1 Homo sapiens 137-140 19240354-5 2009 The mean volume of water consumed in a day (including bottled and tap water) was 1.39 l. Among those who reported to exclusively consume tap water, the mean daily volume of tap water consumed was 1.45 l. The daily amount of cold water consumed in a day was lower for older respondents, more markedly for men than women. Water 19-24 nuclear RNA export factor 1 Homo sapiens 137-140 19240355-5 2009 Among 253 respondents who consumed water: (a) 177/253 (70%) of tap water samples contained more than 10 microg l(-1) total inorganic arsenic (ave. 66 microg l(-1), median 20 microg l(-1)); (b) As((III)) occurred as a small proportion of total arsenic in most samples (ave. 22%, median 3%); and (c) tungsten occurred in concentrations ranging from below the detection limit (3 microg l(-1)) to a maximum of 610 microg l(-1) (ave. 30 microg l(-1), median 3 microg l(-1)). Water 35-40 nuclear RNA export factor 1 Homo sapiens 63-66 19240355-5 2009 Among 253 respondents who consumed water: (a) 177/253 (70%) of tap water samples contained more than 10 microg l(-1) total inorganic arsenic (ave. 66 microg l(-1), median 20 microg l(-1)); (b) As((III)) occurred as a small proportion of total arsenic in most samples (ave. 22%, median 3%); and (c) tungsten occurred in concentrations ranging from below the detection limit (3 microg l(-1)) to a maximum of 610 microg l(-1) (ave. 30 microg l(-1), median 3 microg l(-1)). Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 19240355-8 2009 This suggests that householders in this area were likely to be exposed to both metals simultaneously, given that 253/307 of the respondents (82%) reported consuming tap water. Water 169-174 nuclear RNA export factor 1 Homo sapiens 165-168 19240358-7 2009 For tap water, the type of storage had a significant effect on the susceptibility to contamination (chi(2) = 12.090; p = 0.007). Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 19606593-6 2009 The delta18O values for the water of nearly all samples of diesel was close to the delta18O of local tap water at the filling station. Water 28-33 nuclear RNA export factor 1 Homo sapiens 101-104 19606593-6 2009 The delta18O values for the water of nearly all samples of diesel was close to the delta18O of local tap water at the filling station. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 19558100-8 2009 Phosphorus tended to release under river water than tap water. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 19954078-5 2009 The diarrhea cases were distributed among all country groups who has used tap water A and the attack rate was ranged from 5.21% (20/384) to 21.23% (100/471). Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 18953497-3 2009 Tap water in few locations in Europe contains up to 139 microg/L mostly bound to humic substances, probably leaching from marine sediments in the aquifers. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 19543414-1 2009 There is a tendency to align higher levels of fluoride in natural mineral water with the existing higher levels in tap water. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 19543414-4 2009 A deterministic approach was used whereby consumption quantities of tap water and different brands of bottled water were linked with their respective fluoride concentrations. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 19586601-1 2009 During hair coloring a number of disulfide bonds in cystine are oxidized (1) to create cysteic acid, forming binding sites for metal ions such as Ca(2+ )and Cu(2+ )from tap water (2). Water 173-178 nuclear RNA export factor 1 Homo sapiens 169-172 19586601-5 2009 Nanoscale secondary ion mass spectrometry (NanoSIMS) has been used to locate the calcium and copper within hair that has been treated with a colorant and washed multiple times in tap water containing these ions. Water 183-188 nuclear RNA export factor 1 Homo sapiens 179-182 19438126-10 2009 Industrial towns (Korangi, Landhi and SITE) had significantly higher concentration of chromium (micro = 82.4; SE = 8.9) in their ground and tap water as compared to the mean chromium concentration (micro = 33; SE = 2.2) in the water samples of rest of the towns of Karachi (P < 0.001). Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 19216032-6 2009 However, microcystins are present frequently in tap water at lower doses. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 19216032-7 2009 Here, we hypothesized that chronic consume of tap water containing low doses of microcystins may be a risk factor for liver and colorectal cancer. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 19401989-3 2009 Tap water is readily available, safe, and effective and, thus, the preferred irrigation fluid. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 19203604-6 2009 The proposed method was validated by simultaneous determination of phosphate and silicate in detergent and tap water and also Co(2+) and Ni(2+) in tap water samples. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 19203604-6 2009 The proposed method was validated by simultaneous determination of phosphate and silicate in detergent and tap water and also Co(2+) and Ni(2+) in tap water samples. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 18834589-9 2009 Also, 13 species were detected in tap water with concentrations up to 0.13 microgL(-1) for tri(chloropropyl) phosphate (TCPP). Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 19304108-3 2009 The patient was unaware that he was wearing a bandage contact lens and repeatedly rinsed his face and eyelids with tap water. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 19387929-1 2009 BACKGROUND: The corrosion of drinking water pipe materials can release different elements into tap water. Water 38-43 nuclear RNA export factor 1 Homo sapiens 95-98 19387929-1 2009 BACKGROUND: The corrosion of drinking water pipe materials can release different elements into tap water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 19387929-13 2009 There were remarkable regional differences in the frequency of tap water contamination. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 18365760-0 2009 Risk assessment of trihalomethanes from tap water in Fortaleza, Brazil. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 18365760-2 2009 The mean levels of THM compounds were obtained in Fortaleza tap water as follow: 63.9 microg L(-1) for chloroform (CHCl(3)), 40.0 microg L(-1) for bromodichloromethane (CHBrCl(2)), and 15.6 microg L(-1) for dibromochloromethane (CHBr(2)Cl). Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 18365760-4 2009 The mean CR for THMs in tap water is 3.96 x 10(-4). Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 19341604-2 2009 The company issued advice through mass media to boil tap water before consumption; this advice was lifted six days later. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 19200549-7 2009 A cyclohexyldiol-silica fiber was used, as a simple example of applicability, for the successful determination of benzaldehyde, acetophenone and dimethylphenol at trace level in spiked tap water. Water 189-194 nuclear RNA export factor 1 Homo sapiens 185-188 19368213-4 2009 Transition of chemical equilibrium of the BrO3- reductive reaction was theorized as the reason for pH dependency of the BrO3- reduction.The electrochemicaltreatment of BrO3- -contaminated tap water resulted in a rapid decrease in BrO3- concentration from 100 to 48 microg/L with a contact time of 9.2 s. Thus, electrochemical treatment allowed the rapid removal of BrO3-. Water 192-197 nuclear RNA export factor 1 Homo sapiens 188-191 19178932-3 2009 The main hypothesis was that the difference in the alkalinity value between tap water and domestic wastewater is almost exclusively a result of the hydrolysis of urea (NH(2)CONH(2), excreted in the human urine) to ammonia (NH(3)), regardless of the question what fraction of NH(3(aq)) is transformed to NH(4)(+). Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 19178932-4 2009 Results from a field study show that the ratio between the alkalinity added to tap water when raw wastewater is formed (in meq/l units) and the TAN (total ammonia nitrogen, mole/l) concentration in the raw wastewater is almost 1:1 in purely domestic sewage and close to 1:1 in domestic wastewater streams mixed with light industry wastewaters. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 18823399-7 2009 Young water found in the PSW also was present in UFA monitoring wells that tap a highly transmissive zone (43- to 53-m depth) in the UFA. Water 6-11 nuclear RNA export factor 1 Homo sapiens 75-78 22059353-8 2009 Source of drinking water with a strong association with drinking tap water was the only factor significantly associated with seropositivity to cryptosporidiosis infection (OR= 37.33, P< 0.001). Water 19-24 nuclear RNA export factor 1 Homo sapiens 65-68 18335002-1 2009 Volunteer studies suggest that showering/bathing with chlorinated tap water contributes to daily chloroform inhalation exposure for the majority of US adults. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 19062029-7 2009 The recoveries of N-nitrosodimethylamine, N-nitrosomorpholine, N-nitrosomethylethylamine, and N-nitrosopyrrolidine present in tap water sample at a concentration of 10 ng/L (mean+/-standard deviation, n=4) were (94.8+/-2.7)%, (102.0+/-6.9)%, (99.3+/-3.9)%, and (102.8+/-2.5)%, respectively. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 19127436-8 2009 While they selectively dissolved in gastric-like medium, in tap water (intake conditions), the matrix remained almost unchanged and efficiently prevented drug dissolution. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 19222249-3 2009 Current therapeutic strategies include topical aluminum salts, tap-water iontophoresis, oral anticholinergic agents, local surgical approaches, and sympathectomies. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 18789711-1 2009 Radon concentrations are measured in the tap water collected in different areas in Marrakech (Morocco) by using liquid scintillation techniques. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 19402494-1 2009 Organic matter in the tap water was isolated into strongly hydrophobic acids, weakly hydrophobic acids, charged hydrophilic and neutral hydrophilic by DAX-8, XAD-4 and IRA-958 synthetic resins. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 22059353-8 2009 Source of drinking water with a strong association with drinking tap water was the only factor significantly associated with seropositivity to cryptosporidiosis infection (OR= 37.33, P< 0.001). Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 19288451-6 2009 The developed sensor was applied to tap water and the urine of a smoker. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 19204863-5 2009 Concentration of microcystin-LR was 650 microg L(-1) in the reservoir, while the tap water contained 2.5 microg L(-1). Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 19759456-8 2009 The presence of these compounds in the tap water, surface water and animal and human tissues indicates their global contamination and bioaccumulative phenomena in the ecosystems. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 19785868-9 2009 It is important to irrigate with safe tap water at a temperature of around 37 degrees C. Most patients treated in this way feel safe to go out again. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 19934515-6 2009 When pure urine was diluted with tap water, use of a higher tap water proportion for dilution expedited the electrolysis to achieve a nearly complete removal of phosphate in solution, but dilution caused the increase in energy consumption. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 19934515-6 2009 When pure urine was diluted with tap water, use of a higher tap water proportion for dilution expedited the electrolysis to achieve a nearly complete removal of phosphate in solution, but dilution caused the increase in energy consumption. Water 37-42 nuclear RNA export factor 1 Homo sapiens 60-63 19934515-6 2009 When pure urine was diluted with tap water, use of a higher tap water proportion for dilution expedited the electrolysis to achieve a nearly complete removal of phosphate in solution, but dilution caused the increase in energy consumption. Water 64-69 nuclear RNA export factor 1 Homo sapiens 33-36 19934515-6 2009 When pure urine was diluted with tap water, use of a higher tap water proportion for dilution expedited the electrolysis to achieve a nearly complete removal of phosphate in solution, but dilution caused the increase in energy consumption. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 19271520-0 2008 [A flow injection on-line unequal flow complexation preconcentration procedure coupled with flame atomic absorption spectrometry for determination of lead in tap water]. Water 162-167 nuclear RNA export factor 1 Homo sapiens 158-161 19107388-4 2008 Here we analyzed thirty-two hospital tap water samples that were collected from different locations in three hospitals so as to evaluate the prevalence of NTM species. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 19087789-11 2008 In tap water Ca2+ concentrations ranged between 0-337 mg/l, Na+ between 1-332 mg/l, and Mg(2+) between 0.3-315 mg/l. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 19087789-13 2008 CONCLUSIONS: Water, even bottled water or tap water, has a great variability in the concentrations of Ca(2+), Mg(2+) and Na(+). Water 13-18 nuclear RNA export factor 1 Homo sapiens 42-45 19087789-13 2008 CONCLUSIONS: Water, even bottled water or tap water, has a great variability in the concentrations of Ca(2+), Mg(2+) and Na(+). Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 18805568-5 2008 In tap water, at the groundwater supplied sampling point, brominated species, bromoform and dibromoacetonitrile, were detected at the highest levels most probably due to bromide ion intrusion from seawater. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 19068326-6 2008 The proposed fluorescence optode was successfully applied to the determination of cobalt content of vitamin B12 ampoule, cobalt cake, cobalt alloy and tap water samples. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 19256380-10 2008 In the third stage, raw leachate was diluted by tap water in order to decrease the FA concentration. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 19271520-1 2008 A simple, environmentally friendly, cost-effective, and sensitive method was developed for the determination of trace lead in tap water by flow injection (FI) on-line unequal flow complexation preconcentration procedure coupled with flame atomic absorption spectrometry (FAAS). Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 19271520-11 2008 The proposed method has been successfully applied to the determination of lead in tap water samples. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 18953970-7 2008 Studies have shown that tap water is safe to use for irrigation, that white petrolatum ointment is as effective as antibiotic ointment in postprocedure care, and that wetting the wound as early as 12 hours after repair does not increase the risk of infection. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 19232219-8 2008 DISCUSSION: Since the results obtained in the analyses of the substances used were correct and no adverse effect was observed after the re-administration of the substances, we may conclude that the outbreak would be related to the washing process performed previously to the sterilization of the instrumentation used in the surgery, mainly because the recommendation to use distilled and sterile water for this purpose was not followed and, on the contrary, tap water continued to be used. Water 396-401 nuclear RNA export factor 1 Homo sapiens 458-461 19232219-8 2008 DISCUSSION: Since the results obtained in the analyses of the substances used were correct and no adverse effect was observed after the re-administration of the substances, we may conclude that the outbreak would be related to the washing process performed previously to the sterilization of the instrumentation used in the surgery, mainly because the recommendation to use distilled and sterile water for this purpose was not followed and, on the contrary, tap water continued to be used. Water 462-467 nuclear RNA export factor 1 Homo sapiens 458-461 19003750-3 2008 A 22-year-old drug-abuser injected flunitrazepam tablets dissolved in tap water into her left femoral artery and presented with clinical signs of acute ischaemia of the left leg. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 18842119-0 2008 Impact of a silver layer on the membrane of tap water filters on the microbiological quality of filtered water. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 18842119-0 2008 Impact of a silver layer on the membrane of tap water filters on the microbiological quality of filtered water. Water 105-110 nuclear RNA export factor 1 Homo sapiens 44-47 18677274-10 2008 More than 99% of bactericidal or fungicidal activity was noted for all species, except for Candida albicans, in tap water at either pH 7.0 or 8.4. Water 116-121 nuclear RNA export factor 1 Homo sapiens 112-115 18800868-5 2008 The WDT was performed, consisting of a baseline intraocular pressure (IOP) measurement, followed by the ingestion of 1 L of tap water within 5 min. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 18721951-0 2008 Tap water irrigation and additives to optimize success with the Malone antegrade continence enema: the Indiana University algorithm. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 18721951-1 2008 PURPOSE: We report the long-term effectiveness of standard tap water for Malone antegrade continence enema irrigation as well as our algorithm for managing refractory constipation/fecal incontinence in a large single institution experience. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 18555497-11 2008 Following the earthquake, drinking stream water or tap water without boiling or chlorination may have led to a common source water-borne outbreak of rotavirus gastroenteritis. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 18571218-1 2008 This study was conducted to compare housewives" winter and summer exposures to volatile disinfection by-products (DBPs) in chlorinated tap water. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 18571218-5 2008 All of the subjects answered that they consumed tap water after either thermal treatment or purification through filtration systems. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 18571218-8 2008 In both seasons, the ingestion route can be discounted, because tap water is processed before consumption, eliminating the volatile DBPs. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 18709190-10 2008 This method was successfully applied to the determination of arsenate in mineral-, drinking- and tap-water samples. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 18850657-6 2008 This method was successfully applied to separate MCs from other compounds in spiked tap water after solid-phase extraction. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 18620920-7 2008 The procedure was applied to tap water, well water, river water and sea water, and accuracy was assessed through the analysis of certified reference water or recovery experiments. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 18656684-5 2008 The proposed method was successfully applied to the analysis of tap water and well water samples. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 18470871-2 2008 The method was applied to model reaction mixtures in the study of the formation of iodoacetic acid after chlorinated tap water was boiled in the presence of potassium iodide or iodized table salt. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 18769704-0 2008 A reader responds to "Should we use saline or tap water for cleansing wounds? Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 18585247-12 2008 Fe(III) and Mn(II) ions, present in treated tap water in relatively high concentrations, did not interfere. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 18585247-13 2008 Effective pH adjusting of the loaded solution in on-line mode, when applying diluted Clark-Lubs buffering solution, allowed accurate copper determination in tap water (compared to graphite furnace atomic absorption spectrometry, GFAAS) using standard addition or combination calibration method. Water 161-166 nuclear RNA export factor 1 Homo sapiens 157-160 18761943-8 2008 Identical norovirus sequences were detected in stool samples, on surfaces and in tap water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 18761943-11 2008 Epidemiological results indicated that consuming tap water was a risk factor; however, this could not be concluded definitively on the basis of the available data. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 18538069-9 2008 However, filtering a tap-water solution of 0.8 mg F/L reduced the fluoride concentration only until 8 L had been filtered. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 18675148-2 2008 Tap water probing revealed persistent colonization of all ICU water taps with a single P aeruginosa clonotype. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 18675148-2 2008 Tap water probing revealed persistent colonization of all ICU water taps with a single P aeruginosa clonotype. Water 62-67 nuclear RNA export factor 1 Homo sapiens 0-3 18602659-0 2008 Perfluorooctanesulfonate and perfluorooctanoate in raw and treated tap water from Osaka, Japan. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 18602659-8 2008 Concentration ranges of PFOS and PFOA in potable tap water were 0.16-22 ng/l and 2.3-84 ng/l, respectively. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 18602659-9 2008 There were positive correlations between PFC concentrations in raw water and tap water samples. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 18602659-11 2008 Based on the current action value reported by U.S. Environmental Protection Agency, PFOA concentrations found in tap water in Osaka is not expected to pose health risks. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 18502432-10 2008 Finally, the study was applied to determine the vitamins in several real aqueous samples including mixed juice fruit, urine and tap water samples and relatively good results were obtained. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 18495203-3 2008 Dosing of orthophosphate against corrosion did not increase microbial growth potential in the water and in the biofilm in both corroded and uncorroded systems receiving tap water with a low content of organic carbon and of biodegradable organic fraction. Water 173-178 nuclear RNA export factor 1 Homo sapiens 169-172 18495203-4 2008 However, in tap water having a high concentration of organic carbon from acetate addition, orthophosphate addition promoted the growth of bacteria, allowed more bacteria to assemble on corroded and uncorroded surfaces, and increased the consumption of organic carbon. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 18594344-2 2008 METHODS: Tap water was collected from the bathroom sink of 100 households in Hong Kong and tested for the presence of Acanthamoeba by means of PCR amplification. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 18423519-10 2008 The environmental load was evaluated by carbon dioxide generation as an index and it was found that the carbon dioxide generated by the electrolysis method was 1/70 lower than that by the dilution method with tap water. Water 213-218 nuclear RNA export factor 1 Homo sapiens 209-212 18470314-8 2008 Consumption of tap water at home was a significant predictor of PFOA blood concentrations in Arnsberg. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 18504848-3 2008 The aim of the present study was to evaluate the indoor health risks due to tap water consumption contaminated by BTEX. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 18379423-1 2008 BACKGROUND: Laboratory evidence suggests tap water disinfection by-products (DBPs) could have an effect very early in pregnancy, typically before clinical detectability. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 18504848-6 2008 For evaluation of human risks due to the use of contaminated tap water, a mathematical model was elaborated. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 18492345-0 2008 Measurement of fuel oxygenates in tap water using solid-phase microextraction gas chromatography-mass spectrometry. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 17942224-8 2008 The method was applied to the determination of molybdenum(VI) in steels and tap water and well water samples. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 18335212-9 2008 It was successfully used as an indicator electrode in potentiometric determination of terbium(III) ions with EDTA and in direct determination in tap water and binary mixtures with quantitative results. Water 149-154 nuclear RNA export factor 1 Homo sapiens 145-148 18492345-3 2008 This method quantifies trace levels of methyl tertiary-butyl ether, ethyl tertiary-butyl ether, di-isopropyl ether, and tertiary-amyl methyl ether in tap water. Water 154-159 nuclear RNA export factor 1 Homo sapiens 150-153 18492345-4 2008 The method achieves detection limits of less than 0.025 microg/L for all analytes and linear ranges of three orders of magnitude in the measurement of the alkyl ether fuel oxygenates in 5-mL tap water samples. Water 195-200 nuclear RNA export factor 1 Homo sapiens 191-194 18492345-7 2008 Methyl tertiary-butyl ether was detected in samples of tap water taken from geographically diverse regions of the United States. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 18411377-3 2008 ANSWER: Lead exposure through drinking tap water while breastfeeding is not associated with any serious concerns in most available studies. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 18254034-16 2008 For chronic wounds, the relative risk of developing an infection when cleansed with tap water compared with normal saline was 0.16, (95% CI 0.01 to 2.96). Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 18411377-1 2008 QUESTION: Owing to the recent concerns of lead (Pb) leaking into tap water, one of our female patients is concerned about the effects of Pb exposure to newborns while breastfeeding. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 19385472-10 2008 Placentae washed well with running tap water to remove blood clots. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 17410115-3 2008 To examine the accuracy of a nitrate/nitrite test strip, we recruited Washington State residents to estimate levels of these contaminants in their tap water using these strips, and simultaneously provide a tap water sample for laboratory analysis. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 18275109-0 2008 Sensitivity enhancement for the analysis of naproxen in tap water by solid-phase extraction coupled in-line to capillary electrophoresis. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 18275109-1 2008 SPE coupled in-line to CE, as the strategy to enhance the concentration sensitivity in CE, has been used to enrich naproxen in tap water samples. Water 131-136 nuclear RNA export factor 1 Homo sapiens 127-130 18788518-8 2008 The OR value were 1.749 for multipara, 1.995 for those going to the nearest healthcare facilities by the most convenient traffic in less than 10 minutes, 3.011 for those drinking tap water, 5.435 for those with the education of high school, 29.149 for those with over 5 times in terms of frequency of prenatal checkup and 37.822 for those being advocated on institutional delivery. Water 183-188 nuclear RNA export factor 1 Homo sapiens 179-182 18371799-10 2008 The applicability for analysing ground, lake and tap-water samples collected in the vicinity of uranium deposits was successfully demonstrated. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 18371820-0 2008 Quantitative analysis of hydrolysis of carbaryl in tap water and river by excitation-emission matrix fluorescence coupled with second-order calibration. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 18371820-1 2008 A novel method was proposed to determine simultaneously carbaryl and its degradation product 1-naphthol in river and tap water in this paper. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 18371820-5 2008 It was also applied to investigate the hydrolysis kinetics of carbaryl in river water and tap water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 17697431-3 2008 Tap water is a major dietary source but bioavailability of organically bound iodine may be impaired. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17697431-6 2008 Tap water contained 2 microg/l elemental iodine in Randers and 140 microg/l iodine bound in humic substances in Skagen. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17697431-11 2008 Bioavailability of iodine in humic substances in Skagen tap water was about 85 %. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 18518807-11 2008 Thus, although exposure to disinfection by-products in tap water may be a risk factor for human bladder cancer, this may not be true for canine bladder cancer at the concentrations at which dogs are exposed. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 18164742-6 2008 Except for silica, other nanoparticles rapidly aggregated in tap water due to electric double layer (EDL) compression. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 18164742-7 2008 The stability of silica in tap water is related to its low Hamaker constant. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 18371881-8 2008 The method was successfully applied to the extraction and determination of gold in tap water and silicate ore samples. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 18408264-4 2008 The water samples in the study were of two types, viz, borewell water and tap water, these being commonly used by the people of Davangere City, Karnataka. Water 4-9 nuclear RNA export factor 1 Homo sapiens 74-77 18254034-17 2008 Tap water was more effective than saline in reducing the infection rate in adults with acute wounds (RR 0.63, 95% CI 0.40 to 0.99). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17998610-9 2008 Previous surveys in England and Korea have shown that acanthamoebae are found in 15 to 30% of tap water samples in the home and have been associated with corneal infection in contact lens wearers. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 18245965-5 2008 RESULTS: Eyes irrigated with PSS with chlorine showed an increase in fluorescein scores, and eyes washed with both tap water and PSS with chlorine showed an increase in Rose Bengal scores. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 18595407-3 2008 It implied that the concentration of THMs in swimming pool water was higher than those in tap water, particularly, brominated-THMs. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 18595407-8 2008 Cancer risk of THMs concluded from various routes in descending order was: skin exposure while swimming, gastro-intestinal exposure from tap water intake, and skin exposure to tap water and gastro-intestinal exposure while swimming. Water 180-185 nuclear RNA export factor 1 Homo sapiens 176-179 18182788-1 2008 An essential but frequently neglected aspect of dialysis treatment is the dialysis fluid produced by blending treated tap water with concentrated solutions containing electrolytes and buffer. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 18536508-1 2008 To prevent formation of trihalomethanes (THMs) in drinking water, removing precursors of trihalomethanes (PTHMs) in water resources for tap water is essential. Water 59-64 nuclear RNA export factor 1 Homo sapiens 136-139 19092219-5 2008 At the markets, although the tap water was found to be free of microbes, contaminated and non-contaminated vegetables are mixed and washed in the same bowl, which may bring about further spreading of infectious bacteria. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 18983000-25 2008 At present, the most appropriate option for securing safe water for drinking and cooking is treatment of water at the tap. Water 105-110 nuclear RNA export factor 1 Homo sapiens 118-121 18824804-0 2008 Investigation of formaldehyde pollution of tap water and rain water using a novel visual colorimetry. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 18824804-1 2008 The pollution of tap water and rain water with formaldehyde in Toyama Pref., Japan was investigated by means of a simple, rapid and cost-effective visual colorimetry developed by us. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 18027194-0 2007 Assessment and management of tap water lead contamination in Lower Saxony, Germany. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 18824804-10 2008 It must be concerned about the pollution of rainwater with formaldehyde, when rain water is applied for tap water and miscellaneous purpose. Water 48-53 nuclear RNA export factor 1 Homo sapiens 104-107 18441443-5 2008 Concerning the financial part, the implementation of membrane processes in the wastewater purification installation is economically feasible, especially when expensive tap water is used as pure water. Water 172-177 nuclear RNA export factor 1 Homo sapiens 168-171 18036538-5 2007 The applications to chlorinated tap water, well water, and river water have been validated. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 18027194-12 2007 There were remarkable regional differences in the frequency of tap water contamination. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 18278404-8 2007 The relationship between the concentration of fluoride in tap water and the prevalence of dental caries showed a negative correlation with the coefficient of 0.81 (except 1.14 mg/L fluoride ). Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 18278404-9 2007 There was also a positive correlation between the concentration of fluoride in tap water and the community dental fluorosis index (CFI) with a coefficient of 0.78. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 17689184-4 2007 Column tests were carried out to investigate the removal of arsenate from tap water under dynamic conditions. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 17878564-1 2007 The toxicological risks and lifetime cancer risks of trihalomethanes through oral ingestion, dermal absorption, and inhalation exposure from tap water in selected regions in Lebanon are estimated. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 17878567-6 2007 It is predicted that airway inflammation can occur if humidifier reservoirs are filled with tap water, sometimes even at typical drinking-water distribution-system endotoxin concentrations. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 18007978-0 2007 Drink a toast to tap water: study suggests water consumption benefit outweighs THM hazard. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 18007978-0 2007 Drink a toast to tap water: study suggests water consumption benefit outweighs THM hazard. Water 43-48 nuclear RNA export factor 1 Homo sapiens 17-20 18007986-3 2007 A pooled analysis based on six case-control studies observed a positive association between tap water and bladder cancer but none for nontap fluid intake, suggesting that contaminants in tap water may be responsible for the excess risk. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 18007986-3 2007 A pooled analysis based on six case-control studies observed a positive association between tap water and bladder cancer but none for nontap fluid intake, suggesting that contaminants in tap water may be responsible for the excess risk. Water 191-196 nuclear RNA export factor 1 Homo sapiens 92-95 17662298-7 2007 Arsenic adsorption in the filter from As-spiked tap water was relatively lower than that from artificial As solution because high HCO(-)(3) concentration restrained siderite dissolution and thus suppressed production of the fresh Fe oxides on the siderite grains. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 17925648-0 2007 The impact of a legislative intervention to reduce tap water scald burns in an urban community. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 17925648-6 2007 Tap water scalds increased from 15 to 22 per million/yr after legislation enactment. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17925648-11 2007 In New York City, tap water scald burns remain a significant public health risk and continue to occur within buildings exempt from current law. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 18257309-5 2007 The relative standard deviations (RSDs) and relative recoveries (n = 5) from tap water fortified samples were 3.1% -7.9%, and 101% - 105%, and from waste water fortified samples were 3.3% - 7.9%, and 92.5% - 97.0%, respectively. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 17551841-10 2007 The study found that most people (91%) in the Langas slum used wells as the main source of domestic water, whereas the rest used tap water. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 17406836-4 2007 The water load test was performed by having subjects drinking room-temperature tap water at a predetermined rate of 15 ml/min. Water 4-9 nuclear RNA export factor 1 Homo sapiens 79-82 18050065-6 2007 Colored tap water pumped on the right was emptied from the left. Water 12-17 nuclear RNA export factor 1 Homo sapiens 8-11 17697181-9 2007 In particular, exposure of the contact lenses to tap water or other sources of water should be avoided. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 17697181-9 2007 In particular, exposure of the contact lenses to tap water or other sources of water should be avoided. Water 79-84 nuclear RNA export factor 1 Homo sapiens 49-52 17990551-4 2007 The surface of titania whiskers is covered by the insoluble carbonates generated from carbon dioxide produced during the degradation of organics and metal ions such as calcium in the tap water, and the activity of the titania whiskers decreases gradually till deactivation. Water 187-192 nuclear RNA export factor 1 Homo sapiens 183-186 21631794-15 2007 For chronic wounds, the relative risk of developing an infection when cleansed with tap water compared with normal saline was 0.16 (95% CI 0.01-2.96). Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 21631794-21 2007 Conclusions Although the evidence is limited one trial has suggested that the use of tap water to cleanse acute wounds reduces the infection rate and other trials conclude that there is no difference in the infection and healing rates between wounds that were not cleansed and those cleansed with tap water and other solutions. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 17938825-2 2007 These highly reactive species are formed from the reaction of hydrogen peroxide with redox metals such as copper, which are thought to be absorbed by the hair from the from-the-tap wash water. Water 186-191 nuclear RNA export factor 1 Homo sapiens 177-180 17728016-1 2007 This study examined tap water as a source of Pseudomonas aeruginosa in a medical intensive care setting. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 17728016-5 2007 P. aeruginosa was found in 11.4% of 484 tap water samples taken from patients" rooms and in 5.3% of 189 other tap water samples (P<0.01). Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 17878557-0 2007 Opportunistic Aspergillus pathogens measured in home and hospital tap water by quantitative PCR (QPCR). Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 17878557-3 2007 Water samples were taken from the kitchen tap in the homes of 60 patients who were diagnosed with legionellosis. Water 0-5 nuclear RNA export factor 1 Homo sapiens 42-45 17878557-7 2007 None of the Aspergillus species were found in any of the hospital water samples.The development of a simple DNA extraction method along with QPCR analysis is suitable for rapid screening of tap water for opportunistic fungal pathogens. Water 194-199 nuclear RNA export factor 1 Homo sapiens 190-193 17707431-9 2007 RESULTS: Tap water as a solvent had the greatest decrease in concentration, declining below 50% by week 2 and reaching 25% by week 4. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 17707431-14 2007 Tap water solvent alone should be avoided. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17903461-4 2007 The system allowed the re-circulation of the acceptor solution and was applied to ammonium determination in surface and tap water, providing relative standard deviations lower than 1.5%. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 17406836-4 2007 The water load test was performed by having subjects drinking room-temperature tap water at a predetermined rate of 15 ml/min. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 17822074-0 2007 Lead levels high in Canadian tap water. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 17416463-7 2007 Better results were achieved in a previous stage using tap water with nitrate added as a sole pollutant as a synthetic feed (critical load of 130 gNO(3)-N/(m(3)h) and denitrification rate of 200 gNO(3)-N/(m(3)h) at a nitrate load of 250 gNO(3)-N/(m(3)h)). Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 17478044-1 2007 INTRODUCTION: Tap water scalds among those >or=60 years old are often attributed to physical impairments with aging. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 17478044-2 2007 This study assesses socio-economics associated with tap water scalds among seniors and the elderly. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 17478044-13 2007 CONCLUSION: These findings report that tap water scalds result in significant morbidity, mortality and health care costs for local seniors and the elderly. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 17688298-2 2007 A study of radioactivity content in tap water samples collected in the Central Italy was performed in order to check the compliance with recent European regulations. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 17574561-10 2007 The performance of the method was checked by analysis of river and tap water samples, and the relative recoveries of triazines from river and tap water at a spiking level of 5.0 microg L(-1) were 85.2-114.5% and 87.8-119.4%, respectively. Water 146-151 nuclear RNA export factor 1 Homo sapiens 142-145 17931998-7 2007 During procedure the patients injected tap water (300-450 ml) through the (neo-)appendicostomy with a thin catheter. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 17499836-0 2007 Superparamagnetic nanoparticles in tap water. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 17499259-1 2007 A disk-type solid-phase extraction (SPE) method was used for the extraction of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) in natural water and tap water. Water 166-171 nuclear RNA export factor 1 Homo sapiens 162-165 17535441-8 2007 Using a combination of case control methodology and spatial analysis, the spatial patterns of THMs and individual measures of tap water consumption provide estimates of the effects of ingestion of specific amounts of some DBPs on rectal cancer risk. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 17490771-6 2007 The probability of detecting positive samples was 50% (the critical level of detection) when 2 l samples of tap water were inoculated with 0.7 log PFU of HAV, 25 g samples of iceberg lettuce were inoculated with 1.0 log PFU of HAV, and 25 g samples of fresh and frozen raspberries were inoculated with 1.0 and 1.5 log PFU of HAV, respectively. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 17503254-4 2007 Although urinary arsenic concentration increased with higher exposure in tap water, urinary 8-OHdG concentration did not differ by community within Arizona or Sonora, and was not associated with urinary arsenic concentration. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 17693308-8 2007 This technique was successfully applied to the analysis of copper in tap water representing the first successful copper determination in real samples using the BFE. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 17089219-7 2007 The WOMAC activity, pain, and total scores improved significantly also in the tap water group at the end of the treatment course, but no improvement was detected at the end of the 3-month follow-up period. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 17538754-12 2007 The prevalence of infection among people who drank water from wells was 92 percent compared with 74.8 percent of those who drank tap water (p-value is less than 0.001). Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 17377785-5 2007 Tap water and surface water samples collected from our laboratory and Wohushan reservoir, respectively, were successfully analyzed using the proposed method. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17767880-7 2007 The main source of water for drinking and daily life among emigrations was tap water (85.4% and 87.0%). Water 19-24 nuclear RNA export factor 1 Homo sapiens 75-78 17767880-7 2007 The main source of water for drinking and daily life among emigrations was tap water (85.4% and 87.0%). Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 17363038-5 2007 The relatively low capacity in treating As-spiked tap water arose from the suppression of FeCO(3) dissolution in the presence of high HCO(3)(-) concentration (333 mg/L), which consequently limited the formation of fresh Fe(III) oxides. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 17363038-6 2007 However, the H(2)O(2)-conditioning greatly increased As adsorption capacity of the column for remediating As-spiked tap water. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 17456554-1 2007 OBJECTIVES: To compare wound infection rates for irrigation with tap water versus sterile saline before closure of wounds in the emergency department. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 17402708-1 2007 A novel method for the determination of hepatotoxins; microcystins (MCs), and nodularin (Nod) in lake water and domestic chlorinated tap water has been developed using liquid chromatography hyphenated with electrospray ionization triple quadrupole mass spectrometry (LC-ESI-MS/MS). Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 17402708-12 2007 The application of this LC-ESI-MS/MS method for routine screening of hepatotoxins in lake and chlorinated tap water (average Cl2=0.23 mg/L) is achieved and this study represents the first direct method for the screening of hepatotoxins in chlorinated tap water. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 17495409-3 2007 This proposed method has excellent reproducibility, and was applied to recovery tests of oxalate ion in tap water and human urine; the results were satisfactory. Water 108-113 nuclear RNA export factor 1 Homo sapiens 104-107 17485621-0 2007 Bottled, filtered, and tap water use in Latino and non-Latino children. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 17485621-9 2007 Latino parents were less likely than non-Latino parents to drink tap water (odds ratio, 0.26; 95% confidence interval, 0.10-0.67) and less likely to give tap water to their children (odds ratio, 0.32; 95% confidence interval, 0.15-0.70). Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 17485621-10 2007 More Latinos believed that tap water would make them sick (odds ratio, 5.63; 95% confidence interval, 2.17-14.54). Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 17485621-14 2007 CONCLUSIONS: Many Latino families avoid drinking tap water because they fear it causes illness. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 17596097-1 2007 When topical therapy and tap water iontophoresis (TWI) fail, are unavailable, or are deemed unsatisfactory by patients with palmar or plantar hyperhidrosis (HH), the next logical treatment option is botulinum toxin type A (BTX-A). Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 17502745-9 2007 CONCLUSIONS: The important message conveyed by this case was the finding that for several years, unknown to his eye care physicians, the patient cleaned his lenses with the Boston Cleaning System, as instructed, but followed this step with a routine rinse with tap water and storage in tap water in his lens case, which was not replaced or cleaned. Water 265-270 nuclear RNA export factor 1 Homo sapiens 261-264 17502745-9 2007 CONCLUSIONS: The important message conveyed by this case was the finding that for several years, unknown to his eye care physicians, the patient cleaned his lenses with the Boston Cleaning System, as instructed, but followed this step with a routine rinse with tap water and storage in tap water in his lens case, which was not replaced or cleaned. Water 265-270 nuclear RNA export factor 1 Homo sapiens 286-289 17502745-9 2007 CONCLUSIONS: The important message conveyed by this case was the finding that for several years, unknown to his eye care physicians, the patient cleaned his lenses with the Boston Cleaning System, as instructed, but followed this step with a routine rinse with tap water and storage in tap water in his lens case, which was not replaced or cleaned. Water 290-295 nuclear RNA export factor 1 Homo sapiens 261-264 17250866-6 2007 This phenomenon was observed not only in the filtration of carbonate solution, but also in the filtration of the NaCl solution and the tap water. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 17123683-8 2007 There were no statistical differences among these groups except isotonic saline, at 3min post-exposure (in wash solutions), showed a significantly difference (p<0.05) when compared to tap water. Water 191-196 nuclear RNA export factor 1 Homo sapiens 187-190 18489334-14 2007 While in the mineral water group finger circumference decreased significantly, measurements in the tap water group revealed a statistically significant increase. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 17237925-4 2007 Addition of sodium thiosulfate to tap water prevented pyrethroid degradation as a result of oxidation by free chlorine. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 17334887-1 2007 The new German Drinking Water Ordinance (TrinkwV 2001) demands that the requirements of water intended for human consumption be met up to the intrinsic tap, at which the water is used. Water 24-29 nuclear RNA export factor 1 Homo sapiens 152-155 17334887-1 2007 The new German Drinking Water Ordinance (TrinkwV 2001) demands that the requirements of water intended for human consumption be met up to the intrinsic tap, at which the water is used. Water 170-175 nuclear RNA export factor 1 Homo sapiens 152-155 17334889-2 2007 These regulations have to ensure that legal requirements on drinking water are met at the tap. Water 69-74 nuclear RNA export factor 1 Homo sapiens 90-93 16670711-8 2007 Non-Hispanic white women drank 0.4 (95% confidence interval (CI) 0.2; 0.7) liters more cold tap water per day than Hispanic women and 0.3 (95% CI 0.1; 0.4) liters more than non-Hispanic black women. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 16670711-9 2007 Non-Hispanic white women also reported drinking a higher proportion of filtered tap water, whereas Hispanic women replaced more of their tap water with bottled water. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 16670711-9 2007 Non-Hispanic white women also reported drinking a higher proportion of filtered tap water, whereas Hispanic women replaced more of their tap water with bottled water. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 17521416-0 2007 Hygienic safety of reusable tap water filters (Germlyser) with an operating time of 4 or 8 weeks in a haematological oncology transplantation unit. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 17521416-1 2007 BACKGROUND: Microbial safe tap water is crucial for the safety of immunosuppressed patients. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 17521416-10 2007 Using a validated reprocessing in a washer/disinfector with alkaline, acid treatment and thermic disinfection, the filters were effectively reprocessable and now provide tap water meeting the German drinking water regulations as well as the WHO guidelines, including absence of pathogens. Water 174-179 nuclear RNA export factor 1 Homo sapiens 170-173 17521416-10 2007 Using a validated reprocessing in a washer/disinfector with alkaline, acid treatment and thermic disinfection, the filters were effectively reprocessable and now provide tap water meeting the German drinking water regulations as well as the WHO guidelines, including absence of pathogens. Water 208-213 nuclear RNA export factor 1 Homo sapiens 170-173 19071743-5 2007 Based on these features, the system was applied to tap-water and surface water samples with no previous treatment required. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 17482933-14 2007 Potential causes of P. aeruginosa contamination include the lack of adequate manual cleaning before disinfection, failure to sterilize the needle guide, and the use of a tap-water rinse after disinfection. Water 174-179 nuclear RNA export factor 1 Homo sapiens 170-173 19554128-0 2007 Rate of pediatric tap water scald injuries in eastern Ontario. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 19554128-1 2007 BACKGROUND: Tap water scalds can be devastating and are entirely preventable. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 19554128-4 2007 OBJECTIVES: The present study evaluated the rate of pediatric tap water scalds in Ottawa, Ontario over the 10-year period from 1993 to 2002 in an attempt to identify the impact of this national awareness campaign. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 19554128-5 2007 METHODS: Data from the Children"s Hospital of Eastern Ontario available in the Canadian Hospitals Injury Reporting and Prevention Program database were used to calculate the yearly incidence density of tap water scalds among children younger than 15 years in the city of Ottawa. Water 206-211 nuclear RNA export factor 1 Homo sapiens 202-205 17318683-3 2007 The first substance was a 10-ml solution of tap water with 0.5% xanthan with a viscosity of 4500 mPa s, comparable to a yogurt drink. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 17318683-5 2007 Tap water was used as the control substance. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17318683-6 2007 Mean pharyngeal residue after swallowing tap water was 2.3% (SD = 1.2) of the initial volume in the oral cavity. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 16938388-10 2007 It was noticed that tap water has no effect in leaching of arsenic from CalSiCo-sludge but rain water causes significant amount of leaching, which is mostly due to pH effect. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 17375781-6 2007 Burns by child abuse occur mostly from tap water (50%) and usually in children less than 2 years old. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 18240489-8 2007 The amount of water flowing through the tap per minute was also recorded. Water 14-19 nuclear RNA export factor 1 Homo sapiens 40-43 17432377-0 2007 Floc size distributions in dissolved air flotation of Winnipeg tap water. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 17432377-1 2007 A bench-scale continuous flow dissolved air flotation (DAF) system was operated using Winnipeg tap water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 17432377-5 2007 At this dosage, the DAF effluent achieved a turbidity of 0.25 NTU and color of 3.8 TCU, significantly lower than that for the tap water. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 19071348-6 2007 The method was applied to the determination of uranium(VI) in tap water, waste-water and well water samples. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 17402285-0 2007 Unsafe tap water in households supplied from groundwater in the Salento Region of Southern Italy. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 17402289-1 2007 The consumption of bottled and plastic-bagged drinking water in Tanzania has increased largely because of the deteriorating quality of tap water. Water 55-60 nuclear RNA export factor 1 Homo sapiens 135-138 17402289-8 2007 Microbiological quality of tap water was found to be worse compared with bottled water, with 49.2% and 26.2% of sampling points showing the presence of total coliform and faecal coliform organisms, respectively. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 17204273-6 2007 The method was validated at levels of 0.25, 1.0, and 5.0 microg/L in the tap water and river water samples, and accuracy was achieved in the range of 94-109%. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 17180336-8 2007 Application of the electrodes to determine perchlorate in tap water and human urine is also reported. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 17377749-3 2007 They had used a contact lens care system irregularly with tap water. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 17377749-7 2007 Careful contact lens management is needed and tap-water rinsing should be eliminated from the lens care regimen. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 17255419-5 2007 Patients drank 800-1000 mL of tap water to establish a background for dynamic contrast-enhanced CT scans. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 17365576-6 2007 When arsenic intake from consumption of tap water and beverages made from tap water (microg/L arsenic x L/d = microg/d) was used as a predictor variable, the correlation was markedly increased for individuals with >1 microg/L arsenic (R2 = .48). Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 17365576-6 2007 When arsenic intake from consumption of tap water and beverages made from tap water (microg/L arsenic x L/d = microg/d) was used as a predictor variable, the correlation was markedly increased for individuals with >1 microg/L arsenic (R2 = .48). Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 17214679-1 2007 BACKGROUND: Palmar hyperhidrosis is characterized by excessive sweating on the palm, and among the various treatment modalities, tap water iontophoresis has been widely used. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 17455864-8 2007 Other potential risk factors for bladder cancer are other urinary tract infections and drinking tap water with chlorination by-products or arsenic. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 17890843-0 2007 Estimation of the consumption of cold tap water for microbiological risk assessment: an overview of studies and statistical analysis of data. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 17890843-1 2007 The volume of cold tap water consumed is an essential element in quantitative microbial risk assessment. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 17890843-2 2007 This paper presents a review of tap water consumption studies. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 17366900-6 2007 Compared with the coefficient value in tap water, that in synthetic wastewater and industrial wastewater is decreased by 39.0% and 50.9%, respectively. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 16455284-3 2007 Below are presented results of investigations into the influence of temperature, gas content and the solution level in an ultrasonic cleaner on cavitation intensity in the tap water. Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 16455284-5 2007 It has now been found that the tap water reaches the highest cavitation intensity at temperatures below 20 degrees C but during heating at higher temperatures (20-40 degrees C) a second peak of cavitation intensity may appear-depending on the height of water in the bath and air content. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 16455284-5 2007 It has now been found that the tap water reaches the highest cavitation intensity at temperatures below 20 degrees C but during heating at higher temperatures (20-40 degrees C) a second peak of cavitation intensity may appear-depending on the height of water in the bath and air content. Water 253-258 nuclear RNA export factor 1 Homo sapiens 31-34 17489418-6 2007 In addition, water utilities can characterise their tap water flavour, track it for changes and correlate changes to customer complaints. Water 13-18 nuclear RNA export factor 1 Homo sapiens 52-55 17425085-9 2007 When flushed with tap water, nitrogen and phosphorus were retained by the vegetated mesocosms, but leached from the non-vegetated mesocosms. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 17489396-3 2007 A case study that uses untrained citizens to monitor chlorine flavour of tap water is presented. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 17489418-6 2007 In addition, water utilities can characterise their tap water flavour, track it for changes and correlate changes to customer complaints. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 17489422-6 2007 Therefore, dechlorinated tap water may be the best background water to use for a particular drinking water evaluation of chlorine and chloramine thresholds. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 17489422-6 2007 Therefore, dechlorinated tap water may be the best background water to use for a particular drinking water evaluation of chlorine and chloramine thresholds. Water 62-67 nuclear RNA export factor 1 Homo sapiens 25-28 17180999-4 2006 The concentration of noroviruses in tap water was estimated based on qualitative data and a most probable number (MPN) method with an assumed Poisson lognormal distribution. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 17849979-4 2007 A pilot scale hollow fibre MBR system of 220 L was fed by adequately diluting white wine with tap water, simulating wastewaters generated in wineries. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 17386527-9 2007 Application to the analysis in pesticide spiked samples of tap water and fruit yields satisfactory apparent recoveries (84-114%), and for the extraction procedure in fruits and a commercial formulation, recoveries were of 81-98% and 104%, respectively. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 17180999-5 2006 This numerical method was evaluated using two sets of available count data of Cryptosporidium: that collected from a river and that found in tap water in Japan. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 17176821-5 2006 The average daily consumption of tap water as plain drinking water and as heated tap water, e.g. in coffee and tea, was 0.86 +/- 0.48 l and 0.94 +/- 0.69 l, respectively. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 17174662-3 2006 PURPOSE: The purpose of this study was to compare the setting behavior of irreversible hydrocolloid impression materials when mixed with tap and distilled water, and to determine the impact of typical cations present in tap water and their concentrations on the setting process. Water 224-229 nuclear RNA export factor 1 Homo sapiens 220-223 17174662-9 2006 RESULTS: Statistical analysis showed significant (P<.001) acceleration in the setting rate for Kromopan 100, the working time of which was shorter with tap water by 23.4 seconds and the setting time, by 32.8 seconds. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 17176821-5 2006 The average daily consumption of tap water as plain drinking water and as heated tap water, e.g. in coffee and tea, was 0.86 +/- 0.48 l and 0.94 +/- 0.69 l, respectively. Water 37-42 nuclear RNA export factor 1 Homo sapiens 81-84 17174662-11 2006 At the same time, the rigidity of the set impression materials mixed with tap water increased by approximately 10%. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 17176821-5 2006 The average daily consumption of tap water as plain drinking water and as heated tap water, e.g. in coffee and tea, was 0.86 +/- 0.48 l and 0.94 +/- 0.69 l, respectively. Water 61-66 nuclear RNA export factor 1 Homo sapiens 33-36 17174662-12 2006 With Ypeen Premium, the setting time decreased significantly by 20.0 seconds (P<.001) with tap water, while the working time and rigidity did not change. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 17176821-5 2006 The average daily consumption of tap water as plain drinking water and as heated tap water, e.g. in coffee and tea, was 0.86 +/- 0.48 l and 0.94 +/- 0.69 l, respectively. Water 61-66 nuclear RNA export factor 1 Homo sapiens 33-36 17174662-15 2006 CONCLUSION: Setting of irreversible hydrocolloid impression materials can be significantly accelerated when tap water with high water hardness is used for mixing or when the mixing water contains higher concentrations of cations such as Na(+), Ca(2+), and Al(3+). Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 17174662-15 2006 CONCLUSION: Setting of irreversible hydrocolloid impression materials can be significantly accelerated when tap water with high water hardness is used for mixing or when the mixing water contains higher concentrations of cations such as Na(+), Ca(2+), and Al(3+). Water 128-133 nuclear RNA export factor 1 Homo sapiens 108-111 17174662-15 2006 CONCLUSION: Setting of irreversible hydrocolloid impression materials can be significantly accelerated when tap water with high water hardness is used for mixing or when the mixing water contains higher concentrations of cations such as Na(+), Ca(2+), and Al(3+). Water 128-133 nuclear RNA export factor 1 Homo sapiens 108-111 17176821-6 2006 Women consumed more cold tap water than did men, while men appeared to have a higher consumption of heated tap water. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 17176821-7 2006 Cold tap water intake was highest in the oldest age group, (> or =70 years). Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 17288152-1 2006 A novel technique of liquid phase microextraction supported by hollow fiber membrane (LPME-HFM) was applied to extract tramadol in tap water, urine and human plasma. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 17091438-7 2006 2000 ml of tap water. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 17217173-7 2006 The method has been successfully applied for determination of trace amounts of thiocyanate in tap water, saliva sample and a synthetic mixture. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 16487958-6 2006 Household tap water arsenic levels in Ajo (20.3+/-3.7 microg/L) were higher than in those Tucson (4.0+/-2.3 microg/L), as were mean urinary total inorganic arsenic levels (29.1+/-20.4 and 11.0+/-12.0 microg/L, respectively). Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 27718711-1 2006 The valves set bath tap water temperature to a maximum of 48 C. The ECA steering committee has submitted the subject of Ms Creagh"s Hot Water Burns Like Fire campaign as a matter for discussion at RCN congress, next April. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 17144261-3 2006 The volumetric oxygen transfer coefficient (kLa) values for superficial air velocities between 8.4 cm min(-1) and 57.0 cm min(-1) varied from 20.8 h(-1) to 58.8 h(-1) for tap water, and 16.8 h(-1) to 53.0 h(-1) for the anaerobic pre-treated effluent. Water 175-180 nuclear RNA export factor 1 Homo sapiens 171-174 16990636-4 2006 In phase B, tap water and the concentration that yielded the best pellet delivery from phase A were used with the narrower size 8 and shorter size 20 French tubes. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 17367032-7 2006 In the in vitro experiment, Periogard exhibited the greatest inhibition halo average, followed by the experimental solution, Brushtox, and sterile tap water (P<.05). Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 16982516-7 2006 The concentration of iodoacetic acid in tap water samples boiled with 2 g l-1 of iodized table salt was found to be in the 1.5 microg l-1 range, whilst the concentration of chloroiodoacetic acid was estimated to be three to five times lower. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 16990176-6 2006 In children aged 1 - 13, the only significant risk factor was the consumption of at-risk tap water (i.e., filtered or unfiltered surface water or unfiltered shallow well water; OR = 6.13). Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 16990176-6 2006 In children aged 1 - 13, the only significant risk factor was the consumption of at-risk tap water (i.e., filtered or unfiltered surface water or unfiltered shallow well water; OR = 6.13). Water 137-142 nuclear RNA export factor 1 Homo sapiens 89-92 16990176-6 2006 In children aged 1 - 13, the only significant risk factor was the consumption of at-risk tap water (i.e., filtered or unfiltered surface water or unfiltered shallow well water; OR = 6.13). Water 137-142 nuclear RNA export factor 1 Homo sapiens 89-92 17225816-1 2006 OBJECTIVES: Due to increased consumption of pre-packaged drinks, tap water may no longer be the principal source of water intake and consequently fluoride intake. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 17225816-1 2006 OBJECTIVES: Due to increased consumption of pre-packaged drinks, tap water may no longer be the principal source of water intake and consequently fluoride intake. Water 116-121 nuclear RNA export factor 1 Homo sapiens 65-68 17225816-8 2006 Tap water, fruit squashes and cordials (extremely sweet non-alcoholic fruit flavoured drink concentrates) prepared with tap water, as well as cooked rice, pasta and vegetables were important sources of fluoride in optimally and sub-optimally fluoridated areas. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17225816-8 2006 Tap water, fruit squashes and cordials (extremely sweet non-alcoholic fruit flavoured drink concentrates) prepared with tap water, as well as cooked rice, pasta and vegetables were important sources of fluoride in optimally and sub-optimally fluoridated areas. Water 124-129 nuclear RNA export factor 1 Homo sapiens 0-3 17225816-8 2006 Tap water, fruit squashes and cordials (extremely sweet non-alcoholic fruit flavoured drink concentrates) prepared with tap water, as well as cooked rice, pasta and vegetables were important sources of fluoride in optimally and sub-optimally fluoridated areas. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 16840540-4 2006 The mineralized water was designed to mimic the composition of a typical tap water. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 16982516-1 2006 Iodoacetic and chloroiodoacetic acids were formed when municipal chlorinated tap water was allowed to react with iodized (with potassium iodide) table salt or with potassium iodide itself. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 16970300-9 2006 The electrode was applicable for analysis of spiked arsenic in tap water containing a significant amount of various ion elements. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 16966806-5 2006 With the high sensitivity of the method, Pb(II), Cu(II) and Fe(III) in tap water were successfully determined, and the recoveries were 99 - 105%. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 16966806-6 2006 The concentrations of these metal ions found in tap water did not exceed the maximum allowed concentrations regulated by the U.S. Environmental Protection Agency. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 16840540-4 2006 The mineralized water was designed to mimic the composition of a typical tap water. Water 16-21 nuclear RNA export factor 1 Homo sapiens 73-76 17366771-4 2006 The mean total arsenic (microg/L) in tap-water was 20.3+/-3.7 in Ajo and 4.0+/-2.3 in Tucson. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 17367032-8 2006 CONCLUSIONS: After a single brushing, severe contamination by mutans streptococci colonies/biofilms was observed on all toothbrushes sprayed with sterile tap water (control). Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 17723578-6 2006 Half-lives values obtained for model ultrapure water solutions were in good agreement with those observed in tap water samples. Water 47-52 nuclear RNA export factor 1 Homo sapiens 109-112 17723578-6 2006 Half-lives values obtained for model ultrapure water solutions were in good agreement with those observed in tap water samples. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 17723578-9 2006 Both species were also generated after the addition of parabens to chlorinated tap water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 17723578-11 2006 They were identified as bromo- and bromochloro-parabens, formed due to the existence of traces of bromide in tap water sources. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 17723578-12 2006 Experiments carried out by mixing paraben-containing personal care products with tap water, containing free chlorine, confirmed the formation of all above described halogenated by-products. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 16813019-3 2006 Consumer surveys usually stress two main factors: dissatisfaction with tap water organoleptics (especially taste) and health/risk concerns. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 16953177-2 2006 Tap water was electrolyzed in a water vessel using platinum cell technology. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 16953177-3 2006 The electrolyzed tap water (called Puri-water) was put in contact with five major periodontopathogens or toothbrushes contaminated with these bacteria for 30 sec. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 16953177-7 2006 Our results demonstrate that the electrolyzed tap water is effective as a mouthwash and for toothbrush disinfection. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 17723474-5 2006 Water samples including tap water, well water, snow water, reservoir water, and wastewater were analyzed by the proposed procedure and the recoveries at 5 microg L(-1) spiked level were in the range of 86.8-102.6%. Water 0-5 nuclear RNA export factor 1 Homo sapiens 24-27 16452917-17 2006 Households with tube well water had the worst BMI compared with those with tap water (P<0.001). Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 16740415-0 2006 Common RAPD pattern of Pseudomonas aeruginosa from patients and tap water in a medical intensive care unit. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 17044511-4 2006 Water quality also had a significant effect, with a decreasing degradation rate of chlorpyrifos in the sequence of distilled water > tap water > river water > lake wate > paddy water. Water 0-5 nuclear RNA export factor 1 Homo sapiens 136-139 17044511-4 2006 Water quality also had a significant effect, with a decreasing degradation rate of chlorpyrifos in the sequence of distilled water > tap water > river water > lake wate > paddy water. Water 125-130 nuclear RNA export factor 1 Homo sapiens 136-139 16643833-1 2006 We describe a simple, rapid, and sensitive fluorescence method for measurement of aluminum (Al) in human biological fluids, in dialysis solutions, and in tap water, which uses 8-hydroxyquinoline for ion chelation. Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 16832971-1 2006 Today, bottled and tap drinking water mainly originates from underground waters which might contain considerable amounts of naturally occurring radionuclides. Water 32-37 nuclear RNA export factor 1 Homo sapiens 19-22 16700706-4 2006 Those who had drunk tap water had a three-fold increased risk for illness (95% CI 2.4-4.0). Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 16917709-5 2006 The highest levels of salinity was evident in tap water. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 16981089-4 2006 Tap water was used for irrigations after discharge from hospital. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 16902368-6 2006 For public water users, the best-fit model included age, tap water drinks per day, servings of home-grown fruit and vegetables, and carbon filter use. Water 11-16 nuclear RNA export factor 1 Homo sapiens 57-60 16889815-2 2006 Tap water samples collected in the Quebec City (Canada) distribution system on a spatio-temporal basis were subjected to diverse indoor handling scenarios: storing water in the refrigerator, boiling water followed by storage and, finally, filtering water with a point-of-use commercial pitcher also followed by storage. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 16889815-10 2006 Percentages of change in chlorinated DBPs in the different scenarios varied according to initial concentrations in tap water (baseline water), that is, according to the spatio-temporal variations of these substances in the distribution system. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 16889815-10 2006 Percentages of change in chlorinated DBPs in the different scenarios varied according to initial concentrations in tap water (baseline water), that is, according to the spatio-temporal variations of these substances in the distribution system. Water 135-140 nuclear RNA export factor 1 Homo sapiens 115-118 16836953-2 2006 Diagnostic testing and long-term treatment are best initiated after disimpaction has been achieved, by large-volume tap water enemas and/or oral colonic lavage with polyethylene glycol. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 16807859-0 2006 Acquisition of multidrug-resistant Serratia marcescens by critically ill patients who consumed tap water during receipt of oral medication. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 16807859-2 2006 Examination of the outbreak revealed epidemiological evidence that consumption of tap water from a contaminated faucet during receipt of oral medication was the mechanism of S. marcescens acquisition. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 16672062-4 2006 METHODS: The study combined a daily follow-up of digestive morbidity among a panel of 544 volunteers and a microbiological surveillance of tap water. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 18970612-7 2006 The application of the method to the analysis of water samples (tap and mineral water) gave accurate results based on recovery studies (93-106%). Water 49-54 nuclear RNA export factor 1 Homo sapiens 64-67 16679899-4 2006 This work addresses the issue of how the current safety standard for tap water temperature could be adjusted to provide a level of protection to children equivalent to that for an adult at 120 degrees F. A well-accepted mathematical model for predicting burn injury as a function of applied surface temperature and time is used to identify these equivalent conditions. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 16740415-9 2006 Isolates from patients showed a similar distribution of genotypes as did tap water isolates, and strains of identical genotype as patient strains had been isolated previously from tap water outlets in 8 out of 16 (50%) infection or colonization episodes. Water 184-189 nuclear RNA export factor 1 Homo sapiens 180-183 16284957-11 2006 The association of bladder cancer with tap water consumption, but not with nontap water fluids, suggests that carcinogenic chemicals in tap water may explain the increased risk. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 16827181-4 2006 The terminal volume of tap water in copper and steel water pipes should be not less than 0.1 liter, whereas that in plastic water pipes should be not less than 1 liter. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 16760588-1 2006 A target value for iminoctadine triacetate residues in tap water was set at 6 microg/l in Japan. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 16760598-7 2006 Tap water samples from a laboratory were successfully analyzed using the proposed method. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 16827181-4 2006 The terminal volume of tap water in copper and steel water pipes should be not less than 0.1 liter, whereas that in plastic water pipes should be not less than 1 liter. Water 53-58 nuclear RNA export factor 1 Homo sapiens 23-26 16827181-4 2006 The terminal volume of tap water in copper and steel water pipes should be not less than 0.1 liter, whereas that in plastic water pipes should be not less than 1 liter. Water 53-58 nuclear RNA export factor 1 Homo sapiens 23-26 16581538-9 2006 For chloroform from showering, strong correlations were observed for indoor air and exhaled breath, blood and exhaled breath, indoor air and blood, and tap water and blood. Water 156-161 nuclear RNA export factor 1 Homo sapiens 152-155 16608596-14 2006 RESULTS: Tap water was the poorest cleaning solution, while UltraDose was the most effective. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 16583822-0 2006 Characteristics of biofilm community formed in the chlorinated biodegradable organic matter-limited tap water. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 16115838-9 2006 Tap water sprinkling and occasionally alcohol were used. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 16497651-0 2006 Tap-water enema for children with myelomeningocele and neurogenic bowel dysfunction. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 16497651-1 2006 AIM: To evaluate the outcome of transrectal irrigation (TRI) using clean tap water without salt in children with myelomeningocele and neurogenic bowel problems. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 16497651-9 2006 CONCLUSION: Transrectal irrigation with tap water is a safe method to resolve constipation and faecal incontinence in children with myelomeningocele and neurogenic bowel dysfunction, but it does not help children to independence at the toilet. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 16517632-10 2006 Furthermore, the community structure of the tap water did not change substantially for several months. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 23105572-7 2006 Mean arsenic level detected in samples collected from tap water supply was 0.013 ppm (Range 0-0.0430 ppm, Standard Deviation 0.00911 and Standard error of Mean 0.000515). Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 23105572-9 2006 The mean arsenic level detected in water samples of booster pumping station was within WHO/EPA permissible limit while mean arsenic level detected in tap water samples was marginally higher. Water 154-159 nuclear RNA export factor 1 Homo sapiens 150-153 23105572-10 2006 Mixing of ground water and contamination through broken or leaking channel could be the possible reason of higher arsenic level in tap water. Water 17-22 nuclear RNA export factor 1 Homo sapiens 131-134 23105572-10 2006 Mixing of ground water and contamination through broken or leaking channel could be the possible reason of higher arsenic level in tap water. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 16194574-7 2006 Tap water recoveries averaged 32% for new filters, 30% for filters used twice, and 38% for filters used three times. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 16304088-5 2006 For MR colonography, the colon was filled with approximately 2000 mL of tap water. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 16604844-4 2006 Approximately 49% of households used water treatment devices to treat their tap water. Water 37-42 nuclear RNA export factor 1 Homo sapiens 76-79 16604844-4 2006 Approximately 49% of households used water treatment devices to treat their tap water. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 16516263-9 2006 Finally, the results of discriminant function analysis showed that in rural households, garden size, greenhouse size, and garden watering times per month with tap treated water are associated with water consumption. Water 129-134 nuclear RNA export factor 1 Homo sapiens 159-162 16516263-9 2006 Finally, the results of discriminant function analysis showed that in rural households, garden size, greenhouse size, and garden watering times per month with tap treated water are associated with water consumption. Water 171-176 nuclear RNA export factor 1 Homo sapiens 159-162 16408926-1 2006 The method presented here provides a direct way to determine mercury in tap water samples at the parts-per-trillion level. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 16298016-2 2006 A tap water tracer was injected into a fracture-dominated, salt-water plume formed during a previous salt-water injection experiment. Water 6-11 nuclear RNA export factor 1 Homo sapiens 2-5 16298016-2 2006 A tap water tracer was injected into a fracture-dominated, salt-water plume formed during a previous salt-water injection experiment. Water 64-69 nuclear RNA export factor 1 Homo sapiens 2-5 16298016-2 2006 A tap water tracer was injected into a fracture-dominated, salt-water plume formed during a previous salt-water injection experiment. Water 64-69 nuclear RNA export factor 1 Homo sapiens 2-5 16298016-3 2006 The tap water tracer was injected into a central injection well under constant hydraulic head for 34 days. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 16023177-1 2006 The paper presents the results of determination of volatile organohalogen compounds (VOX) in urine samples from subjects exposed to these compounds in their workplaces and through consumption of chlorinated tap water. Water 211-216 nuclear RNA export factor 1 Homo sapiens 207-210 16023177-7 2006 Their presence in the organisms was most probably related to consumption of tap water produced by chlorination of surface waters. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 16154195-2 2006 The most dominant THM compounds are chloroform, bromodichloromethane (BDCM), and dibromochloromethane (DBCM) in Istanbul tap water. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 16154195-5 2006 The lifetime cancer risks of chloroform, BDCM, and DBCM from tap water of all 15 districts were higher than 10(-6), the negligible risk level defined by the USEPA. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 16702240-3 2006 The mean values of tap water and well water were found to be 12 kBq m(-3) with a maximum of 18 kBq m(-3) and 41 kBq m(-3) with a maximum of 127 kBq m(-3), respectively. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 17176650-8 2006 Fluoridated tap water was associated with an overall improved profile of caries, concurrent with an expressively larger inequality in the distribution of dental disease. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 16399605-5 2006 Short- and long-term tap water alternatives are suggested for when tap water is deemed unsuitable for use. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 16399605-5 2006 Short- and long-term tap water alternatives are suggested for when tap water is deemed unsuitable for use. Water 25-30 nuclear RNA export factor 1 Homo sapiens 67-70 16399605-5 2006 Short- and long-term tap water alternatives are suggested for when tap water is deemed unsuitable for use. Water 71-76 nuclear RNA export factor 1 Homo sapiens 21-24 16399605-5 2006 Short- and long-term tap water alternatives are suggested for when tap water is deemed unsuitable for use. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 16785752-7 2006 CONCLUSION: Immediate copious irrigation with tap water reduced the severity in alkali burns of the eye and shortened the healing time. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 16440156-1 2006 PURPOSE: In Japan, sterile water is used for rinsing in surgical handwashing, whereas in Western countries tap water is generally used. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 16440156-2 2006 We conducted this study to examine the conditions and the equipment that affect bacterial contamination in tap water and to determine whether the tap water in our institute is suitable for surgical handwashing. Water 150-155 nuclear RNA export factor 1 Homo sapiens 146-149 16440156-3 2006 METHODS: First, we examined the water pipes and measured the free chlorine content in the tap water in the operating room. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 16440156-6 2006 RESULTS: The mean free chlorine levels in the tap water and the sterile water were 0.30 +/- 0.05 and 0.07 +/- 0.03 mg/l, respectively. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 16440156-7 2006 The handwashing test using tap water showed immediate, persistent, and cumulative bacteria activity within the minimum limits set by the Food and Drug Administration (FDA). Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 16440156-8 2006 CONCLUSION: The free chlorine levels in the tap water in our institute satisfied Japanese health regulations. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 16440156-10 2006 Thus, we conclude that this tap water is safe to use for rinsing in surgical handwashing. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 16506635-3 2005 When these agents are ineffective or the side effects too bothersome, patients often resort to palliative care, for example, with tap water, saline, bicarbonate solutions, mouthwashes, or saliva substitutes. Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 18970287-11 2005 Application of the method to tap water and two different river water samples resulted in values well confirmed by direct determinations with ET-AAS. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 16381148-1 2005 Sales of bottled water have increased dramatically in recent years, with worldwide sales of more than dollars 35 billion, largely because of the public perception of purity and safety and public concern about the quality of tap water. Water 17-22 nuclear RNA export factor 1 Homo sapiens 224-227 16236866-9 2005 We suggest that nonsterile tap water is probably a safe alternative. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 15937663-6 2005 The method was successfully used for analysis of tap-water and groundwater matrices spiked at the 0.10 microg L(-1), revealing the suitability of the method for determination of pyrethroid pesticides in real samples. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 18970321-9 2005 The developed method has been effectively applied to tap water and mineral water samples, with recoveries ranging from 90 to 102% for 5-ml samples passed through the two columns. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 16015024-0 2005 Gender difference of in vivo skin surface pH in the axilla and the effect of a standardized washing procedure with tap water. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 16122167-7 2005 The method has been used to determine heavy metal ions in tap water. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 16050503-5 2005 Drinking non-chlorinated municipal tap water was strongly associated with illness (OR 34.4). Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 16163011-10 2005 The high frequency of Acanthamoeba infection strongly suggests that tap water rinsing should be eliminated from the lens care regimen for overnight OK. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 29569550-9 2005 The accuracy of method was verified using a real sample (spiked tap water) by standard addition calibration technique. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 16137981-11 2005 By contrast, hydrotherapy with tap water resulted only in the temporary improvement of just a single parameter: the VAS score improved significantly (p < 0.01). Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 15976248-4 2005 In the Azunol group, patients gargled with 4 mg Azunol diluted with 100 mL tap water (40 microg/mL). Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 15976248-5 2005 In the control group, patients gargled with 100 mL of tap water. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 16002374-1 2005 Individual exposure to trihalomethanes (THMs) in tap water can occur through ingestion, inhalation, or dermal exposure. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 16002374-4 2005 We conducted our study at a single residence in each of two water utility service areas, one with relatively high and the other low total THM in the residence tap water. Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 16149302-0 2005 [Impact of iodination on the total mutagenic activity of chlorinated tap water]. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 16149302-1 2005 The impact of iodination on the total mutagenic activity (TMA) of chlorinated tap water was studied. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 16149302-5 2005 Iodination substantially reduced the TMA of chlorinated tap water. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 16149302-6 2005 The minimally effective dose of iodine against the TMA of chlorinated tap water was 1 mg/l, as evidenced by the tests using all the strains/variants and 0.5 mg/l, as shown by the tests using the strain TA 100 in the variant without metabolic activation. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 15690178-0 2005 Reusable terminal tap water filters for nosocomial legionellosis prevention. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 15866015-5 2005 by the use of disposable, terminal tap water filter systems with non-impregnated, as well as impregnated, filters with prolonged usage intervals. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 16046831-4 2005 We used tap water to wash the hands at the sink used for washing surgical instruments in the operating room and non sterilized plastic brushes. Water 12-17 nuclear RNA export factor 1 Homo sapiens 8-11 16046831-9 2005 When using tap water for surgical hand washing, 1) the hand-rubbing method should be used; 2) a quick-alcohol-based disinfectant scrub should be used; 3) the concentration of free chloride in the water should be maintained at over 0.1 PPM; 4) the bacterial contamination of the water should be checked; and 5) the faucet should be routinely cleaned and sterilized. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 16075942-2 2005 Earlier results from San Francisco suggested an association (OR 6.76) between tap water and cryptosporidiosis among HIV + persons. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 15951638-3 2005 Four house tap water samples from residents, whose contact lens storage cases had been contaminated by Acanthamoeba, were also found to be contaminated with Acanthamoeba. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 15951638-8 2005 Water storage tanks appear to promote FLA colonization, including Acanthamoeba, in domestic tap water. Water 0-5 nuclear RNA export factor 1 Homo sapiens 92-95 15941051-2 2005 This method makes it possible to quantify 0.3 microg/l of polycarbamate in tap water, which is a 1/100 of the residual target value of 30 microg/l in Japan. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 15880964-7 2005 The mean (+/- SD) fluoride content for all tap water was 0.20 +/- 0.17 microg F/g (ranging from 0.01 to 0.88 microg F/g) and 0.24 +/- 0.24 microg F/g for all bottled water (ranging from 0.01 to 2.80 microg F/g). Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 15940115-3 2005 The application of molecular typing methods made it possible, during the last approximately 7 years, to identify ICU tap water as a significant source of exogenous P aeruginosa isolates. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 15940115-4 2005 A review of prospective studies published between 1998 and 2005 showed that between 9.7% and 68.1% of randomly taken tap water samples on different types of ICUs were positive for P aeruginosa , and between 14.2% and 50% of infection/colonization episodes in patients were due to genotypes found in ICU water. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 15721893-0 2005 Bladder cancer mortality reduction after installation of a tap-water supply system in an arsenious-endemic area in southwestern Taiwan. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 16001369-4 2005 An optimal water treatment system should include tap water pre-treatment and a double reverse osmosis process. Water 11-16 nuclear RNA export factor 1 Homo sapiens 49-52 16001369-9 2005 Treated tap water used to prepare dialysis fluid should be within European Pharmacopoeia limits at the water treatment system inlet and at the reverse osmosis outlet. Water 12-17 nuclear RNA export factor 1 Homo sapiens 8-11 16001369-9 2005 Treated tap water used to prepare dialysis fluid should be within European Pharmacopoeia limits at the water treatment system inlet and at the reverse osmosis outlet. Water 103-108 nuclear RNA export factor 1 Homo sapiens 8-11 15924307-5 2005 Application to the analysis of fortified tap water samples yielded good recovery values (91-103%, according to the herbicide). Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 16134575-2 2005 The article summarizes the literature on the dynamics of tap water lead contamination and discusses this widespread source of lead exposure in the context of the latest research evidence. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 15951854-12 2005 Whether in patients or normal subjects, drinking hard water should be avoided; tap water or low calcium content water is preferable. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 15951854-12 2005 Whether in patients or normal subjects, drinking hard water should be avoided; tap water or low calcium content water is preferable. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 15880964-14 2005 Monitoring of fluoride content of both bottled and tap water is strongly advised. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 15799243-0 2005 Airborne exposure to trihalomethanes from tap water in homes with refrigeration-type and evaporative cooling systems. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 15799243-1 2005 This study evaluates airborne concentrations of common trihalomethane compounds (THM) in selected living spaces of homes supplied with chlorinated tap water containing >85 ppb total THM. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 15714242-6 2005 Patients performed antegrade enemas every 24 to 48 hours with tap water. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 15752492-1 2005 In Thailand, surface water and groundwater are the main water sources for tap water and drinking water production. Water 21-26 nuclear RNA export factor 1 Homo sapiens 74-77 15752492-1 2005 In Thailand, surface water and groundwater are the main water sources for tap water and drinking water production. Water 37-42 nuclear RNA export factor 1 Homo sapiens 74-77 15752492-1 2005 In Thailand, surface water and groundwater are the main water sources for tap water and drinking water production. Water 37-42 nuclear RNA export factor 1 Homo sapiens 74-77 15752492-6 2005 The concentration of disinfection by-products was higher in tap water produced from Chao Praya river than from Mae Klong river. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 15733317-4 2005 METHODS: In the current analysis, we constructed a personal delivered dose (PDD) model that included personal information on tap water consumption and bathing habits so that inhalation, ingestion, and dermal absorption were also considered. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 15790122-2 2005 The method proved to be applicable to different kinds of water samples used in the experiment and tap-water samples from different suppliers. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 15790122-7 2005 For ice of tap water, which contained relatively higher amount of cations, the TSDC profiles were quite different in shape compared with the standard ice-water samples (shift of peaks A - D to higher temperature, and a strong increase in the current strength of peaks B - E). Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 16013579-0 2005 [Determination of bromodichloromethane and dibromochloromethane in tap water using headspace gas chromatography with standard addition method]. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 15782974-8 2005 The quantitation limits of these compounds ranged from 1.0 to 8.0 ng/l in 500 ml tap water samples. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 18969883-0 2005 Preconcentration and determination of ultra trace amounts of arsenic(III) and arsenic(V) in tap water and total arsenic in biological samples by cloud point extraction and electrothermal atomic absorption spectrometry. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 18969883-11 2005 The method was successfully applied to the determination of As(III) and As(V) in tap water and total arsenic in biological samples (hair and nail). Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 15740765-0 2005 Multi-route trihalomethane exposure in households using municipal tap water treated with chlorine or ozone-chlorine. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 15740765-4 2005 Similar to previous findings, the winter chloroform concentration in tap water treated with chlorine (22.1 microg/l, median) was significantly higher than that in the tap water treated with ozone-chlorine (16.8 microg/l, median). Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 15740765-4 2005 Similar to previous findings, the winter chloroform concentration in tap water treated with chlorine (22.1 microg/l, median) was significantly higher than that in the tap water treated with ozone-chlorine (16.8 microg/l, median). Water 171-176 nuclear RNA export factor 1 Homo sapiens 167-170 15689218-7 2005 Bathing in the Dead Sea salt solution significantly improved skin barrier function compared with the tap water-treated control forearm in the subgroup with elevated basal TEWL. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 15623296-6 2005 Tap water was analyzed, and lead emissions were clearly observed. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 15620895-7 2005 The method was applied to the determination of nitrite in tap water, waste water, and human urine samples. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 16961003-6 2005 Further analysis of the data suggested that tap water concentrations primarily controlled the blood concentrations from bathing exposure, whereas tap water concentrations and ambient air concentrations resulting from water use affected the blood concentrations from showering exposure. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 16961003-6 2005 Further analysis of the data suggested that tap water concentrations primarily controlled the blood concentrations from bathing exposure, whereas tap water concentrations and ambient air concentrations resulting from water use affected the blood concentrations from showering exposure. Water 150-155 nuclear RNA export factor 1 Homo sapiens 146-149 16961003-6 2005 Further analysis of the data suggested that tap water concentrations primarily controlled the blood concentrations from bathing exposure, whereas tap water concentrations and ambient air concentrations resulting from water use affected the blood concentrations from showering exposure. Water 150-155 nuclear RNA export factor 1 Homo sapiens 146-149 16312961-0 2005 Perception of tap water risks and quality: a structural equation model approach. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 16235508-17 2005 Removal of contact lenses and immediate irrigation with room temperature tap water is recommended for ocular exposures. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 15701379-3 2005 Furthermore, around 48% (123 samples) of the tap-water samples taken from 255 dwellings showed radon concentrations over the MCL. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 15561740-2 2005 Average activity concentrations of 238U, 234U and 235U in tap water from surface water were 9.6 +/- 7.1, 12.8 +/- 9.7 and 0.41 +/- 0.31 Bq m(-3), respectively, whereas from ground water they were 4.5 +/- 6.0, 5.7 +/- 6.9 and 0.19 +/- 0.27 Bq m(-3), respectively. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 15561740-2 2005 Average activity concentrations of 238U, 234U and 235U in tap water from surface water were 9.6 +/- 7.1, 12.8 +/- 9.7 and 0.41 +/- 0.31 Bq m(-3), respectively, whereas from ground water they were 4.5 +/- 6.0, 5.7 +/- 6.9 and 0.19 +/- 0.27 Bq m(-3), respectively. Water 81-86 nuclear RNA export factor 1 Homo sapiens 58-61 15561740-2 2005 Average activity concentrations of 238U, 234U and 235U in tap water from surface water were 9.6 +/- 7.1, 12.8 +/- 9.7 and 0.41 +/- 0.31 Bq m(-3), respectively, whereas from ground water they were 4.5 +/- 6.0, 5.7 +/- 6.9 and 0.19 +/- 0.27 Bq m(-3), respectively. Water 81-86 nuclear RNA export factor 1 Homo sapiens 58-61 15852985-5 2005 Abluent could eliminate nitrite effectively, whose efficiency was 1-5 times higher than that of tap water. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 15644082-9 2005 Even if cavitation intensity in glycerin solution was greater, the cavitation occurrence probability was less in glycerin solution than in tap water. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 15644082-10 2005 Our results suggest that tap water contains particles that cause an increase in the cavitation occurrence probability. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 15663308-14 2005 It was interesting to note that the removal efficiency was even better for tap water and much better for wastewater when compared to that using distilled water. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 15887563-0 2005 Development of a method for the concentration and recovery of microsporidia from tap water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 15887563-4 2005 This study details method development for the detection of microsporidia in tap water. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 15887563-10 2005 Percent recoveries for 10 L tap water samples (n = 5) using the Envirocheck sampling capsule without a density gradient purification step were 26.1+/-13.4 compared to 25+/-13.8 for samples subjected to a density gradient purification step. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 16312961-1 2005 The present study aims to test a model of tap water risk and quality perception. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 16312961-11 2005 Finally, the use of tap water to drink at home can be moderately explained and depends mostly on the ability to use alternatives (i.e. bottled water), tap water taste, and perceived risk. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 16312961-11 2005 Finally, the use of tap water to drink at home can be moderately explained and depends mostly on the ability to use alternatives (i.e. bottled water), tap water taste, and perceived risk. Water 24-29 nuclear RNA export factor 1 Homo sapiens 151-154 16312961-11 2005 Finally, the use of tap water to drink at home can be moderately explained and depends mostly on the ability to use alternatives (i.e. bottled water), tap water taste, and perceived risk. Water 143-148 nuclear RNA export factor 1 Homo sapiens 20-23 16312961-11 2005 Finally, the use of tap water to drink at home can be moderately explained and depends mostly on the ability to use alternatives (i.e. bottled water), tap water taste, and perceived risk. Water 143-148 nuclear RNA export factor 1 Homo sapiens 20-23 15828349-8 2004 The method has been applied to the determination of chromium in tap water and waste water with satisfactory results. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 15633500-8 2004 RESULTS: Air and water specimens obtained from dental units supplied with tap water had microbial counts significantly (t-test, p < 0.05) greater than IWR dental units. Water 17-22 nuclear RNA export factor 1 Homo sapiens 74-77 15633500-8 2004 RESULTS: Air and water specimens obtained from dental units supplied with tap water had microbial counts significantly (t-test, p < 0.05) greater than IWR dental units. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 15567676-12 2004 In 95.2% of the departments the nebulizers were filled with tap water and were not changed on a daily basis (81.2%). Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 15530321-1 2004 OBJECTIVE: To describe the characteristics of patients with tap-water scalds admitted to our hospital and review current knowledge on their prevention. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 15544657-4 2004 (ii) The adhesive force of specimens using tap water as a medium was approximately one-half to two-third of that of specimens using resting saliva as a medium. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 15491674-5 2004 However, lead was absent in the local tap water and only half the concentration of selenium was present in the tap water in contrast to the ice core water. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 15491674-5 2004 However, lead was absent in the local tap water and only half the concentration of selenium was present in the tap water in contrast to the ice core water. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 15541810-0 2004 Lung cancer mortality reduction after installation of tap-water supply system in an arseniasis-endemic area in Southwestern Taiwan. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 15508038-8 2004 Finally, the electrode was applied to different real samples (tap-water, urine and wine) for the analysis of trace metals with satisfactory results. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 15527429-8 2004 Bilateral glycopyrrolate was superior to both unilateral glycopyrrolate and tap water in most patients. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 15580097-1 2004 The aim of this review was to identify whether cleansing with tap water results in higher rates of wound infection or delayed healing compared with other cleansing solutions in adults or children with acute uncomplicated traumatic soft tissue wounds. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 15525622-4 2004 In the control group, patients gargled with 25 mL of tap water. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 15525622-7 2004 RESULTS: Before orotracheal intubation, all 19 patients who gargled with tap water (control group) had bacterial colonization on the posterior walls of the pharynx. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 18969645-9 2004 Low levels of dichloromethane and chloroform ranging from 0.04 to 1.13mugg(-1) were found in samples obtained from small gardens irrigated with tap water. Water 148-153 nuclear RNA export factor 1 Homo sapiens 144-147 15530321-2 2004 PATIENTS AND METHODS: We performed a retrospective study of admissions for tap-water scalds. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 15530321-3 2004 The medical records codified as water-tap scalds (MBDS; CIE-9-CM, 940.0-949.5, E.924.0, E.924.2) of patients admitted to our hospital for more than 24 hours from January 1 to December 31, 2003 were reviewed. Water 32-37 nuclear RNA export factor 1 Homo sapiens 38-41 15316185-0 2004 A probabilistic estimation of fluoride intake by infants up to the age of 4 months from infant formula reconstituted with tap water in the fluoridated regions of Ireland. Water 126-131 nuclear RNA export factor 1 Homo sapiens 122-125 15371236-0 2004 Ischemic heart disease mortality reduction in an arseniasis-endemic area in southwestern Taiwan after a switch in the tap-water supply system. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 15316185-1 2004 Two probabilistic models were developed to estimate the acute and chronic exposure to fluoride of exclusively formula-fed infants aged 0-4 months as a result of the consumption of infant formula reconstituted with fluoridated tap water in Ireland. Water 230-235 nuclear RNA export factor 1 Homo sapiens 226-229 15325157-2 2004 We investigated the mortality of a cohort of 5144 residents in Guastalla, northern Italy, who were supplied tap water with high chloroform and trihalomethane content between 1965 and 1987. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 15243686-11 2004 P. aeruginosa was isolated from the room"s tap water in 62.4% of samples. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 15243686-12 2004 More than 90% of tap water samples had pulsotypes 1 and 2, which were frequently isolated in the stomach (59%) but were only rarely associated with VAP. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 15330391-4 2004 Participants with lead in the tap water above the detection limit of 5 microg/l (N = 142) showed significantly higher blood lead levels (median 31 microg/l) compared to those with no detectable lead in the tap water (N = 106; median blood lead 24 microg/l, p < = 0.001). Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 15388805-5 2004 A significant increase in DNA migration was observed in both cell types after 1 h treatment with filtered and tap water, and, to a lesser extent, chlorine dioxide pre-disinfected water. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 15388805-7 2004 Overloading of the carbon filter, with a consequent peak release, might explain the high genotoxicity found in water samples C and D. Cell toxicity and DNA damage increases were also detected in metabolically competent HepG2 cells treated with a lower concentration of tap water extract for a longer exposure time (24 h). Water 273-278 nuclear RNA export factor 1 Homo sapiens 269-272 15493459-8 2004 Our results demonstrate that ascorbic acid is rapidly oxidized to dehydroascorbic acid and further decomposed to oxalic- and threonic acid in copper contaminated household tap water that is buffered with bicarbonate. Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 15230888-1 2004 BACKGROUND: Direct electrical current (d.c.) administration based on tap water iontophoresis has been used as a therapeutic option for palmoplantar hyperhidrosis. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 15248985-9 2004 The method was used to measure bromide in river water and tap water. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 15330391-5 2004 There is a close correlation between the average lead concentration in the tap water and blood lead concentrations (N = 142 value pairs, Spearman"s rho 0.43, p < = 0.0001). Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 15090668-8 2004 The total fluid intake was 18.9 l/week of which, on average, 18% was cold tap water; 30% of this tap water was consumed outside the home. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 15344726-1 2004 First aid from the water tap? Better not! Water 19-24 nuclear RNA export factor 1 Homo sapiens 25-29 15131626-15 2004 Changes in the sources of water meant that less water consumed was likely to come from the tap in the house and more from drinks made elsewhere, than 20 years previously. Water 26-31 nuclear RNA export factor 1 Homo sapiens 91-94 15131626-15 2004 Changes in the sources of water meant that less water consumed was likely to come from the tap in the house and more from drinks made elsewhere, than 20 years previously. Water 48-53 nuclear RNA export factor 1 Homo sapiens 91-94 15097021-6 2004 Cumulative exposure to trihalomethanes was estimated by combining individual year-by-year average trihalomethane level and daily tap water consumption. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 15090668-8 2004 The total fluid intake was 18.9 l/week of which, on average, 18% was cold tap water; 30% of this tap water was consumed outside the home. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 15117067-10 2004 The tap water samples analyzed contain variable concentrations of the four trihalomethanes, ranging from 1.0 to 66.5 microg l(-1), depending of the compound. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 15066944-7 2004 However, when ingested with 16 oz of room temperature tap water, phenylpropanolamine increased SBP by 82+/-2 mm Hg. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 15057194-3 2004 The Environmental Protection Agency (EPA) requires water authorities to test tap water in 10-100 residences annually for lead. Water 51-56 nuclear RNA export factor 1 Homo sapiens 77-80 14986461-10 2004 The mean iodine concentration for tap drinking water was 22.8 micrograms/L (range 0.5-53.5 micrograms/L) and for mineral water 7 micrograms/L (range 0-15 micrograms/L). Water 47-52 nuclear RNA export factor 1 Homo sapiens 34-37 15145587-16 2004 It is also clear that consumers" regularly consume more than 500 HPC/ml from drinking water taken from the household tap. Water 86-91 nuclear RNA export factor 1 Homo sapiens 117-120 15061416-9 2004 Contaminated tap water had been used to dilute alcohol for skin antisepsis and for decontamination of the caps of heparin vials. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 15061416-11 2004 CONCLUSION: This is potentially the largest single-source nosocomial bloodstream infection outbreak ever reported, and the first report of an alcohol skin antiseptic contaminated by tap water as a source for nosocomial bacteremia. Water 186-191 nuclear RNA export factor 1 Homo sapiens 182-185 15060497-11 2004 Tap water exhibited the highest incidence of leakage, sterile water the least, with the other irrigation solutions leading to intermediate leakage. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 15074609-8 2004 The majority of the tap water samples, collected from areas along the seashore contained increased concentrations of chloride ions, which is a clear indication of seawater intrusion into the related aquifers. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 15016444-3 2004 The goal of the present study is to investigate the influence of water quality and the geographic location of consumers within a distribution system on consumer perception of tap water. Water 65-70 nuclear RNA export factor 1 Homo sapiens 175-178 18969359-9 2004 Real samples collected from tap water and well water were successfully analyzed using the proposed method. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 14663545-9 2004 The analytical procedure was successfully applied to several samples of tap water and the results were in good agreement with those from AAS determination. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 16892578-6 2004 Consumption of tap water averaged 0.73 L (max. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 15651116-6 2004 Patients with a higher O antibody titre (> or = 1 in 80) by Widal test were found to have consumed both tap water and pure water. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 15007904-0 2004 [Volatile organic compounds of the tap water in the Watarase, Tone and Edo River system]. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 14643286-2 2004 The most dominant THMs are chloroform and bromodichloromethane (BDCM) in Hong Kong tap water. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 14691169-0 2004 Acanthamoeba keratitis: the role of domestic tap water contamination in the United Kingdom. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 14691169-7 2004 In six cases, identical Acanthamoeba mtDNA profiles were found for the clinical and home tap water isolates. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 15546402-9 2004 Mycobacteria were also detected in tap water and their number was increased 10(3)-10(4)-fold higher after storage. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 15030145-8 2004 Tap water samples, when analyzed by this assay, could not be guaranteed for biological stability due to their high BDOC concentrations (0.17 to 0.23 mg/L) that corresponded to 26-36% of the initial DOC level. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 27820018-26 2004 CONCLUSIONS: Current RCT evidence suggests the use of a surgical sterile catheterisation technique is not required, and that tap water is sufficient for cleaning genitalia. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 14750886-8 2004 Analysis of tap water, spiked with chloroform or carbon tetrachloride, gave recoveries within 1.0-2.6% of the recoveries by the standard GC method. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 15007904-10 2004 RESULTS: Concentrations of THMs in the downstream tap water samples were higher than those in the samples from the upperstream. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 15007904-12 2004 In tap water of local government C, trichloroethylene was detected. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 14691275-1 2004 AIMS: To assess spatial fluctuations, temporal variability, and errors due to sampling and analysis in levels of disinfection by-products in routine monitoring tap water samples and in water samples collected in households within the same distribution system for an exposure assessment study. Water 164-169 nuclear RNA export factor 1 Homo sapiens 160-163 14978297-4 2004 As is known, some kinds of mineral waters contain naturally occurring radionuclides in higher concentration than the usual drinking (tap) water. Water 35-40 nuclear RNA export factor 1 Homo sapiens 133-136 14690388-6 2003 In experiments using high-performance liquid chromatography-UV spectroscopy (HPLC-UV) and HPLC tandem mass spectrometry (HPLC-MS/MS), DKN was found to rapidly react with hypochlorite in tap water, yielding the BA metabolite as the major end product. Water 190-195 nuclear RNA export factor 1 Homo sapiens 186-189 15237641-1 2004 Chlorinous flavors at the tap are the leading cause of customers" complaints and dissatisfaction with drinking water. Water 111-116 nuclear RNA export factor 1 Homo sapiens 26-29 15537002-2 2004 In the subsequent treatment steps of washing with tap water, ammonium removed from urine was eluted from the surface of the clinoptilolite to be recovered for further reuse. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 15537002-6 2004 The recovery was calculated as 9.73 mg ammonium per gram of clinoptilolite, corresponding to an efficiency of 63% only through washing with tap water. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 14690388-7 2003 One milligram per liter (19 microM) of hypochlorite residue in tap water was able to completely oxidize up to 1600 microg/L (4.45 micromol/L) of DKN. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 14690388-8 2003 In tap water, the disappearance of IXF was much more rapid than in DI water. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 14690388-10 2003 As a result, the herbicide solutions prepared with tap water at 500 microg/L will no longer possess any herbicidal activity after 48 h of storage. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 14690388-11 2003 However, in agronomic settings, highly concentrated tank solutions (600-800 mg/L) may be prepared with tap water since the conversion of IXF to BA would represent <5% of the herbicide; therefore, any impact on the herbicide efficacy would be negligible. Water 107-112 nuclear RNA export factor 1 Homo sapiens 103-106 14567450-6 2003 Our results demonstrate that ascorbic acid can induce a pH dependent hydroxyl radical generating reaction in copper contaminated household tap water that is buffered with bicarbonate. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 14644662-6 2003 Periodic urine samples were collected from early to late pregnancy among 29 pregnant women living in Antofagasta, Chile, who drank tap water containing 40 micro g/L In-As. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 14750691-6 2003 Tap water in the capital Amman, where approximately 35% of the population live, has a very low radon concentration, 3.9 Bq l(-1). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 14616463-3 2003 The first group of 10 subjects drank 500 mL of cranberry juice diluted with 1500 mL tap water for 2 weeks, while the second group drank 2000 mL of tap water for the same period. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 14620452-6 2003 About 87% of formula fed children had tap water added to the bottle. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 14684951-4 2003 They wore cotton underwear, which they had washed in cold tap water. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 12867198-0 2003 The mutagenic potentials of tap water samples in Shanghai. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 12867198-5 2003 Two tap water samples from city north, which were directly from Yangtze River, were also not mutagenic. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 12867198-7 2003 The boiled water displayed an even stronger mutagenic potential compared to its original tap water. Water 11-16 nuclear RNA export factor 1 Homo sapiens 89-92 12867198-7 2003 The boiled water displayed an even stronger mutagenic potential compared to its original tap water. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 12867198-10 2003 Qualitatively similar spectra were observed except for the peaks of three chlorinated aromatic hydrocarbon compounds, which existed only in the tap water. Water 148-153 nuclear RNA export factor 1 Homo sapiens 144-147 16450544-3 2003 Slides washed in untreated tap water showed the best results concerning differentiation and colour intensity, while slides washed with softened or other treated water showed poorer degrees of differentiation and colour intensity. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 15058835-2 2003 The aim of this report is to compare a bottled spring water with a very low mineral content with tap water in the reconstitution and/or dilution of 6 different infant starting formulas and cow"s milk. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 14610562-6 2003 The mean fluoride intake for 4-18-year-olds when the source of water intake is solely fluoridated tap water was estimated to be 0.26 mg F per day; compared with 0.16 mg F per day, when a combination of tap and bottled water is consumed. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 14610562-6 2003 The mean fluoride intake for 4-18-year-olds when the source of water intake is solely fluoridated tap water was estimated to be 0.26 mg F per day; compared with 0.16 mg F per day, when a combination of tap and bottled water is consumed. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 14610562-8 2003 Consumption of bottled water containing a negligible amount of fluoride in preference to fluoridated tap water might result in less than optimal fluoride ingestion in young people. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 15049550-3 2003 Table water is bottled purified water subject to the same requisites as tap water, whatever its original characteristics, during the process of purification, it can be modified to render it ideal for the needs of the consumer. Water 6-11 nuclear RNA export factor 1 Homo sapiens 72-75 15049556-4 2003 (Local Health Unit) in collaboration with the Institute of Hygiene of the Catholic University of Rome carried out a survey to evaluate perception towards tap water quality in a sample of students. Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 14569179-0 2003 Trihalomethane levels in home tap water and semen quality. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 14556666-7 2003 The odds ratios (95% confidence intervals) were 0.73 (0.55-0.96) for tap water, 0.72 (0.63-0.84) for flush toilets, 0.74 (0.66-0.83) for urban location, 1.34 (1.09-1.64) for 7 or more people in the household, 1.19 (1.00-1.41) for 4th or 5th in birth order, and 1.47 (1.17-1.85) for 6th or more in birth order. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 14626901-2 2003 Concentrations of DBPs (mean +/- standard deviation) in tap water were the following: total trihalomethanes (THMs) 205 +/- 70 micrograms/l, five haloacetic acids (HAAs) 150 +/- 30 micrograms/l, and 3-chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone (mutagen X or MX) 160 +/- 50 ng/l. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 14626901-4 2003 The mutagenic activity of tap water extracts in the Salmonella TA-100 assay was 14,900 net revertants/l. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 14626901-8 2003 Due to concerns over microbiological safety of water, average daily consumption of non-boiled tap water in pregnant women was only 0.01 l/day, while consumption of boiled tap water was 0.81 l/day. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 14626901-8 2003 Due to concerns over microbiological safety of water, average daily consumption of non-boiled tap water in pregnant women was only 0.01 l/day, while consumption of boiled tap water was 0.81 l/day. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 14621355-2 2003 Common household bleach containing 5.25% sodium hypochlorite, diluted in a 1:10 ratio with tap water, is a safe and effective method to reduce colony-forming units per milliliter (CFU/ml) to a study-defined acceptable range of 100 CFU/ml when a standard procedure was consistently used. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 12689853-5 2003 In the latter group, tap water (2,000 ml) was administered intragastrically to the ewe followed by DDAVP (20 microg bolus, 4 microg/h) and a maintenance intravenous infusion of 5% dextrose water for 4 h to achieve maternal hyponatremia of 10-12 meq/l. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 12936882-3 2003 The city water where I live is loaded with phosphates and other minerals, so I"m worried that my tap water doesn"t meet the definition of "plain water". Water 9-14 nuclear RNA export factor 1 Homo sapiens 97-100 12936882-3 2003 The city water where I live is loaded with phosphates and other minerals, so I"m worried that my tap water doesn"t meet the definition of "plain water". Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 12938971-5 2003 The contribution of drinking water to the total uranium intake is sometimes significant as the uranium concentration range in 29 analyzed tap and bottled "mineral" waters is 0.04-5.86 microg L(-1) and the drinking water consumption about 1 L d(-1) or more. Water 29-34 nuclear RNA export factor 1 Homo sapiens 138-141 12846731-4 2003 The recordings were continuously made for 3 h after the ingestion of 100 mL of tap water with (16 subjects) or without (eight subjects) 10 g of lactulose. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 12851114-5 2003 This article presents the results of nine studies, including seven dose reconstruction or simulation studies involving human volunteers, that quantitatively characterize the absorbed dose of Cr(VI) following contact with tap water via all routes of exposure. Water 225-230 nuclear RNA export factor 1 Homo sapiens 221-224 12851114-9 2003 Based on a physiologically based pharmacokinetic model for chromium derived from published studies, coupled with the dose reconstruction studies presented in this article, the available information clearly indicates that (1) Cr(VI) ingested in tap water at concentrations below 2 mg/L is rapidly reduced to Cr(III), and (2) even trace amounts of Cr(VI) are not systemically circulated. Water 248-253 nuclear RNA export factor 1 Homo sapiens 244-247 12851114-10 2003 This assessment indicates that exposure to Cr(VI) in tap water via all plausible routes of exposure, at concentrations well in excess of the current U.S. Environmental Protection Agency (EPA) maximum contaminant level of 100 microg/L (ppb), and perhaps those as high as several parts per million, should not pose an acute or chronic health hazard to humans. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 14677264-4 2003 Tap water should be preferred to mineral water usually in stores. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12873071-11 2003 Two spoons of the commercial bleach was added to 200 mL of tap water. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 12814092-0 2003 Flushing wounds in children--is tap water OK? Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 12834222-5 2003 Method detection limits were at sub-ppb level for pure water and sub-ppm level for tap water. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 12782495-10 2003 Incorporating tap water consumption showed a similar pattern of reduced cycle length with increasing TTHM exposure. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 12872527-0 2003 A tap water turbidity crisis in Tel Aviv, Israel, due to technical failure: toxicological and risk management issues. Water 6-11 nuclear RNA export factor 1 Homo sapiens 2-5 12854693-0 2003 Copper concentrations in tap water and possible effects on infant"s health--results of a study in Lower Saxony, Germany. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 12858392-7 2003 This method was applied to determine haloacetic acids in tap water by combination with liquid-liquid extraction and back-extraction into NaOH solution. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 12777181-11 2003 The factors most strongly associated with symptoms were drinking tap water (OR = 7.8, 95% CI 1.3-48), exposure to vapors from the basement (OR = 10.4, 2.3-47) and eating foods prepared with tap water (OR = 8.6, 1.9-40). Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 12777181-11 2003 The factors most strongly associated with symptoms were drinking tap water (OR = 7.8, 95% CI 1.3-48), exposure to vapors from the basement (OR = 10.4, 2.3-47) and eating foods prepared with tap water (OR = 8.6, 1.9-40). Water 194-199 nuclear RNA export factor 1 Homo sapiens 190-193 12727595-2 2003 Data from the literature were used to assign statistical distributions to swimming pool chloroform concentrations, frequency and duration of swimming, showering and bathing, and average tap water consumption. Water 190-195 nuclear RNA export factor 1 Homo sapiens 186-189 12712026-2 2003 The purpose of this study was to compare the infection rates of wounds irrigated with normal saline solution versus those of wounds irrigated with running tap water. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 12712026-11 2003 Tap water and normal saline solution pressures and flow rates differed. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12712026-13 2003 However, more wounds were located on the hand in the tap water group (21.3%; 95% confidence interval [CI] 16.3% to 27.1%) compared with those in the normal saline solution group (9.2%; 95% CI 5.9% to 13.4%). Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 12712026-16 2003 Tap water might be an effective alternative to normal saline solution for wound irrigation in children. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12775063-19 2003 The calibration curve displayed a similar pattern as did those for other matrixes, including PBS and tap water, although its sensitivity was a little less due to the interference with certain components in the surface water. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 12636128-0 2003 Tap water filters. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12745350-4 2003 An interquartile range increase in effluent water turbidity of 0.8 Nephelometric Turbidity Units was associated with a relative risk of self-reported GI illness of 1.47 (95% Confidence Interval 1.16, 1.86) at a lag of 2 days after control for daily rate of consumption of non-boiled tap water, behavioural covariates, day of the week and a seasonally-related linear trend. Water 44-49 nuclear RNA export factor 1 Homo sapiens 283-286 12636128-1 2003 Moen PureTouch filters remove impurities from tap water without removing fluoride. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 12397274-7 2002 In the test group, water from the hot water tap at approximately body temperature was instilled into the colon by means of the accessory channel of the colonoscope with a 30 mL syringe. Water 19-24 nuclear RNA export factor 1 Homo sapiens 44-47 12705354-3 2003 Tap water and mineral water were found to contain various amounts of NOx that were drastically reduced by treatment with a reverse osmosis column and remained in trace amounts after ion exchange column treatment. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12514004-5 2003 When modifications were made in the elution and concentration steps to streamline the Filta-Max procedure, the mean percentages of recovery from filtered tap water were 40.2% +/- 16.3% for oocysts and 49.4% +/- 12.3% for cysts by the modified procedures, while matrix spike oocyst recovery percentages ranged from 2.1 to 36.5% and cyst recovery percentages ranged from 22.7 to 68.3%. Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 12680094-2 2003 The present paper gives the results of assessment of the mutagenic activity of tap water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 12708296-5 2003 The tap water filtration resistance of the dynamic bio-membrane sheet with gel-layer attaching on was about 1.9 x 10(9) m-1, which almost equaled to that of the untapped sheet. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 12708296-7 2003 The untapped dynamic bio-membrane sheet showed an initial resistance to tap water permeation, but the one with gel-layer attaching on had little initial resistance. Water 76-81 nuclear RNA export factor 1 Homo sapiens 6-9 12725389-5 2003 The solid-phase recovery rates of ten pesticides spiked into tap water and raw water were in the range of 69-111%. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 12515584-0 2003 Endemic cryptosporidiosis and exposure to municipal tap water in persons with acquired immunodeficiency syndrome (AIDS): a case-control study. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 12515584-7 2003 In the multivariable analysis with adjustments for confounders, tap water consumption inside and outside the home at the highest exposure categories was associated with the occurrence of cryptosporidiosis (inside the home: odds ratio (OR), 6.76; 95% CI 1.37-33.5, and outside the home: OR 3.16; 95% CI 1.23-8.13). Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 12515584-8 2003 The PAF was 85%; that is, the proportion of cases of cryptosporidiosis in San Francisco AIDS patients attributable to tap water consumption could have been as high as 85%. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 12602823-4 2003 The rate of degradation was more in tap water as compared to rain and distilled water. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 12635833-4 2003 Arsenic safe drinking water is provided for adopted villages by constructing shallow, concrete dugwells designed to tap the water of the unconfined aquifer, 20-30 feet below ground level, that contains low levels (< 0.05 mg/L) of arsenic in the target region. Water 22-27 nuclear RNA export factor 1 Homo sapiens 116-119 12607622-6 2002 Water specimens were collected from the triple syringe, high speed outlet, cup filler and surgery tap. Water 0-5 nuclear RNA export factor 1 Homo sapiens 98-101 12545634-9 2002 Enemas are done twice a week, they last on average one hour with an average of 3 litres of liquid, usually tap water. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 12362104-10 2002 Also, the median number of phases III per hour with CHO was higher than with tap water (0.4 v. 0.0; P < 0.05). Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 12413214-3 2002 Acrylic columns packed with chitosan and zeolite-sewage sludge mixtures in optimum ratio 1.0:10 and 3.0:10, respectively, were leached with tap water and sewage effluent at different pH levels. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 12361943-7 2002 Children 1 year old showed the highest rate of diarrhea during the dry season [odds ratio (OR) = 2.1 with 95% confidence interval (CI), 0.99-4.71], particularly those from households perceiving unpleasant taste of tap water (OR, 1.7; 95% CI, 0.97-2.92) and consuming vegetables washed only with water (OR, 2.2; 95% CI, 1.10-4.39). Water 218-223 nuclear RNA export factor 1 Homo sapiens 214-217 12362104-9 2002 During exercise, the number of subjects with a phase III was higher with CHO than with tap water (n =6 v. n =1; P < 0.05). Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 12399690-1 2002 The tap water of Kuopio, Finland, was fluoridated from 1959 to 1992. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 12352219-4 2002 One group (10 subjects) drank carbonated water and the other (11 subjects) tap water for almost 15 days. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 18968726-1 2002 A simple and sensitive method for the speciation, separation and preconcentration of Cr(VI) and Cr(III) in tap water was developed. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 18968726-12 2002 The proposed method was applied to tap water samples and chromium species have been determined with the relative error <3%. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 12117645-2 2002 We evaluated urinary excretion of trichloroacetic acid (TCAA) as an exposure biomarker using 10 volunteers who normally consume their domestic tap water. Water 147-152 nuclear RNA export factor 1 Homo sapiens 143-146 12369053-9 2002 In the past, the European Pharmacopoeia and the Italian Health Ministry released some reference values for tap water, values which were extended to water used for dialysis. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 12148328-5 2002 Typically, water passes through three to six such valves before reaching the tap. Water 11-16 nuclear RNA export factor 1 Homo sapiens 77-80 12100915-14 2002 Tap water, however, can change urinary electrolytes in patients who form calcium stones. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12023920-4 2002 Descriptive epidemiology suggested that drinking unboiled tap water in a single water zone was the common factor linking cases. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 12023920-4 2002 Descriptive epidemiology suggested that drinking unboiled tap water in a single water zone was the common factor linking cases. Water 80-85 nuclear RNA export factor 1 Homo sapiens 58-61 12120840-0 2002 Safe hot tap water and the risk of scalds and legionella infection. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 12126069-7 2002 The second group [control; tap-water-treated] consisted of 15 patients, 8 males (53.3%) and 7 females (46.6%). Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 12138517-2 2002 The aim of this study is to investigate the efficacy of two different chemical disinfectant agents and tap water where the laryngoscope blades were contaminated by different microorganisms and try to create a simple, effective and easy decontamination method. Water 107-112 nuclear RNA export factor 1 Homo sapiens 103-106 12146880-4 2002 In Eskisehir (Turkey) drinking and tap water are supplied from a water treatment plant, consisting mainly of screening, sedimentation, filtration and sterilization units and having a capacity of 80.000 m3/d. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 12521169-6 2002 Recoveries of the five sulfonylureas extracted from 1 L of tap water and surface water samples such as river water and rainwater at a 50 ng/L spike level were not lower than 96%. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 12394948-5 2002 INTERVENTIONS: P. aeruginosa also was found in 150 of 259 (58%) tap water samples taken from patient rooms. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 12394948-13 2002 CONCLUSIONS: Tap water from faucets contaminated with P. aeruginosa plays an important role in the propagation of this pathogen among patients. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 12216046-1 2002 This study was designed to compare the infection rates of simple lacerations irrigated with tap water versus sterile normal saline before repair. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 12196423-4 2002 RESULTS: Tap water pH 6.2-6.9 was associated with a fourfold higher risk of type 1 diabetes compared with pH > or =7.7 (OR 3.73, 95% CI 1.52-9.15). Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 12196423-6 2002 Higher tap water concentration of zinc was associated with lower risk of type 1 diabetes after adjustment for pH and other possible confounders, but the overall association was strictly not significant. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 12192223-5 2002 RESULTS: According to postQ, total water intake was 2.6 liters per day, whereas tap water intake was 0.6 liters per day. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 12192223-6 2002 Intraclass correlation coefficients of postQ compared with preQ were 0.85 for tap water daily intake and 0.77 for duration of showering and bathing. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 12192223-7 2002 Pearson"s correlation coefficients were 0.84 for tap water daily intake, 0.81 for frequency of showering, and 0.94 for bathing. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 12322735-11 2002 Tap water samples at Frankfurt/M (mean of 35 ng/L, maximum of 71 ng/L) were in the same range as MTBE amounts in drinking water at the Lower Rhine site. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12216759-6 2002 RESULTS: The tap water produced misregistration of the needle images. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 12463138-4 2002 After studying their composition and adapting the dietary advice (particularly concerning dairy foods) to this ionic composition, various types of water can be advised to patients, including tap water, most types of spring water, but not all mineral waters. Water 147-152 nuclear RNA export factor 1 Homo sapiens 191-194 12239573-0 2002 Reducing bacterial counts in dental unit waterlines: tap water versus distilled water. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 12239573-5 2002 RESULTS: The microbial plate counts of seven tap water specimens (controls) ranged from 4 to 95 CFU/mL. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 12039784-0 2002 Identification of nontuberculous mycobacteria existing in tap water by PCR-restriction fragment length polymorphism. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 12039784-2 2002 Using acid-fast staining, culture, and PCR, acid-fast bacilli were detected in 83.7% of 49 hospital tap water samples and nontuberculous mycobacteria (NTM) were detected in 20.4% of the same 49 samples. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 12039784-4 2002 Our findings indicate that NTM in hospital tap water are the possible cause of false positives in acid-fast staining and of nosocomial infection in immunocompromised patients. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 12000273-1 2002 [reaction: see text] Nanometer tin-mediated allylation of aldehydes or ketones in distilled or tap water gave rise to corresponding homoallyl alcohol in high yield without any other assistance such as heat or supersonic or acidic media. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 11978559-8 2002 The method of choice in treating palmoplantar hyperhidrosis is tap water iontophoresis. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 11978559-13 2002 It can be stated that in spite of the interesting and promising new alternatives, especially using botulinum toxin, the tried-and-true procedures such as tap water iontophoresis and aluminium chloride salts still have a firm place in the treatment of hyperhidrosis. Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 12073573-7 2002 The rate of bacteria elimination for hand-washing with soap and tap water after taking care of a patient was insufficient, especially when before care was provided the number of bacteria on the nurse"s hands were less than 100 CFU/agar plate. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 12057180-0 2002 [Halogenated by-products of chlorination in tap water]. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 11974735-0 2002 Can tap water be used to irrigate wounds in A&E? Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 11974735-1 2002 After critiquing the seven selected articles, it seems likely that tap water can be used as an irrigant and cleansing agent for soft-tissue wounds. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 11974735-2 2002 However, the current research on tap water has involved human and rat wound studies and tap water culture studies (Dire, 1990; Riyat and Quinton, 1997; Moscati, 1998). Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 11974735-2 2002 However, the current research on tap water has involved human and rat wound studies and tap water culture studies (Dire, 1990; Riyat and Quinton, 1997; Moscati, 1998). Water 92-97 nuclear RNA export factor 1 Homo sapiens 33-36 11974735-5 2002 Two key conclusions could be drawn from the available research: The tap water tested was generally agreed to be safe from harmful bacteria and had no contaminating bacteria; Human and rat models showed a clear benefit in using tap water to cleanse soft tissue wounds, thus concluding tap water is safe for use on wounds (Towler, 2000). Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 11974735-5 2002 Two key conclusions could be drawn from the available research: The tap water tested was generally agreed to be safe from harmful bacteria and had no contaminating bacteria; Human and rat models showed a clear benefit in using tap water to cleanse soft tissue wounds, thus concluding tap water is safe for use on wounds (Towler, 2000). Water 231-236 nuclear RNA export factor 1 Homo sapiens 68-71 11974735-5 2002 Two key conclusions could be drawn from the available research: The tap water tested was generally agreed to be safe from harmful bacteria and had no contaminating bacteria; Human and rat models showed a clear benefit in using tap water to cleanse soft tissue wounds, thus concluding tap water is safe for use on wounds (Towler, 2000). Water 231-236 nuclear RNA export factor 1 Homo sapiens 68-71 11904109-5 2002 Patients drank 480 mL of tap water at room temperature in less than 5 minutes. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 11974735-6 2002 The financial benefits were also stated in the studies; tap water can have huge cost-saving potential for A&E departments. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 12541976-6 2002 Tap water was analyzed under the same conditions. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12012198-1 2002 A rapid and simple method for separation and determination of tributyltin (TBT) in mineral and tap water is described. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 11979327-5 2002 A penile water-cuff is connected through a pressure tube to a three-way tap. Water 9-14 nuclear RNA export factor 1 Homo sapiens 72-75 11953281-4 2002 METHODS: Altogether 66 volunteers were drinking 300 ml oxygenated or tap water within 15 minutes. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 11953281-8 2002 In the meantime they were drinking per day three times 300 ml either oxygenated water or tap water. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 11886195-3 2002 A strain of S. paucimobilis identical to one of the patient"s was isolated from tap water collected in the haematological unit. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 12000273-0 2002 Application of tin and nanometer tin in allylation of carbonyl compounds in tap water. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 11830654-4 2002 In earlier experiments, Ringer had suspended them in a saline medium for which he admitted to having used London tap water, which is hard: The hearts contracted beautifully. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 11830654-5 2002 When he proceeded to replace the tap water with distilled water, he made a startling finding: The beating of the hearts became progressively weaker, and stopped altogether after about 20 min. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 11793075-2 2002 The saline solution is usually made at home by adding measured quantities of common salt to tap water. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 11885352-6 2002 The electrolyte release of chlorine from the dental unit tap water by anodic oxidation without addition of any chemical disinfectant also resulted in continuously low colony numbers of the water. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 11858947-0 2002 Effect of tap-water iontophoresis on sweat gland recruitment, skin temperature and skin blood flow. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 11858947-2 2002 Seven days of tap-water iontophoresis decreased the number of active sweat glands by 72% which significantly increased forearm skin temperature and blood flow during mild exercise (70 W) in the heat (32 degrees C). Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 12519612-15 2002 For chronic wounds, the odds of developing an infection when cleansed with tap water compared with normal saline was 0.16, 95 % Confidence Interval (CI) 0.01, 2.96. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 12519612-20 2002 However the quality of the tap water should be considered prior to its use and in the absence of potable tap water, boiled and cooled water as well as distilled water can be used as wound cleansing agents. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 11899878-3 2002 Phenol and hydrochloric acid added to tap water caused statistically significant changes in anti-immunoglobulin activity of Klebsiella strains. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 12541622-8 2002 The method was used for the determination of trace chrysene in tap water, mineral water, rain water and river water. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 11771929-6 2001 Mean CdB was higher among children within 4 km of a zinc smelter and consuming > or =500 ml of tap water daily (x1.34; 95% CI=[1.14-1.51]) compared with children living more than 4 km away and consuming <500 ml of tap water daily. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 11766801-2 2002 A total of 23 tap water samples were examined for infectious enteroviruses and adenoviruses by a cell culture technique followed by polymerase chain reaction (PCR) amplification. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 11766801-8 2002 Several types of adenovirus were detected in tap water samples and some water samples were found to contain adenoviruses which were closely related to enteric adenovirus types 40 and 41. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 11579665-3 2001 It also provides a primer on water treatment and alternatives to tap water. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 11547116-10 2001 Due to the elevated sodium content in softened tap water families should be alerted to use untreated tap water for preparing enemas. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 11547116-10 2001 Due to the elevated sodium content in softened tap water families should be alerted to use untreated tap water for preparing enemas. Water 51-56 nuclear RNA export factor 1 Homo sapiens 101-104 11845090-9 2001 Tap water usage for food follows a normal distribution (arithmetic mean in winter=1.55 l/j, 95% CI [0.20-2.90]; arithmetic mean in spring=1.78 l/j, [0.13-3.43]). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 11686389-4 2001 A simple technique was used to detect, observe, and evaluate the concentration of free-living amoebae in dental unit and tap water samples. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 11845090-11 2001 Tap water intake amounts to more than 80% of total drinking water consumption, and pure tap water (i.e not added, modified nor boiled) amounts to 42% of total drinking water. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 11603856-7 2001 All strains were able to grow in tap water samples, which were filtered and autoclaved, and a final concentration of 10(5)-10(6) cfu ml(-1) was observed. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 11603856-2 2001 After bottling, the autochthonous microflora reached 6 x 10(5) cfu ml(-1) after a 5-day incubation period in tap water unfiltered and which was non-autoclaved. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 11681570-3 2001 The recoveries for the analytes in tap water varies between 70 and 100%. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 11603856-8 2001 Any inherent capability of Aeromonas to grow in tap water was eliminated by the presence of autochthonous microflora and "ultramicrocells" bacteria. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 11708062-8 2001 The recoveries were 99 and 108% for tap water (4 ml loading) and underground water (12 ml loading), respectively. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 11584209-3 2001 METHODS: Fifteen colostomy irrigators(with more than 3 years" experience) performed washout with tap water compared with water containing 0.025 mg/kg glyceryl trinitrate. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 11708070-0 2001 Simple miniaturized amperometric flow cell for monitoring residual chlorine in tap water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 11476237-9 2001 The method is demonstrated with deionized and tap water samples spiked with carbamate insecticides. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 11551599-2 2001 Contaminated tap water, used for rinsing surgical devices after disinfection, was identified as the source of the outbreak. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 11519974-9 2001 CONCLUSION: The comparison of these data with other surveys points to a low total water intake, especially a low tap water intake, in German children and adolescents and underlines cultural influences on food and drinking habits. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 11382287-11 2001 For example, tap water samples were analyzed directly while a short degassing of mineral water (to prevent bubble formation during the separation) and filtration of river water samples (to remove particulates and colloids) were the only operations needed in this respect. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 11394791-2 2001 Tap water, which had been filtered through biologically active granular activated carbon, was used as an innoculum for biofilm growth in annular reactors (ARs). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 11445506-4 2001 In addition, dipstick measurements were made of nitrates and nitrites in tap water for the subset of women living in the same home they had lived in during their pregnancies. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 11424725-1 2001 Energy consumption in sewage treatment facilities in Japan has increased due to increasing tap water consumption. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 11990623-5 2001 This method has been used to determine trace thiocyanate in urine and tap water samples. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 11820547-0 2001 Evidence-based practice: tap water cleansing of leg ulcers in the community. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 11820547-3 2001 One question remains unanswered: What is the evidence for the use of sterile saline or clean tap water for cleansing of leg ulcers in the community? Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 11820547-5 2001 Application of these principles enabled clinicians to collaborate in the search for evidence to support or refute tap water cleansing of leg ulcers. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 11477520-2 2001 Individual differences in consumption of bottled or filtered water, variability in tap water consumption at home and at work, dermal and inhalation exposure to volatile contaminants, and changes in residency during pregnancy may lead to exposure misclassification. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 11477520-6 2001 Pregnant women consumed more water than non-pregnant women (3.4 vs. 3.0 total l/day), especially cold tap water at home (1.8 vs. 1.3 l/day, 95% CI for the difference=0.1, 0.9). Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 11349981-6 2001 Although these findings suggest the serological response may be associated with type of tap water and certain foods, additional research is needed to clarifythe role of both food and drinking water in endemic Cryptosporidium infection. Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 11307974-8 2001 The procedure is applicable to the quantification of bisphenol A in tap water, raw water and stream water. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 11990628-0 2001 On-line preconcentration system using a packed-bed filter for the determination of lead in tap water by inductively coupled plasma atomic emission spectrometry with ultrasonic nebulization. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 11318912-7 2001 For half of the tap water sources we examined, adults may fulfill between 8% and 16% of their Ca2+ DRI and between 6% and 31% of their Mg2+ DRI by drinking 2 liters per day. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 11207149-6 2001 Adjustment for identified risk factors for anencephaly did not substantially alter these associations, nor did control for maternal dietary nitrate, total vitamin C intake, and quantity of tap water consumed. Water 193-198 nuclear RNA export factor 1 Homo sapiens 189-192 11327069-10 2001 RESULTS: The HPC counts, in colony forming units (CFU)/ml, were reduced 3- to 5-fold by flushing tap water through the units, but they returned after units were idle overnight. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 11228965-2 2001 Long-term tests (6-8 months) in a synthetic, microbially stable soft tap water confirmed that lower pHs and higher temperatures increased copper release to water. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 11161657-6 2001 All lifetime cancer risks for CHCl(3), CHBrCl(2), CHBr2Cl, and CHBr3 from consuming tap water in the three water supply areas were higher than 10(-6). Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 11217022-6 2001 The method was successfully applied to a local tap water sample and an aqueous soil extract. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 18968171-7 2001 The method was applied to the determination of periodate and iodate in tap water and spring water with satisfactory results. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 11198025-3 2001 Over a period of 7 months, 5 (29%) of 17 patients were infected with P aeruginosa genotypes also detectable in tap water. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 11206919-1 2001 Biofilm are formed wherever there is some water in our environment: pipes, pipelines, tap water systems, air conditioning systems... Water 42-47 nuclear RNA export factor 1 Homo sapiens 86-89 11124219-9 2001 The taste threshold in tap water was 2.6 mg/l Cu for both copper sulfate and copper chloride. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 10974639-4 2000 The health center does have electricity and tap water. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 11548067-3 2001 In the current study, we specifically evaluated the long-term reproducibility of tap water and toenail concentrations of arsenic, and the relation between water, toenail, and urinary measurement. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 11548067-6 2001 Tap water arsenic concentrations ranged from undetectable (<0.01 microg/L) to 66.6 microg/L. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 17216984-5 2001 The reassessment proved that, there was an increase in number of families use tap water inside the house by 29% compared with 1995 assessment. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 11215012-7 2000 The most commonly consumed water intake categories were plain and boiled tap water. Water 27-32 nuclear RNA export factor 1 Homo sapiens 73-76 11318912-1 2001 OBJECTIVES: Because of growing concern that constituents of drinking water may have adverse health effects, consumption of tap water in North America has decreased and consumption of bottled water has increased. Water 69-74 nuclear RNA export factor 1 Homo sapiens 123-126 11318912-1 2001 OBJECTIVES: Because of growing concern that constituents of drinking water may have adverse health effects, consumption of tap water in North America has decreased and consumption of bottled water has increased. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 11318912-1 2001 OBJECTIVES: Because of growing concern that constituents of drinking water may have adverse health effects, consumption of tap water in North America has decreased and consumption of bottled water has increased. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 11318912-2 2001 Our objectives were to 1) determine whether North American tap water contains clinically important levels of calcium (Ca2+), magnesium (Mg2+), and sodium (Na+) and 2) determine whether differences in mineral content of tap water and commercially available bottled waters are clinically important. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 11093645-10 2000 Application was illustrated by the analysis of water samples collected from tap water, ground water and farm water in the southern Taichung area. Water 47-52 nuclear RNA export factor 1 Homo sapiens 76-79 11052716-1 2000 In 1997 this laboratory initiated a research program with the objective of examining the effect that rinsing of produce with tap water would have on pesticide residues. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 11052716-8 2000 One subsample was processed unwashed, whereas the other was rinsed under tap water. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 11220594-6 2000 The analytical results obtained for standard reference materials are in good agreement with the certified or indicated values and satisfactory recoveries of spiked cobalt in tap water are obtained. Water 178-183 nuclear RNA export factor 1 Homo sapiens 174-177 11110211-9 2000 The results are therefore consistent with their relative concentration in tap water and their vapor pressures. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 11028268-11 2000 Tap water from municipal nets has not to be considered as relevant source of sporadic infections. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 12524742-0 2000 Fluoride levels best in tap water, study finds. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 11103297-13 2000 Tap water was a more important source of fluoride than soft drinks. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 10981483-4 2000 Sometimes the tap water showed very high aluminum content that does not permit the water treatment system to efficiently remove all the aluminum, forcing the use of water treatment systems with a double reverse-osmosis filter on line. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 10865315-16 2000 When an alternative disinfection technique is required, washing the speculum with chlorhexidine gluconate and tap water is preferred over wiping with a 70% isopropyl alcohol swab. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 11036787-7 2000 The use of tap water instead of spring water may be helpful to improve the efficacy of drug treatment via drinking water. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 11860936-9 2000 The positive detection rates (> 50 pg/ml) of microcystin in well, tap-water, river and pond water were 0.00%, 0.00%, 36.23% and 17.14% respectively. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 10973152-4 2000 RESULTS/CONCLUSIONS: The results of the adjusted model showed that the proportion of households without tap water was the variable that contributed the most to the increasing fluctuation of cholera incidence rates. Water 108-113 nuclear RNA export factor 1 Homo sapiens 104-107 10879874-2 2000 In order to provide reproducible samples with moderate presence of possible interferences, spiked tap water was used for this first set of experiments. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 11109210-9 2000 Black non-Hispanic children also drank more tap water (21.3 ml/kg/day) than white non-Hispanic children (12.7 ml/kg/day) and Hispanic children (14.9 ml/kg/day). Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 10916342-8 2000 Among the visitors to Ogose who were traced, 7 persons who stayed only one day during the outbreak and drank half a glass to 2 glasses (100 to 360 ml) of tap water had cryptosporidiosis confirmed by laboratory tests. Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 11256708-6 2000 In deionized water and a sample of chlorinated tap water, systematic biases relative to strict adherence to Method 552 were precise and could be corrected for using similarly treated standards and analyte-fortified (spiked) samples. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 10842904-0 2000 Colonic cleansing, fluid absorption, and discomfort following tap water and soapsuds enemas. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 10832370-0 2000 Bottled vs. tap water--how about fluoride and iodine? Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 11225875-0 2000 Determination of uranium in tap water by ICP-MS. A fast and accurate procedure has been developed for the determination of uranium at microg L(-1) level in tap and mineral water. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 10717374-9 2000 An estimated 17% of mothers lived in households with tap water lead concentrations of 10 microg/litre (the [WHO,] guideline) or above in 1993 compared with 49% in 1981. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 10728111-0 2000 Fluoride and bacterial content of bottled water vs tap water. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 10728111-1 2000 CONTEXT: Bottled water has become a status symbol and is frequently used in place of tap water. Water 17-22 nuclear RNA export factor 1 Homo sapiens 85-88 10728111-1 2000 CONTEXT: Bottled water has become a status symbol and is frequently used in place of tap water. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 10728111-17 2000 Recently, the Environmental Protection Agency, Washington, DC, published a final ruling that requires community water systems to regularly report to the public on the quality of local tap water; there are no similar proposals to determine the quality of bottled water through labeling. Water 112-117 nuclear RNA export factor 1 Homo sapiens 184-187 10800246-2 2000 BACKGROUND: Based on sporadic reports of microbial contamination of mineral waters, it has been recommended that, for safety reasons, particularly immunocompromised patients should drink tap water rather than bottled mineral water. Water 191-196 nuclear RNA export factor 1 Homo sapiens 187-190 10800246-11 2000 CONCLUSION: Tap water as well as bottled water are both supremely safe components of nutrition. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 10800246-12 2000 The recommendation that tap water is better than mineral water, particularly for high-risk patients, is not supported by the literature. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 10694773-7 2000 RESULTS: Iodine in tap water varied from 2.1 to 30.2 microg/l; the iodine content was in general highest in the eastern part of Denmark and lowest in the western part of Denmark. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 10662561-12 2000 Consumption of tap water in the hospital was commoner among affected staff members than among controls, but this did not reach significance (P = 0.1). Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 11022436-2 2000 Saline or tap water is often used to loosen the dressing and therefore help to remove it. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 10652914-9 2000 CONCLUSIONS: The use of Gd-DTPA as a positive contrast agent may not be imperative, and T1-weighted FLASH imaging in combination with true FISP imaging with ingestion of tap water can be very useful in evaluating AGC with MR imaging. Water 174-179 nuclear RNA export factor 1 Homo sapiens 170-173 10717374-13 2000 Nevertheless, between 63% and 76% of cases of mothers with blood lead concentrations of 10 microg/dl or above were attributable to tap water lead. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 10717374-15 2000 About 15% of infants may be exposed via bottle feeds to tap water lead concentrations that exceed the WHO guideline of 10 microg/litre. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 11203905-12 2000 Pasteurization of tap water can reduce contamination; this water can be used as acceptable dental treatment water (< 200 CFU/mL). Water 59-64 nuclear RNA export factor 1 Homo sapiens 18-21 10689212-6 2000 In the subgroup aged 21 to 60 years, the highest rates of seronegativity were found in individuals with higher level of education living in houses with tap water (66.6%). Water 156-161 nuclear RNA export factor 1 Homo sapiens 152-155 11203905-12 2000 Pasteurization of tap water can reduce contamination; this water can be used as acceptable dental treatment water (< 200 CFU/mL). Water 59-64 nuclear RNA export factor 1 Homo sapiens 18-21 10589502-3 1999 A 500 mL sample of tap water is preconcentrated by solid-phase extraction (SPE) with 300 mg combined polystyrene-divinylbenzene and methacrylate macroporous resins. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 10669294-4 1999 Sample capacity was investigated by injecting large volumes (up to 6 ml) using a high total hardness and chloride tap water. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 10669294-10 1999 Reproducibilities in tap water were 18% (5 microg l(-1), n=12) and 21% (1 microg l(-1), n=4) respectively for 1.5 and 6 ml injection volumes with conductivity detection, and 17% at 0.5 microg l(-1) (n=9) with spectrophotometric detection. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 10607459-1 1999 Chloroform in tap water has been a significant problem because it may be a carcinogenic substituent. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 10607459-3 1999 Iron ions in tap water cause discoloration and a bad odor. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 21662735-11 1999 The ability of the system to do practical analysis was demonstrated by the accurate determination of MMT in spiked samples of gasoline, human urine, and tap water. Water 157-162 nuclear RNA export factor 1 Homo sapiens 153-156 10585303-0 1999 Determination of the extent of excessive copper concentrations in the tap-water of households with copper pipes and an assessment of possible health hazards for infants. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 10585303-4 1999 To determine precisely a possible connection between the amount of copper in tap-water and the risk of early childhood liver disease, an attempt was first made, through an epidemiological survey, to determine the extent of excessive concentrations of copper in the tap-water of households with copper pipes. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 10585303-4 1999 To determine precisely a possible connection between the amount of copper in tap-water and the risk of early childhood liver disease, an attempt was first made, through an epidemiological survey, to determine the extent of excessive concentrations of copper in the tap-water of households with copper pipes. Water 269-274 nuclear RNA export factor 1 Homo sapiens 265-268 10574209-6 1999 The optimized procedure was applied to the analysis of HAAs in tap water and the results obtained by standard addition agreed with those of EPA method 552.2, whereas discrepancies due to matrix interferences were observed using external calibration. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 10571798-10 1999 As the high tap water concentration of strontium was adequately reduced during the water purification process, contamination of the final dialysis fluid occurred by the addition of concentrates contaminated with strontium. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 10571798-10 1999 As the high tap water concentration of strontium was adequately reduced during the water purification process, contamination of the final dialysis fluid occurred by the addition of concentrates contaminated with strontium. Water 83-88 nuclear RNA export factor 1 Homo sapiens 12-15 28308316-9 1999 Xylem water deltaD was also strongly dependent on tree size (diameter at breast height), with smaller trees appearing to preferentially tap deeper sources of soil water than larger trees. Water 6-11 nuclear RNA export factor 1 Homo sapiens 136-139 10489993-12 1999 The association was stronger among men with above-median tap water consumption. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 10549314-0 1999 A hospital outbreak of gastroenteritis possibly related to the contamination of tap water by a small round structured virus. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 10552714-7 1999 The proposed method has been applied to the determination of paraquat in tap water, milk, and white wine samples with recoveries of 89-104%. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 11203905-8 2000 RESULTS: Pasteurized water was significantly less contaminated than was tap water. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 11203905-12 2000 Pasteurization of tap water can reduce contamination; this water can be used as acceptable dental treatment water (< 200 CFU/mL). Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 10579409-3 1999 Tap water was supplied from 2 L cups, 1 cup per pen. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 10519171-2 1999 The aim of this study was to assess the relationships between daily tap-water consumption, As quantities thus ingested and biological arsenical impregnation. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 10503706-8 1999 Moreover, it is also shown that the annual effective dose due to inhalation of radon emanating from tap water and flushing water is negligible compared to the total annual dose for indoor radon in Algiers. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 10500466-1 1999 A case of thermal injury following the introduction of excessively hot tap water into the colon during irrigation of a sigmoid colostomy is described. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 10497939-5 1999 The method was applied to the trace determination of several sulphonates present in tap water, seawater and water from the Ebro river. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 18967666-6 1999 The developed methods were applied to Cu(II) and Zn(II) determination in natural and tap water. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 18967646-6 1999 Validation of the method was made by comparison of the results of analyses of tap water by another electrochemical method and by recovery test for river and mineral water. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 10552586-0 1999 Major degradation pathway of thiuram in tap water processed by oxidation with sodium hypochlorite. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 10552586-4 1999 Subsequently, it was suggested that monitoring of bis(dimethylcarbamoyl) disulfide, its trisulfide, and dimethylamine should be included for the management and control of thiuram in tap water processed by oxidation with sodium hypochlorite. Water 186-191 nuclear RNA export factor 1 Homo sapiens 182-185 10383875-0 1999 Chronic poisoning by copper in tap water: I. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 10383875-3 1999 Copper in tap water has caused a series of severe systemic diseases in Germany in recent years (copper induced liver cirrhosis). Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 10383875-4 1999 Besides cirrhosis, another type of disease with predominantly gastrointestinal symptoms has occurred which likewise appeared to be induced by copper in tap water. Water 156-161 nuclear RNA export factor 1 Homo sapiens 152-155 10383876-0 1999 Chronic poisoning by copper in tap water: II. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 10383876-3 1999 Copper in tap water has caused a series of severe systemic diseases in Germany in recent years (chronic copper poisoning, CCuP). Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 10383879-2 1999 Incorrect application of copper tubes in households may lead to elevated copper concentrations in tap water. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 10399335-7 1999 The repeatability and the reproducibility between days of the method (n = 6), expressed as relative standard deviation, for tap water spiked at a level of 1 ng l-1 were between 5.7 and 25.6% and between 7.6 and 26.5%, respectively. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 10229903-4 1999 Iodine in tap water obtained from 55 different locations in Denmark varied from <1.0 to 139 microg/l. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 11821591-3 1999 The mean objective reduction in sweat output was 49%, 51%, 26%, and 22% at week 3, 6, 10, and 12, respectively, since the start of treatment with tap water iontophoresis The mean subjective improvements were 43%, 59%, 30%, and 12% at week 3, 6,10, and 12, respectively. Water 150-155 nuclear RNA export factor 1 Homo sapiens 146-149 11821591-5 1999 We conclude that tap water iontophoresis is a safe and useful treatment modality for palmar hyperhidrosis. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 10229903-7 1999 A statistically significant correlation was found between tap water iodine content today and the urinary iodine excretion measured in 41 towns in 1967 (r=0.68, P<0.001). Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 10229903-10 1999 We found that iodine in tap water was a major determinant of regional differences in iodine intake in Denmark. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 10337604-3 1999 Thus we examined the relationship between first morning tap-water lead levels measured in homes in the 1970s and levels of lead in bone measured in the 1990s among middle-aged to elderly men who lived in those homes. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 10780194-5 1999 RESULTS: The gastric emptying of this mineral water was significantly faster than that of tap water, both in dyspeptic patients and in normals. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 10337604-1 1999 Tap water in a city like Boston, which has old houses containing lead plumbing, is known to be a significant source of potential lead exposure. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 10337604-9 1999 We conclude that ingestion of lead-contaminated tap water is an important predictor of elevated bone lead levels later in life. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 10453121-6 1998 Sixty (23%) women of the Bodija market mentioned that tap water was the source of drinking water for their children, while 91 (34%) brought water from their homes, and 45 (17%) bought it from vendors in the market. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 10067727-7 1999 These values are for milk reconstituted with aluminum-free water under laboratory conditions; formulas prepared with tap water in the University Hospital"s infant-feeding unit had even higher aluminum content. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 10023623-3 1999 Detection limits down to 0.1-4 micrograms l-1 were obtained for spiked tap water following a preconcentration step. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 16303407-11 1999 Patients more frequently washed their storage cases in tap water than controls (P<0.05) with resulting contamination, kept storage cases wet rather than air drying them (P<0.05), and had coliform bacteria cultured from the storage case (P<0.05) and had viable Acanthamoeba within the storage case (P<0.0001). Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 16303407-17 1999 CONCLUSIONS: Failure to disinfect contact lenses, non-compliant use of chlorine tablets and/or introduction of tap water rinsing of storage cases were associated with increased risk of Acanthamoeba infection. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 11396041-6 1999 RESULTS: Increased consumption of infant formulas and decreased consumption of tap water and cow"s milk were seen in the CSFII for infants compared to the NFCS. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 10377881-5 1999 The third (exogenous) level mechanisms have been found in the study of the lymphocytic functions of cyanobacterial exometabolites and their derivatives from tap water probes. Water 161-166 nuclear RNA export factor 1 Homo sapiens 157-160 21644686-4 1998 The analytical figures of merit are demonstrated by measurements of very low concentrations of Cr(VI) in tap water. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 11864472-1 1999 OBJECTIVE: To study the harmful effects of organic concentrates from tap water on mammal animals in vivo. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 11864472-8 1999 It suggested that organic pollutants concentrated from tap water had potential carcinogenic effects on mammal animals. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 10220922-2 1999 The optimum pH value for the extraction of the HTDPs from fortified tap water at 2 micrograms/l is 3.0. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 10214678-5 1999 They were most often caused by tap water contamination associated with parasites and viruses, despite good compliance of the water treatment procedures. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 9873221-6 1999 Each calculus was subjected to a water flow of 2 liters/24 h. The capacity of the Anticolana Valley (Fiuggi) water to dissolve human and synthetic calculi was found to be much higher than that of distilled water which in turn was significantly more effective than tap (ACEA) water. Water 109-114 nuclear RNA export factor 1 Homo sapiens 264-267 9873221-6 1999 Each calculus was subjected to a water flow of 2 liters/24 h. The capacity of the Anticolana Valley (Fiuggi) water to dissolve human and synthetic calculi was found to be much higher than that of distilled water which in turn was significantly more effective than tap (ACEA) water. Water 109-114 nuclear RNA export factor 1 Homo sapiens 264-267 9873221-6 1999 Each calculus was subjected to a water flow of 2 liters/24 h. The capacity of the Anticolana Valley (Fiuggi) water to dissolve human and synthetic calculi was found to be much higher than that of distilled water which in turn was significantly more effective than tap (ACEA) water. Water 109-114 nuclear RNA export factor 1 Homo sapiens 264-267 9894347-0 1998 Comparative study of a solid-phase extraction system coupled to capillary electrophoresis in the determination of haloacetic compounds in tap water. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 9854881-3 1998 The descriptive epidemiology, attack rates, a case control study, and the detection of oocysts in the water suggested strongly that the outbreak was associated with drinking unboiled tap water that originated from one deep chalk borehole. Water 102-107 nuclear RNA export factor 1 Homo sapiens 183-186 9854881-3 1998 The descriptive epidemiology, attack rates, a case control study, and the detection of oocysts in the water suggested strongly that the outbreak was associated with drinking unboiled tap water that originated from one deep chalk borehole. Water 187-192 nuclear RNA export factor 1 Homo sapiens 183-186 18967359-7 1998 Sample digestion for water with low organic content such as tap water and clean ground water and some clean surface water can be omitted. Water 21-26 nuclear RNA export factor 1 Homo sapiens 60-63 9871348-3 1998 Following a simple potassium citrate flotation concentrate clean-up procedure, mean recoveries were 56.7% for the tap water samples and 60.9% for river water samples. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 9830712-1 1998 The identification of alkylphosphonic acids in spiked tap water has been investigated by on-line capillary electrophoresis-UV spectrometry-mass spectrometry (CE-UV-MS) in negative-ion mode. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 9874038-0 1998 Nickel in tap water in Warsaw. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 9776190-13 1998 CONCLUSIONS: Showering, hair rinsing, and head submersion in clean tap water do not promote water entry into the middle ear. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-6 1998 Our findings indicate that it is possible to stratify the population into subsets by the amount of tap water consumed. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 9825786-4 1998 Although 18% and 31% of subjects, respectively, denied any tap water consumption at home or work, all but one from each cohort responded positively to having at least one possible alternate source of tap water ingestion such as using tap water to brush teeth or drinking tap water offered in a restaurant. Water 204-209 nuclear RNA export factor 1 Homo sapiens 200-203 9825786-7 1998 This suggests that an observational epidemiologic study of the risk of contracting cryptosporidiosis from everyday tap water consumption is feasible. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 9732068-10 1998 Patients perceive drinking water to be a substantial risk factor for infectious diarrhea and incur significant expense to avoid tap water. Water 27-32 nuclear RNA export factor 1 Homo sapiens 128-131 9867427-0 1998 Tap water scald burns in children. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 9733114-3 1998 A control treatment was normal tap water and the other three treatments comprised the addition to the tap water of 1,000 mg/L sodium as NaCl, 5,000 mg/L NH4Cl, or 5,000 mg/L KHCO3, supplied from age 2 to 47 d. At Day 28, equally sized subsets of these groups were moved to individual cages, where they received a severe exposure to ambient cold. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 9807928-5 1998 The results show that the respondents were aware that hand pump/tap water is safe and took care to use these safe sources for drinking purposes. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 9681978-9 1998 Analyses of tap water revealed lead values under 0. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 9749401-0 1998 Outbreak of nosocomial urinary tract infections due to Pseudomonas aeruginosa in a paediatric surgical unit associated with tap-water contamination. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 9749401-5 1998 Multiple P. aeruginosa isolates were also found in the tap water, as the only putative source of contamination. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 9749401-9 1998 These results illustrate an unexpected risk of nosocomial infection and emphasizes the importance of checking tap water to prevent bacterial contamination through handwashing in contaminated water. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 10065925-3 1998 Sucrose concentration (0.03-0.6 M, corresponding to 1-20%) and ethanol concentration (0-4%) were gradually increased in tap water and in a 0.6 M (ca. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 9639628-4 1998 The source of infection was identified as contaminated tap water. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 9707354-2 1998 They received one 20 mg manidipine dihydrochloride tablet with 100 ml of tap water after a standard breakfast. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 9651449-0 1998 Tap water scald burns in children, by K. W. Feldman, R. T. Schaller, J. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 9647377-3 1998 METHODS: In 21 consecutive patients, 5 to 10 mL of 1.5% acetic acid was sprayed onto the distal esophagus using a spray catheter, followed immediately by spraying 50 mL of tap water. Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 9652120-4 1998 The method was used to determine haloacetic acids in chlorine tap water using the liquid-liquid extraction process. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 9697363-0 1998 [Late manifestation of a form of Indian childhood cirrhosis based on chronic copper poisoning caused by sour tap water]. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 12293742-10 1998 The provision of clean tap-water and facilities to deworm pre-school children would also be welcomed. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 21651287-6 1998 The procedure has been applied to tap water samples (spiked at 0.10 and 0.20 mug L(-)(1) levels) with good results, similar to those obtained with a HPLC system with a conventional fluorescence detector. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 9654799-6 1998 Opposition to fluoridation was lower among those who believed their tap water was fluoridated (even if not): 19.9% vs 34.5%, p < 0.001. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 9530806-3 1998 The system is relatively simple and relies on heated tap water or ice to adjust the temperature. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 9637077-0 1998 Lognormal distributions for total water intake and tap water intake by pregnant and lactating women in the United States. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 9617685-0 1998 Multi-resistant Pseudomonas aeruginosa outbreak associated with contaminated tap water in a neurosurgery intensive care unit. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 9617685-4 1998 P. aeruginosa O11 with the same resistance pattern was isolated from tap water. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 9617685-6 1998 DNA macrorestriction analysis with XbaI established the similarity of the isolates from patients, tap water and solutions. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 9617685-8 1998 The sinks were presumably the main source of P. aeruginosa during this outbreak, via the hands of the nursing staff or nutrition solutions contaminated with tap water. Water 161-166 nuclear RNA export factor 1 Homo sapiens 157-160 9644340-5 1998 Tap water should not be used to rinse any respiratory therapy equipment. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 9432970-0 1998 Assessment of water use for estimating exposure to tap water contaminants. Water 14-19 nuclear RNA export factor 1 Homo sapiens 51-54 9432970-0 1998 Assessment of water use for estimating exposure to tap water contaminants. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 9432970-1 1998 Epidemiological studies examining the association between exposure to tap water contaminants (such as chlorination by-products) and disease outcomes (such as cancer and adverse reproductive outcomes) have been limited by inaccurate exposure assessment. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 9432970-2 1998 Failure to take into account the variation in beverage and tap water consumption and exposure to volatile contaminants through inhalation and dermal absorption can introduce misclassification in assessing the association between exposure to tap water contaminants and health. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 9432970-2 1998 Failure to take into account the variation in beverage and tap water consumption and exposure to volatile contaminants through inhalation and dermal absorption can introduce misclassification in assessing the association between exposure to tap water contaminants and health. Water 245-250 nuclear RNA export factor 1 Homo sapiens 241-244 9432970-3 1998 To refine exposure assessment of tap water contaminants, we describe in detail the tap water consumption, showering, and bathing habits of pregnant women and their male partners as assessed by a questionnaire and a 3-day water diary. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 9432970-3 1998 To refine exposure assessment of tap water contaminants, we describe in detail the tap water consumption, showering, and bathing habits of pregnant women and their male partners as assessed by a questionnaire and a 3-day water diary. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 9432970-5 1998 Half of the participants consumed tap water on a regular basis with an overall mean +/- 1 standard deviation (SD) of 0. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 12456181-1 1998 Crystals were detected in glass bottles containing autoclaved (standard cycle: 1218 C, 17 lb/in2, for 20 min) tap water. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 9551332-0 1998 [Therapy of hyperhidrosis with tap water iontophoresis. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 11819229-4 1998 When the drinking water switched from river and well water to tap water, the gastric cancer incidence decreased to 30.33/10(5) and 26.10/10(5), and the gastric cancer mortality decreased by 59% and 57% respectively.CONCLUSION: The quality of drinking water is one of the important factors of increased incidence of gastric cancer in Changle County, and water quality improvement has a beneficial effect, but the cause of high gastric cancer incidence may be multi-factorial in this area. Water 18-23 nuclear RNA export factor 1 Homo sapiens 62-65 9517519-6 1998 The fraction time esophageal pH <4 was increased after both alcoholic beverages compared with tap water (0.9%; 0.2-5.8%; P < 0.01 versus white wine, P < 0.05 versus red wine) with a greater fraction time after white wine (13.2; 0.3-58.1 ) than after red wine (2.3; 0.7-24.4; P < 0.05). Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 9514043-3 1998 Most of the people (56%) were drinking some bottled water or filtered tap water and 25% of water intake was away from home. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 9514043-3 1998 Most of the people (56%) were drinking some bottled water or filtered tap water and 25% of water intake was away from home. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 9514044-5 1998 The geometric mean of lead in the random tap water samples was 0.5 microgram/l (95% C.I., 0.5-0.6) and 0.7 microgram/l (95% C.I., 0.6-0.8) in the stagnant tap water samples. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 9448748-4 1997 Elevated human exposure to this element, mostly caused by the intake of contaminated tap water, is associated with increased incidences of cancer at various sites. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 9502190-5 1998 One minute after starting the lipid perfusion, 15 g of lactulose dissolved in 20 mL of tap water was infused. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 9476455-9 1997 In addition, certain groups of children were much likely to develop protozoal infections including children whose families lacked tap water inside dwelling (OR = 1.85, 95 per cent CI = 1.26-2.77) and disposed human excreta in septic tank very close to the dwelling (OR = 2.17, 95 per cent CI = 1.43-3.75). Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 9374582-4 1997 Most often tap water, either in the form of supplemental feedings or overly dilute formula, has been given in excessive amounts over relatively short periods of time. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 9463929-0 1997 Risk characterization of methyl tertiary butyl ether (MTBE) in tap water. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 9463929-10 1997 Although some individuals may be exposed to very high concentrations of MTBE in tap water immediately following a localized spill, these exposures are likely to be brief in duration due to large-scale dilution and rapid volatilization of MTBE, the institution of emergency response and remediation measures to minimize human exposures, and the low taste and odor thresholds of MTBE which ensure that its presence in tap water is readily detected at concentrations well below the threshold for human injury. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 9408995-0 1997 Liquid chromatography-atmospheric pressure ionization mass spectrometry for the determination of chloro- and nitrophenolic compounds in tap water and sea water. Water 140-145 nuclear RNA export factor 1 Homo sapiens 136-139 9431267-0 1997 Reduced skin hyperemia during tap water iontophoresis after intake of acetylsalicylic acid. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 9431267-1 1997 Skin microcirculation and skin temperature of 10 healthy subjects (6 men and 4 women, 20-44 yr of age) without any vascular diseases were registered when a thermoindifferent tap water iontophoresis was applied. Water 178-183 nuclear RNA export factor 1 Homo sapiens 174-177 9431267-7 1997 After ending tap water iontophoresis, the skin temperature increased more on the cathode side than on the anode side (P < 0.001). Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 9460351-0 1997 Endoscopy water source: tap or sterile water? Water 10-15 nuclear RNA export factor 1 Homo sapiens 24-27 9460351-6 1997 Many of the tap water samples were positive for normal flora found in city water sources. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 9460351-8 1997 The use of tap water and clean water bottles was found to carry no greater risk than using sterile water and sterile bottles. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 15344248-1 1997 I"ve always used tap water for drinking and cooking, but I wonder if it"s safe. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 9427073-10 1997 A significantly greater rate of clinical remission was observed in subjects enjoying home tap water supplies (p < 0.01). Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 18966962-6 1997 The proposed procedure was applied to determination of chromium (VI) in tap water. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 9372633-1 1997 The variation in lead concentration was measured by thermal ionisation mass spectrometry isotope dilution in household tap water throughout the day when the plumbing system was not fully flushed. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 9372633-3 1997 High precision lead isotopic measurements showed that approximately 50% of the lead in these water samples derives from the tap "housing" compared with the overall household system. Water 93-98 nuclear RNA export factor 1 Homo sapiens 124-127 9299765-3 1997 Drinking water samples were taken from the first tap after the water was led into the building. Water 9-14 nuclear RNA export factor 1 Homo sapiens 49-52 9323392-8 1997 Restaurant water and ice samples contained more than 40 milligrams of fluoride per liter (mg/L), more than 20 times the recommended limit, and a tap water sample from a house located near the main treatment plant contained 200 mg/l of fluoride. Water 149-154 nuclear RNA export factor 1 Homo sapiens 145-148 9299743-5 1997 The ensuing method was applied to river and tap water with good repeatability and reproducibility, and no interference from the sample matrix. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 9100580-8 1997 In contrast, fasted subjects who received tap water did not respond to the Trier Social Stress Test with significant changes in cortisol levels (F = 6.27, P < 0.001). Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 9463965-4 1997 The proposed method was validated by analysing freeze-dried tap water samples with a high content in pesticides of different chemical functionalities. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 19679908-7 1997 Tap-water burns are considerable more common in Iceland compared to other countries. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 9228799-3 1997 The lowest detectable concentrations of the pesticides are between 1-5 ng l(-1), relative recoveries range from 92-105% in tap water spiked at 100 ng l(-1) and the relative standard deviations are in the range 5-12%. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 18966990-9 1997 The proposed method was applied to the determination of both analytes in river and tap water and the results were consistent with those provided by the AAS standard method. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 9193982-1 1997 OBJECTIVE: To investigate the bacterial cleanliness of tap water in a large accident and emergency (A&E) department for its possible use in the cleansing and irrigation of open traumatic wounds. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 9193982-2 1997 METHODS: Tap water samples were collected from different areas within the department and analysed on two separate occasions for coliforms, S aureus, clostridia, pseudomonas, and beta haemolytic streptococci. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 9193982-4 1997 CONCLUSIONS: Tap water of drinking quality can be used to irrigate open traumatic wounds. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 9150766-1 1997 Chlorinated tap water often contains 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX), which is a potent directly acting bacterial mutagen. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 9134720-4 1997 HPC bacteria were isolated from bottled and tap water samples by enumerating them under physical and chemical conditions analogous to human physiology. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 18966793-8 1997 Calibration and the standard addition methods are discussed and demonstrated by determining copper in tap water as a method of testing the procedure. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 9084392-0 1997 Reducing the incidence of tap-water scalds: strategies for physicians. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 9084392-4 1997 Tap-water scalds are preventable. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 8892418-0 1996 Is lead in tap water still a public health problem? Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 9273663-7 1997 Tap water in Poznan contained 0.2 mg F3/dm3, on average. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 9096270-7 1997 Each subject provided a 24-hour urine collection after ingestion of mineral water over a period of 3 days; after a suitable rest period the protocol was repeated using local tap water (Ca: 13 ppm, Mg: 1 ppm). Water 178-183 nuclear RNA export factor 1 Homo sapiens 174-177 9407174-16 1997 CONCLUSION: Each cleansing agent, even normal tap water, influences the skin surface. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 9505333-2 1997 Tap water was exchanged for a 24% EDTA solution as irrigation agent during root planing with a piezo scaler. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 8982415-0 1996 Successful treatment of dyshidrotic hand eczema using tap water iontophoresis with pulsed direct current. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 8982415-1 1996 The efficacy of tap water iontophoresis in treating palmoplantar hyperhidrosis has been sufficiently documented and has led to its extensive use in clinical practice. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 8982415-2 1996 In order to test the efficacy of this treatment modality in cases of dyshidrotic hand eczema, 20 patients were treated with tap water iontophoresis in addition to two-sided steroid-free topical therapy in a randomized half-side-study. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 8982415-4 1996 Only those sides treated with tap water iontophoresis showed significant improvement. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 8892418-7 1996 MAIN OUTCOME MEASURES: Mean geometric blood lead concentrations and the prevalence of raised tap water lead concentration. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 8892418-9 1996 Tap water lead remained the main correlate or raised maternal blood lead concentrations and accounted for 62% and 76% of cases of maternal blood lead concentrations above 5 and 10 micrograms/dl (0.24 and 0.48 mumol/l) respectively. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 8892418-10 1996 The geometric mean maternal blood lead concentration was 3.65 micrograms/dl (0.18 mumol/l) in a random sample of mothers and 3.16 micrograms/dl (0.15 mumol/l) in mothers whose tap water lead concentrations were consistently below 2 micrograms/l (9.7 nmol/l). Water 180-185 nuclear RNA export factor 1 Homo sapiens 176-179 8892418-12 1996 An estimated 13% of infants were exposed via bottle feeds to tap water lead concentrations exceeding the World Health Organisation"s guideline of 10 micrograms/l (48.3 nmol/l). Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 8902118-0 1996 Use of sterile compared with tap water in gastrointestinal endoscopic procedures. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 8902118-13 1996 Our pilot study suggests that the use of tap water as compared with sterile water may be practical as well as provide cost savings. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 9148646-5 1996 The proposed method was successfully applied to the determination of copper(II) in tap water and biological material. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 8908254-5 1996 At last follow-up examination, air conduction thresholds of patients drinking fluoridated tap water were found to be significantly better than those of patients drinking fluoride-poor water, likewise there were significant differences in bone conduction thresholds at 1, 2, and 4 kHz. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 21619368-11 1996 An excellent agreement was found between the results obtained for standard solutions prepared using NANOpure water and spiked tap water samples. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 8806217-1 1996 Contaminated tap water is one source of potentially hazardous air pollutants in residential indoor air. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 8755678-8 1996 In contrast, drinking tap water decreased the risk. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 9027233-5 1996 In addition, tests of the peakwise algorithms were made using a set of liquid water samples with delta D Tap Water over the range of 39-407/1000 with uncorrected data with precisions of SD-(delta D Tap Water < 34/1000 and accuracy within 11/1000. Water 78-83 nuclear RNA export factor 1 Homo sapiens 105-108 21619304-5 1996 The detection limit (S/N = 2) and linear range for a 1 L water sample are 2 mug of C L(-)(1) and 10-2500 mug of C L(-)(1), respectively, and they can be adjusted using samples ranging from 100 mL to 2 L. Good repeatablity (RSD less than 10%) and close to 100% recoveries were obtained for KHP added to real samples such as deionized, mineral, tap, and river water and seawater. Water 57-62 nuclear RNA export factor 1 Homo sapiens 343-346 8686077-3 1996 The cause was exogenous deposition of copper from domestic tap water which contained an increased copper concentration. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 8925642-5 1996 The results showed a significant colecystocinetic effect of the mineral water compared with tap water. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 18966545-8 1996 Two different modes of standard addition (the standard lead solutions being added before and after preconcentration) were used for analysis of tap water samples, and the results obtained by the two modes were found to be quite consistent. Water 147-152 nuclear RNA export factor 1 Homo sapiens 143-146 8743440-6 1996 The mean log variant frequency of peripheral lymphocytes was significantly higher in the medium well water exposure group than in the low and medium tap water exposure groups. Water 153-158 nuclear RNA export factor 1 Homo sapiens 149-152 8602703-9 1996 In the case-control study, persons who drank any unboiled tap water were four times more likely than persons who drank only bottled water to have had cryptosporidiosis (odds ratio, 4.22 [95% Cl, 1.22 to 14.65]; P = 0.02). Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 8833615-4 1996 Total fluid intake, and tap water in particular, showed a strong inverse dose-response relationship to cancer risk among women (odds ratio (OR) for highest to lowest quartile of total fluid intake = 0.3; trend P < 0.01).. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 8740859-4 1996 In some cases colony counts in the filtered water were 10,000 times those in tap water. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 8762348-1 1996 STUDY OBJECTIVES: To investigate whether exposure to tap water contaminated in a major river pollution incident with 2 ethyl 5,5 dimethyl 1,3 dioxane (EDD) and 2 ethyl 4 methyl 1,3 dioxolane (EMD) was associated with an increase of self reported symptoms. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 8727616-0 1996 Gram-negative bacteremia in open-heart-surgery patients traced to probable tap-water contamination of pressure-monitoring equipment. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 28307187-11 1996 prionotes, there was a strong negative correlation between the percentage of water in the stem base of a plant which was derived from the tap root (ground water) and the amount of precipitation which fell at the site. Water 77-82 nuclear RNA export factor 1 Homo sapiens 138-141 8762348-15 1996 Because concentrations of the contaminants would be expected to be evenly distributed in the tap water in the affected area, irrespective of taste or odour, and because of the known toxicity of the parent compounds of EMD and EDD, it is concluded that the increase in self reported symptoms in the study group respondents was associated with noticing the unpleasant taste or odour of the tap water and not with the chemical contamination. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 8834861-0 1996 Ingestion, inhalation, and dermal exposures to chloroform and trichloroethene from tap water. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 20953017-9 1995 It showed that methenamine is superior to tap water iontophoresis and acts faster than glutaraldehyde. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 8834861-4 1996 Analysis of chloroform and trichloethene in expired breath, compounds regulated in water, was also used to determine uptake from tap water by each route (inhalation, ingestion, or absorption). Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 8834731-13 1996 Degassed 17 degrees C water produced no visualizable bubbles, while aerated tap water at 43 degrees C showed a high degree of cavitation. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 8804004-3 1996 Tap water must be considered as the main source of dialysate trace metal contamination. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 8711190-6 1996 Also the tap water samples presented a low concentration of these substances. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 27519332-6 1995 The medication was administered after an overnight fast (10 hours) with 200ml of tap water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 8557088-3 1995 In a case-control study, a strong association between having drunk unboiled tap water from these sources, and a dose-response relationship were found. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 8609195-0 1995 Increased sensitivity of poliovirus detection in tap water concentrates by reverse transcriptase-polymerase chain reaction. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 8609195-1 1995 This study developed a methodology to increase the sensitivity of enteric virus detection in tap water concentrates. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 8609195-8 1995 PCI extraction was found to be sufficient to remove inhibitory substances for reverse transcriptase (RT)-seminested PCR with a sensitivity of 0.2 plaque-forming units/10 microliters (0.2 PFU/l tap water). Water 197-202 nuclear RNA export factor 1 Homo sapiens 193-196 8564432-4 1995 All primates tested to date like sucrose and prefer this sweet substance to tap water. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 7589267-3 1995 A case-control study showed a significant association between illness and consumption of tap water supplied by a particular water company, as well as a dose response effect. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 7639439-11 1995 Epidemiologic studies implicated tap water from a physicians" dormitory as the most likely source of the outbreak. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 7749279-0 1995 Comparison of trihalomethane in tap water with and without activated carbon adsorption during the preparation process of tap water. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 7558823-1 1995 Tap water iontophoresis with direct current represents the therapy of choice in palmoplantar hyperhidrosis. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 7558823-4 1995 The aim of this study was to find ways of minimizing side effects, increasing safety standards and reducing the technical complications of tap water iontophoresis without loss of efficacy. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 7558823-5 1995 In a blind study, 30 patients with palmar hyperhidrosis were treated with tap water iontophoresis using pulsed direct current of 4.3 kHz or 10.0 kHz. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 7558823-12 1995 Because of the minimal side effects, despite minor loss of efficacy tap water iontophoresis with pulsed direct current can be a valuable alternative treatment for palmar hyperhidrosis. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 7609172-4 1995 Complications are relatively minor and tap water appears to be a safe solution for the antegrade continence enema. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 7762628-1 1995 Determination of deuterium (D) concentration in tap water and urine is demonstrated to average error approximately 0.5% (coefficient of variation) using a 400-MHz nuclear magnetic resonance (NMR) instrument. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 7672067-0 1995 Risk factors for hepatitis A infection in France: drinking tap water may be of importance. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 7672067-5 1995 Multivariate analysis found that high level of seroprevalence was also associated with tap water consumption (odd ratio (OR) = 1.56; p < 0.04), overseas travels (OR = 2.26; p < 0.001) and was higher for recruits reporting an history of clinical jaundice (OR = 2.27; p < 0.01). Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 7672067-6 1995 Together with more anticipated factors, tap water consumption may be of importance in France and this study points out the potential part taken by chlorinated water. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 7672067-6 1995 Together with more anticipated factors, tap water consumption may be of importance in France and this study points out the potential part taken by chlorinated water. Water 159-164 nuclear RNA export factor 1 Homo sapiens 40-43 7704192-2 1995 Tap water samples of 400 ml are saturated with sodium chloride and extracted once with 500 microliters of toluene. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 18966240-8 1995 The proposed method was applied to the determination of tin in tap water, hair, serum samples and geological reference samples. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 25121193-0 1995 Environmental Medicine: Integrating a Missing Element into Medical Education People are increasingly concerned about potential environmental health hazards and often ask their physicians questions such as: "Is the tap water safe to drink?" Water 218-223 nuclear RNA export factor 1 Homo sapiens 214-217 7716056-4 1994 Taking into account two following facts: 1) no evidence of renal calculi when the patient was outside her own house and 2) very high concentration of calcium in her home tap water, the role of environmental factors in the pathogenesis of nephrolithiasis in presented patient is very likely. Water 174-179 nuclear RNA export factor 1 Homo sapiens 170-173 7729383-4 1995 Results from the analysis of fluoride sources showed that 61% of tap water samples had fluoride levels above the optimal level of 0.7-1.2 ppm. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 7666747-3 1995 About 250 ml of tap water was administered per os into the airways of severely ill and comatose patients, and death occurred about one hour later. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 7899096-3 1995 The average daily fluoride intake per kilogram body weight from optimally fluoridated tap water was highest (0.080 mg/kg/d) from 7 to 9 months of age, and declined linearly to 0.034 mg/kg/d at 12.5 to 13 years of age. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 7968167-4 1994 Each participant produced 15 swallows of 15 mL of tap water both normally and with a 12-mm bite block placed between the molars. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 7822199-11 1994 Plain tap water is used without additives. Water 10-15 nuclear RNA export factor 1 Homo sapiens 6-9 8085144-3 1994 Tap water lead levels at various locations in the city were < 5 micrograms/l. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 18966134-8 1994 Tap water conductivity measurements were made using CaCl(2) reference solution. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 7978329-2 1994 The determination of several triazines, organophosphorus pesticides, sulfur containing compounds in tap water was performed by SPE-GC using polymer-packed precolumns and flame ionization (FID), nitrogen-phosphorus (NPD) or flame photometric (FPD) detection. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 7978329-6 1994 Analyte recovery was at least 72% when 10 ml of tap-water sample were analysed. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 8091252-1 1994 Animal models suggest that citrate-containing compounds augment absorption of aluminum from food and tap water, causing aluminum accumulation in bone and brain despite normal renal function. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 8202947-0 1994 Lead concentration in tap-water and in blood of selected schoolchildren in southern Saxonia. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 8061662-1 1994 Tap water, flushing water and drinking water including natural mineral water, artificial mineral water and distilled water have been investigated for their radon concentrations. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 8061662-2 1994 It has been found that the radon concentration in natural mineral water samples is the highest and that in tap water is the second highest, while other categories have values very near to the detection limit. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 8061662-4 1994 It is found that annual effective dose due to direct consumption of water (mineral and tap water) is far greater than that due to inhalation of radon emanated from tap water and flushing water. Water 68-73 nuclear RNA export factor 1 Homo sapiens 87-90 8061662-4 1994 It is found that annual effective dose due to direct consumption of water (mineral and tap water) is far greater than that due to inhalation of radon emanated from tap water and flushing water. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 8061662-4 1994 It is found that annual effective dose due to direct consumption of water (mineral and tap water) is far greater than that due to inhalation of radon emanated from tap water and flushing water. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 8061662-5 1994 Moreover, it is also shown that the annual effective doses due to inhalation of radon emanated from tap water and flushing water is negligible when compared to the total annual effective dose for indoor radon in Hong Kong. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 18966063-7 1994 The method has been applied to the analysis of Cr(III) in tap water. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 7943927-6 1994 During the epidemic period, the hospital"s chlorinated well-water system malfunctioned; chlorine levels were undetectable and tap water samples contained elevated microbial levels, including total and fecal coliform bacteria. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 8202947-1 1994 In a study of associations between lead in blood and in tap-water, 113 blood samples and 140 tap-water samples of schoolchildren aged 9 to 12 years were analysed. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 8202947-1 1994 In a study of associations between lead in blood and in tap-water, 113 blood samples and 140 tap-water samples of schoolchildren aged 9 to 12 years were analysed. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 8202947-2 1994 Median and maximum values of blood lead were 8.3 and 34.0 micrograms/dl and of lead in tap water 24 and 2600 micrograms/l. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 8202947-4 1994 The pH values of the tap-water varied from 5.0 to 8.1. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 8202947-5 1994 Both factors involved, i.e., lead pipes and acidic tap-water, have to be amended in order to reduce lead exposure in some regions or locations in Germany. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 8036126-1 1994 Earlier data showed that subjects presented with two samples of distilled water and one of tap water were significantly more consistent in choosing the tap water as preferred than in identifying it as the odd sample in the set. Water 74-79 nuclear RNA export factor 1 Homo sapiens 152-155 7993588-6 1994 During the accident, study subjects who experienced peculiar taste or odor in the tap water were significantly more in the exposed areas (92% vs. 34.3%). Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 7915292-3 1994 Discrepancies between recommended and local practice included lack of specification of detergent/cleaning agent (57%), inadequate contact time for chemical disinfection (40%) and the use of tap water rather than sterile water for rinsing the disinfected bronchoscope (39.7%). Water 194-199 nuclear RNA export factor 1 Homo sapiens 190-193 8036126-1 1994 Earlier data showed that subjects presented with two samples of distilled water and one of tap water were significantly more consistent in choosing the tap water as preferred than in identifying it as the odd sample in the set. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 8036126-1 1994 Earlier data showed that subjects presented with two samples of distilled water and one of tap water were significantly more consistent in choosing the tap water as preferred than in identifying it as the odd sample in the set. Water 95-100 nuclear RNA export factor 1 Homo sapiens 152-155 8036126-1 1994 Earlier data showed that subjects presented with two samples of distilled water and one of tap water were significantly more consistent in choosing the tap water as preferred than in identifying it as the odd sample in the set. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 8036126-1 1994 Earlier data showed that subjects presented with two samples of distilled water and one of tap water were significantly more consistent in choosing the tap water as preferred than in identifying it as the odd sample in the set. Water 95-100 nuclear RNA export factor 1 Homo sapiens 152-155 8057971-6 1994 Chlorinated tap-water and table salt ingestion must also be among the environmental factors studied for correlation to HIV infection. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 24242053-3 1994 quinquefasciatus egg rafts than did the untreated tap water. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 8308130-2 1993 All Legionella strains isolated from tap water in hospitals could be detected distinctly. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 8854898-1 1994 Recently, social concerns regarding tap water quality have increased, mainly because of the possible reduction in safety due to contamination of tap water by various chemicals and more frequent occurrence of the strange odors and tastes in as a result of resource water eutrophication. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 8854898-1 1994 Recently, social concerns regarding tap water quality have increased, mainly because of the possible reduction in safety due to contamination of tap water by various chemicals and more frequent occurrence of the strange odors and tastes in as a result of resource water eutrophication. Water 149-154 nuclear RNA export factor 1 Homo sapiens 36-39 8188820-0 1994 Suitability of autoclaved tap water for preparation of ELISA reagents and washing buffer. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 8188820-2 1994 The performance of the assay, using autoclaved tap water (AT-ELISA) compared favourably to that of the standard assay, using ultrapure water (UP-ELISA) in detecting anti-PRV antibodies in sequential serum samples from a pig experimentally infected with PRV. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 8188820-4 1994 The results suggest that autoclaved tap water may be substituted for ultrapure water for the preparation of ELISA reagents when or where ultrapure water may not be available. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 8303817-8 1993 Minimal dilution of aqueous suspension activated charcoal with tap water greatly increased flow rate through small-bore tubes. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 8214243-0 1993 Preventing tap water scalds: do consumers change their preset thermostats. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 8132983-8 1993 M xenopi isolation was attributed to exposure of clinical specimens to tap water, including rinsing of bronchoscopes with tap water after disinfection, irrigation with tap water during colonoscopy, gargling with tap water before sputum collection, and collecting urine in recently rinsed bedpans. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 8250567-1 1993 The abilities of 10 hygienic hand-washing agents and tap water (containing approximately 0.5 ppm of free chlorine) to eliminate strain HM-175 of hepatitis A virus (HAV) and poliovirus (PV) type 1 (Sabin) were compared by using finger pad and whole-hand protocols with three adult volunteers. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 24198101-3 1993 These isotope ratios were found to be depleted in(206)Pb compared with a mean of 1.160 +- 0.012 for tap water in contact with lead pipes and %typical ratios of 1.17-1.19 for British lead ore deposits and coal. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 8213753-6 1993 After adjustment for cigarette smoking, tap water and coffee consumption, and medical history factors by logistic regression, years of exposure to chlorinated surface water were significantly associated with risk for bladder cancer (p = 0.0007). Water 167-172 nuclear RNA export factor 1 Homo sapiens 40-43 8368217-0 1993 Tap water should not be used. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 8399703-2 1993 Many of these hot liquid burns are from contact with hot tap water, usually in the home. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 8294530-1 1993 The tap water supply in Camelford, North Cornwall and environs was contaminated by aluminium and other metals in 1988. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 8260842-3 1993 Second, experimentally measured and previously reported ratios of chloroform concentrations in air and breath to tap-water concentration are used to evaluate the model predictions. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 8260842-5 1993 This analysis indicates that the ratio of chloroform dermally absorbed in the shower relative to tap-water concentration is between 0.25 and 0.66 mg per mg/L and that the effective permeability of the skin during a 10-min. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 8335721-8 1993 With 200 ml of tap water, the recoveries for most of the examined pesticides were ca. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 8399703-7 1993 Mean tap water temperature was 64.2 degrees C at baseline and 61.2 degrees C at follow-up. Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 8399703-10 1993 There were significant decreases in tap water temperature across all groups, but the majority of households still had temperatures above 55 degrees C at the end of the study. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 8221183-0 1993 [Conservation of tap water in metallo-plastic bags: observed modifications and possible health risks]. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 18965720-9 1993 The new sample introduction system was successfully tested in both a process analysis- and a flow injection analysis mode for the determination of total inorganic carbon in Waco tap water. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 8396110-3 1993 The subjects ingested 200 ml of tap water hourly. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 8333791-4 1993 Tap water included coffee, tea, juices, and glasses of water taken directly from the tap. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 8101198-3 1993 The source of infection was contaminated tap water used for irrigation of the burns, as part of the first-aid treatment which the patients received when entering the hospital. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 8483366-3 1993 A brief tap water rinse serves to eliminate gross soil of host origin known to interfere with disinfectant efficacy. Water 12-17 nuclear RNA export factor 1 Homo sapiens 8-11 8333791-4 1993 Tap water included coffee, tea, juices, and glasses of water taken directly from the tap. Water 55-60 nuclear RNA export factor 1 Homo sapiens 0-3 8333791-10 1993 The tap water component was associated with increased risk in both age categories, and there was a clear dose-response relationship. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 8333791-11 1993 Risks associated with tap water consumption were higher among those who never smoked cigarettes. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 8442518-8 1993 Use of tap water must be carefully monitored, particularly in dressing changes and bathing of surgical patients. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 8436646-5 1993 For treatment of hyperhidrosis, tap water iontophoresis was applied using a modified technique with special electrodes. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 8312955-4 1993 The case-control study revealed an association between cholera and drinking unboiled tap water (OR = 7.2; 95% CI = 1.6-32.2), and also between cholera and limited availability of water (< 1,400 liters per week) within the household (OR = 3.6; 95% CI = 0.8-16.4). Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 8514470-3 1993 The three sources of drinking water in these localities were tap, handpump and well and the prevalence of urinary stone disease in relation with the source of drinking water was 548.3, 303.4 and 189.9/1,00,000 population, respectively. Water 30-35 nuclear RNA export factor 1 Homo sapiens 61-64 8479127-9 1993 In a second in vivo study the effect of dialysate from tap water on plasma aluminum using the predialysis purification procedure was evaluated. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 8514470-5 1993 The tap water was softest with highest prevalence. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 8212415-0 1993 Relationship between the incidence infection stones and the magnesium-calcium ratio of tap water. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 8219899-7 1993 Filtration of tap water through carbon filters markedly reduced mutagenic activity of tested water extracts, whereas ceramic filters were more efficient in depleting of DNA interstrand cross-linking contaminants. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 8212415-1 1993 In a previous study we showed that the magnesium-calcium ratio of tap water is negatively correlated with the incidence of calcium-containing urinary stones. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 8362459-3 1993 A field study found that BCG syringes, which had their rubber seals replaced once, could be used at least 150 times, and DPT syringes more than 200 times even when sterilized in tap water with a hardness of 88 mg calciumoxyde per liter. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 8212415-3 1993 The magnesium-calcium ratio of tap water was found to correlate positively with the incidence of struvite stones. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 8212415-4 1993 The tap water magnesium-calcium ratio was high in regions of basalt and sedimentary rock and was low in granite and limestone areas. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 8212415-6 1993 Thus, this study suggested that the incidence of struvite stones is related to the magnesium-calcium ratio of tap water and to the regional geology, as is the case for calcium-containing stones. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 1304976-3 1992 In order to create experimental conditions employed in a previous study, Sydney tap water (50 mL) was heated at a 10% power level in the 500 W oven. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 1482016-4 1992 The fluorine content in the tap water was always under 0.5 mg/l. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 1341197-1 1992 A clinical trial was conducted in three hospitals to determine if common tap water is suitable for use as a conductive medium in electrocardiography (ECG). Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 1293141-0 1992 Prevalence of smoke detectors and safe tap-water temperatures among welfare recipients in Memphis, Tennessee. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 1574621-1 1992 We fit lognormal distributions to data collected in a national survey for both total water intake and tap water intake by children and adults for these age groups in years: 0 less than age less than 1; 1 less than or equal to age less than 11; 11 less than or equal to age less than 20; 20 less than or equal to age less than 65; 65 less than or equal to age; and all people in the survey taken as a single group. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 1293141-2 1992 The goal of this study was to measure the prevalence of smoke detectors and safe tap-water temperatures among welfare recipients and compare subjects living in safe and unsafe homes. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 1293141-3 1992 We interviewed 109 black women residing in inner-city Memphis who were receiving Aid to Families with Dependent Children and inspected their homes for functional smoke detectors and safe tap-water temperatures. Water 191-196 nuclear RNA export factor 1 Homo sapiens 187-190 1439953-3 1992 The diagnosis was confirmed when samples of tap water that had passed through the in-line deionizer showed low to high calcium concentrations. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 8492301-3 1993 Epinephrine was oxidized rapidly in sodium chloride prepared with tap water (1.20 +/- 0.12 nmoles/min) or in deionized water (0.40 +/- 0.80 nmoles/min), but this oxidation was prevented by the addition of Desferal, a potent metal chelating agent. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 1494212-5 1992 Tap water staying overnight in the tube was considered as tube-rinsing solution. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 1464953-0 1992 [Concentration and form of asbestos fibers in tap drinking water contaminated from a water supply pipe with asbestos-cement]. Water 59-64 nuclear RNA export factor 1 Homo sapiens 46-49 1464953-4 1992 Asbestos fibers were found in the tap water from two areas in which an asbestos-cement pipe was used for public water supply. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 1464953-5 1992 The concentrations of asbestos fibers in the tap water were 2.7 x 10(4) to 27.0 x 10(4) fibers per liter of water in area A and 10.0 x 10(4) to 21.0 x 10(4) in area B. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 1464953-11 1992 Almost all asbestos fibers detected in the tap water possessed the form of thick or sheaved fibers with lengths ranging from ca. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 1464953-17 1992 It was suggested that the contamination of asbestos fibers in the tap water was caused by erosion and peeling off of the inner wall of the asbestos-cement pipe used as a conduit. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 1424511-3 1992 Copepods in the hospital tap water supply were the source for one "outbreak". Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 1356466-7 1992 RESULTS: The infection rate in wounds cleaned with sterile saline was 10.3% compared with 5.4% in wounds cleaned with tap water (p less than 0.05). Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 1624594-8 1992 Of six samples of tap water seeded with varying concentrations of Cryptosporidium oocysts, two (10(2) and 10(3) oocysts/l) were positive by both microscopy and EIA, two (10 and 1/l) by EIA alone, and two (0.1/l and unseeded water) were negative by both microscopy and EIA. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 1625612-3 1992 RESULTS: The contents of 106 aluminium cans and bottles representing 52 different beverages all had a higher aluminium content than Newcastle tap water at 1.4 mumol/L, ranging as high as 385 mumol/L. Water 146-151 nuclear RNA export factor 1 Homo sapiens 142-145 1588354-3 1992 The questionnaire responses were obtained in 1979 from the four exposed communities and compared to those of a Wyoming community whose tap water levels of arsenic were less than 0.001 mg/l in 1979. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 1549435-1 1992 Subjects presented with sets of three samples, two of distilled water and one of tap water, were significantly more consistent in choosing the tap water as preferable than they were in identifying it as the odd sample in the set. Water 64-69 nuclear RNA export factor 1 Homo sapiens 143-146 1549435-1 1992 Subjects presented with sets of three samples, two of distilled water and one of tap water, were significantly more consistent in choosing the tap water as preferable than they were in identifying it as the odd sample in the set. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 1549435-1 1992 Subjects presented with sets of three samples, two of distilled water and one of tap water, were significantly more consistent in choosing the tap water as preferable than they were in identifying it as the odd sample in the set. Water 85-90 nuclear RNA export factor 1 Homo sapiens 143-146 1549435-1 1992 Subjects presented with sets of three samples, two of distilled water and one of tap water, were significantly more consistent in choosing the tap water as preferable than they were in identifying it as the odd sample in the set. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 1549435-1 1992 Subjects presented with sets of three samples, two of distilled water and one of tap water, were significantly more consistent in choosing the tap water as preferable than they were in identifying it as the odd sample in the set. Water 85-90 nuclear RNA export factor 1 Homo sapiens 143-146 1621355-6 1992 Each container was thoroughly cleaned, and the contents vacuum filtered and washed with 1 L of tap water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 1340096-1 1992 Atypical Mycobacteria were demonstrated in tap water. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 1465560-3 1992 It was shown that while the traditional method for water treatment and disinfection reduces the number of these organisms, it fails to eliminate them completely, particularly in the case of tap water intake from shore intakes of surface waters. Water 194-199 nuclear RNA export factor 1 Homo sapiens 190-193 1820466-0 1991 If the tap water smells foul, think MTBE. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 1587101-3 1992 The solutions used were aqueous Dioralyte (1.5 S m-1) and tap water (0.04 S m-1). Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 1531647-3 1992 Initial drinking of tap water (15 degrees C) was 216 +/- 30 ml/7 min (P less than 0.05) with Hypo-air, decreased to 108 +/- 28 ml/7 min (P less than 0.05) with Hypo-H2O, and was 10-50 ml/10-30 min thereafter. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 1752300-3 1991 A case-control study demonstrated a strong statistical association between illness and the consumption of unboiled tap water from a particular source, with evidence of a dose-response relationship. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 1746727-2 1991 Undamaged lungs are removed from the body and then tracheally cannulated and lavaged with tap water more than 250 times. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 1892621-4 1991 Tap water was used commonly for rinsing suction tips while suctioning patients even with tympanic membrane perforations (45%). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 1859649-4 1991 Different fixation methods used on the CNS, rinsed or not rinsed in tap water, led us to suggest that the relatively high calcium content in the tap water in our part of the country was the cause. Water 149-154 nuclear RNA export factor 1 Homo sapiens 145-148 1958444-8 1991 with isovolumetric amounts of normal saline while insensible losses were compensated for by taking tap water orally. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 1673747-2 1991 Of 240 guests surveyed, 110 had a gastrointestinal illness that was significantly associated with the drinking of tap water from the resort"s well (relative risk = 16.1, 95% confidence interval 14.5 to 17.8) and this risk increased significantly with the number of glasses of water consumed (p less than 0.005). Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 1910750-1 1991 Experiments were performed to measure the transfer of trichloroethylene (TCE), a volatile organic compound (VOC), from tap water in showers to indoor air. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 1910750-2 1991 In these experiments, the loss of TCE from tap water in the shower is based on the difference between influent and effluent concentrations. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 2026713-0 1991 Gas chromatographic-mass spectrometric characterization of volatile organic compounds in Barcelona tap water. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 1934765-5 1991 He vomited just after he drank excessive water with his mouth directly to the tap for several minutes, and soon fell into loss of consciousness. Water 41-46 nuclear RNA export factor 1 Homo sapiens 78-81 1882231-6 1991 In the case of tap water, the observed ranges for salinity, chloride and sodium were 0.7-1.5 ppt, and 280-750 and 140-400 mg l-1, respectively. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 1882231-7 1991 The quality of tap water was assessed by comparing values with WHO guidelines. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 2000858-5 1991 When variables were examined by univariate analysis, controls deleted reports of tap water consumption (any vs. more) more often than did cases. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 2059420-1 1991 Experiments were performed to measure the transfer of trichloroethylene (TCE), a volatile organic compound (VOC), from tap water in showers to indoor air. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 2059420-2 1991 In these experiments, the loss of TCE from tap water in the shower is based on the difference between influent and effluent concentrations. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 2026713-2 1991 Volatile organic compounds (VOCs) from Barcelona tap water were isolated by closed-loop stripping analysis (CLSA) and identified and determined by gas chromatography-mass spectrometry. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 2026713-3 1991 The results showed that the Ter river gives the better quality tap water. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 2005005-6 1991 Piglets choosing among birth fluids, sow"s milk or tap water during a 5-min test spent more time with maternal odors than with water (P less than .05). Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 2022688-0 1991 Tap-water scald burns. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 2022688-2 1991 Review of admissions to a regional burn center showed that tap-water burns were an injury of pediatric, elderly, and neurologically impaired patients. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 2022688-4 1991 All those surveyed realized the potential for tap-water scald burns in their homes, and few believed that they could tolerate hot-only tap water at home for as long as 30 seconds. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 2022688-5 1991 Respondents who had previous experience with tap-water burns had not lowered the settings of their water-heater thermostats. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 1662352-6 1991 Tap water and bottled water are under strict vigilance. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 2000176-3 1991 An increase of gastric emptying was noted after alkaline bicarbonated water versus tap water with significant differences at 30" (p less than 0.05), 60" (p less than 0.01) and 120" (p less than 0.05). Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 2000176-5 1991 Alkaline bicarbonated water induced less intensive gallbladder emptying with statistical difference versus tap water at 60" and 120" from the standard meal (p less than 0.01). Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 1980681-4 1990 This implicates, for the first time, domestic tap water as the source of Acanthamoeba sp. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 1844270-1 1991 A quasi-historical cohort study method was used to collect the data of male stomach and liver cancer death from 1984 to 1988 in male residents (> or = 30 years old) of three tap-water-drinking communities at the upper, middle and lower reaches of the Huangpu River. Water 181-186 nuclear RNA export factor 1 Homo sapiens 177-180 1844271-1 1991 A quasi-historical cohort study method was used to collect the data of male stomach and liver cancer death and the data of exposure to relevant risk factors from 1984 to 1988 in male tap-water- and raw-water-drinking cohorts (> or = 30 years old) at both the upper and lower reaches of the Huangpu River. Water 187-192 nuclear RNA export factor 1 Homo sapiens 183-186 2291847-0 1990 An analytical method to determine Henry"s law constant for selected volatile organic compounds at concentrations and temperatures corresponding to tap water use. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 2287784-0 1990 Routes of chloroform exposure and body burden from showering with chlorinated tap water. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 2230333-6 1990 The increased counts in tap water, compared with canal water, were recorded in winter for bacteria and in spring for fungi. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 2287785-0 1990 Chloroform exposure and the health risk associated with multiple uses of chlorinated tap water. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 2261054-11 1990 The other half of the Pseudomonads plus the Flexibacter species were mesotrophic oligocarbotolerants, since they could grow in tap water and in culture media with very high nutrient content. Water 131-136 nuclear RNA export factor 1 Homo sapiens 127-130 2255881-4 1990 In one case we observed "jelly-like crystals" of about 2 mm diameter which dissolved spontaneously in tap water. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 2255881-6 1990 "Jelly-like crystals" developed in our laboratory when the absorbent material of the new diapers was put in contact with urine or tap water. Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 2203255-4 1990 The meal with 90 mL tap water was ingested over 10 and 30 min. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 2114483-2 1990 There are three main sources of drinking water: tap, private treated, and bottled waters. Water 41-46 nuclear RNA export factor 1 Homo sapiens 48-51 2390700-3 1990 If they find tap water unpalatable and drink bottled water instead, they could significantly increase their daily calcium intake by as much as 1.5 g. The majority of bottled waters presently available in this country, together with tap water samples from throughout the British Isles, have been analysed and the results suggest that there are some waters which stone formers should avoid. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 2395338-0 1990 Influence of storage conditions on aluminum concentrations in serum, dialysis fluid, urine, and tap water. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 2395338-6 1990 Frozen storage was superior compared with 4 degrees C, whereas storage at -80 degrees C offered no advantage compared with storage at -20 degrees C. Acidification of tap water samples was necessary to stabilize Al levels during storage. Water 170-175 nuclear RNA export factor 1 Homo sapiens 166-169 2346149-6 1990 While interventions exist for tap water scalds, solutions to the problems of "kitchen" scald and gasoline-involved flame burns are less apparent. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 2114483-3 1990 The findings revealed that tap water had highest level of all chemicals studies (except silica) compared to other waters. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 2114483-4 1990 Sodium level in tap water ranged from 100 to 545.9 mg/l, with an average of 309.4 mg/l. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 2364574-10 1990 The direct hydration of the skin is of short duration and comparable to a tap-water bath. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 2380302-5 1990 Recoveries of greater than 90% were obtained when tap water was spiked with warfarin. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 2118739-0 1990 Use of masking agents in the determination of lead in tap water by flame atomic absorption spectrometry with flow injection pre-concentration. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 2118739-5 1990 Recoveries from tap water samples, to which various amounts of lead had been added, ranged from 94 to 108%. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 2118739-6 1990 Results of analyses of tap water samples using this method were in good agreement with those obtained by electrothermal atomic absorption spectrometry. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 2321644-4 1990 Our fluids are prepared from fluoridated tap water that is purified by reverse osmosis (RO). Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 2321644-6 1990 Since many HD units rely on RO systems to purify fluoridated tap water, it is likely that many HD patients are being exposed inadvertently to increased concentrations of fluoride. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 2361823-4 1990 of 3.1 +/- 1.4 ng/ml (normal less than 0.5 ng/ml); elevated home tap-water aluminium levels of 6.5 +/- 1.2 umol/l (normal less than 2 umol/l); and a GFR of 20.5 mls/min/1.73m, (range 2-50 mls/min/1.73m). Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 2301865-6 1990 Patients with malignant external otitis had a statistically significant higher incidence of aural irrigation with tap water when compared with control subjects. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 18964929-6 1990 The gallium content found in tap water was higher than that in raw water. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 1972840-3 1990 Skin hydration was changed by soaking skin with tap water. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 2073131-11 1990 Finally, soman could be detected in different biological samples like human serum, goat serum, rabbit serum, chicken serum, milk, and tap water in concentrations between 1.3 x 10(-6) and 2.0 x 10(-6) mol/l. Water 138-143 nuclear RNA export factor 1 Homo sapiens 134-137 2081254-3 1990 A positive association between a mother"s consumption of home tap water during the first trimester of pregnancy and cardiac anomalies in her infant was unrelated to the incident of water contamination, the mother"s race, or her educational level. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 2079994-7 1990 It was found that the tap water from Kanagawa prefecture, Japan, had the highest V concentrations among the 21 cities in Japan and the US. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 33816773-8 2021 Results In vitr o , 20 mL of tap water was injected once into the forceps channel and then aspirated for 10 seconds. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 33971104-6 2022 To evaluate the possible association of skin cancer with source of tap water, we calculated odds ratios for participants with melanoma and nonmelanoma skin cancer, compared with participants with no cancer. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 33811631-4 2021 Microplastics in tap water were related to materials of transportation pipelines in drinking-water supply chain. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 33811631-4 2021 Microplastics in tap water were related to materials of transportation pipelines in drinking-water supply chain. Water 93-98 nuclear RNA export factor 1 Homo sapiens 17-20 33818445-2 2021 When electrolysis was performed for 10 minutes using a direct-current electrolytic hydrogen-water generating bottle with tap water, "residual free chlorine" concurrently upon the production of molecular hydrogen (444 mug/L) could be appreciably decreased from 0.18 mg/L to 0.12 mg/L as quantified by a N,N-diethyl-p-phenylenediamine-dye colorimetric method. Water 92-97 nuclear RNA export factor 1 Homo sapiens 121-124 33818445-2 2021 When electrolysis was performed for 10 minutes using a direct-current electrolytic hydrogen-water generating bottle with tap water, "residual free chlorine" concurrently upon the production of molecular hydrogen (444 mug/L) could be appreciably decreased from 0.18 mg/L to 0.12 mg/L as quantified by a N,N-diethyl-p-phenylenediamine-dye colorimetric method. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 33818445-7 2021 Importantly, even when half the amount of tap water was poured into the tank of the apparatus and electrolyzed, both the residual chlorine and ozone concentrations measured were also below the safety standard. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 33820314-4 2021 The attenuation coefficient of tap water is 0.08/m, which is close to Jerlov Type II seawater. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 25212173-4 2014 This behaviour could be due to the decrease in viscosity when the permeant was changed from tap water to leachate. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 33805237-5 2021 A cut-off CV mode, which was operated to maximize Ca2+ removal efficiency per cycle, was found to lead to a specific energy consumption (SEC) of 0.061 kWh/mole removed Ca2+ for partially softening industrial water and 0.077 kWh/m3 removed Ca2+ for slightly softening tap water at a water recovery of 0.5. Water 208-213 nuclear RNA export factor 1 Homo sapiens 267-270 25267146-0 2015 Tap water iontophoresis may be ineffective for axillary hyperhidrosis. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 33806644-5 2021 The samples incorporating metakaolin showed the highest compressive strength of 76.60 MPa at 90 days tap water curing and this was 17% higher than that of the control. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 33771955-1 2021 SIGNIFICANCE: This study provides insight into the current recommendations, clinical behaviors, and risk assessments of eye care professionals on the topic of rigid contact lens exposure to tap water. Water 194-199 nuclear RNA export factor 1 Homo sapiens 190-193 33771955-3 2021 PURPOSE: The purpose of this study was to investigate the practice patterns and risk perceptions of eye care professionals regarding gas-permeable contact lens exposure to tap water. Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 33771955-5 2021 The survey queried participants about their current practices, recommendations, and perceptions of risk regarding exposure of gas-permeable contact lenses to tap water. Water 162-167 nuclear RNA export factor 1 Homo sapiens 158-161 33771955-6 2021 RESULTS: Of those who prescribe gas-permeable contact lenses, 57.4% reported rinsing lenses with tap water, whereas only 32.7% reported engaging in this same behavior in front of patients. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 33771955-7 2021 Of those who reported never rinsing lenses with tap water, 85.6% indicated that rinsing lenses with water increases infection risk, whereas 52.1% of those who rinse lenses with water reported the same perceived risk (P < .001). Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 18438635-8 2008 Among the cathodic electrolyte tested, these can be listed in decreasing order of power density as aerated KMnO(4) solution > KMnO(4) solution without aeration > aerated tap water > aerated tap water with NaCl. Water 180-185 nuclear RNA export factor 1 Homo sapiens 176-179 34822902-8 2022 Target analysis of 110 PPCPs showed detection of 21, 19 and 22 compounds in the drinking water treatment plant with a concentration range of 0.11-844 ng/L in the three seasons, but only 8, 9 and 15 compounds detected in tap water (0.16-32.5 ng/L). Water 224-229 nuclear RNA export factor 1 Homo sapiens 220-223 34822902-9 2022 The variations of the detected chemicals were less obvious in tap water, with most having concentrations below 2 ng/L. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 34749143-5 2022 We compared the cleaning efficiency of TAP water, two grades of purified water, NaCl solution and SDS solution. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 34619120-9 2022 The practicality of the proposed probe was evaluated by quantifying cyanide in tap water and soils and monitoring the liberation of hydrogen cyanide from cyanogenic glycoside-containing foods. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 34883127-8 2022 Moreover, by the established method, trace estrogenic activity (14.7-24.2 pg E2 equivalents (E2Eq)/L) can be detected in a portion of "clean" drinking water (Tap water) samples. Water 151-156 nuclear RNA export factor 1 Homo sapiens 158-161 34883127-8 2022 Moreover, by the established method, trace estrogenic activity (14.7-24.2 pg E2 equivalents (E2Eq)/L) can be detected in a portion of "clean" drinking water (Tap water) samples. Water 162-167 nuclear RNA export factor 1 Homo sapiens 158-161 34749143-6 2022 FINDINGS: The QCM-D results show that both grades of purified water remove more than 90% of Vaseline deposited of the surface while tap water only 75%. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 34800573-6 2022 Our main explanatory variable was the tap water lithium level (Li) from public drinking water supply systems using their own water source (n = 1 325). Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 34800573-6 2022 Our main explanatory variable was the tap water lithium level (Li) from public drinking water supply systems using their own water source (n = 1 325). Water 88-93 nuclear RNA export factor 1 Homo sapiens 38-41 34800573-6 2022 Our main explanatory variable was the tap water lithium level (Li) from public drinking water supply systems using their own water source (n = 1 325). Water 125-130 nuclear RNA export factor 1 Homo sapiens 38-41 34562756-5 2022 Total PFAS concentrations up to 242 ng L-1 (average of 168 ng L-1) were found in tap water from Grapeland Heights, which is the closest location to the Miami international airport that was sampled. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 34562756-7 2022 In general, average total PFAS was higher in tap water (86.3 ng L-1) than in surface waters (46.3 ng L-1), whereas the most predominant and frequently detected PFAS were PFBA, PFBS, PFPeA, PFHxA, PFHxS, PFOA and PFOS. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 34818775-3 2022 OBJECTIVES: We aimed to: 1) measure VOCs in residential indoor air and tap water from EXPERIVA participants; 2) compare concentrations with those in the general population and explore differences related to sociodemographic and housing characteristics; and 3) determine associations between VOC concentrations and density/proximity to UNG wells. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 34818775-7 2022 We assessed the association between different metrics of well density/proximity and indoor air and tap water VOC concentrations using multiple linear regression. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 34818775-10 2022 Indoor air levels of chloroform and tap water levels of total trihalomethanes were higher in Indigenous participants compared to non-Indigenous participants. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 34818775-11 2022 Indoor air levels of chloroform and acetone, and tap water levels of total trihalomethanes were positively associated with UNG wells density/proximity metrics. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 34871940-4 2022 Finally, the developed method was successfully used for determining dimethyl methylphosphonate in beverages such as coffee mix, fruit juice, tap water, milk, and tea. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 34759078-7 2022 Changes in the pH by mouth rinsing with AEW and purified tap water (PTW) were analyzed. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 34525701-6 2022 By combining water chemistry data from public reports, socioeconomic information from the US census, and spatial features using Geographic Information Systems, we trained and tested models to estimate the likelihood of lead contaminated tap water in over 8,000 schools across California and Massachusetts. Water 13-18 nuclear RNA export factor 1 Homo sapiens 237-240 34525701-6 2022 By combining water chemistry data from public reports, socioeconomic information from the US census, and spatial features using Geographic Information Systems, we trained and tested models to estimate the likelihood of lead contaminated tap water in over 8,000 schools across California and Massachusetts. Water 241-246 nuclear RNA export factor 1 Homo sapiens 237-240 34728202-0 2022 Spatial distributions of strontium isotope ratios in human hair and tap water from South Korea. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 34728202-3 2022 In this national-scale study conducted across South Korea, we investigated the spatial distribution patterns of 87Sr/86Sr ratios in human hair and tap water samples to determine their spatial variabilities and the relationships of isotopic signatures between hair and tap water. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 34728202-3 2022 In this national-scale study conducted across South Korea, we investigated the spatial distribution patterns of 87Sr/86Sr ratios in human hair and tap water samples to determine their spatial variabilities and the relationships of isotopic signatures between hair and tap water. Water 272-277 nuclear RNA export factor 1 Homo sapiens 268-271 34728202-4 2022 The strontium isoscapes of tap water and hair showed similar spatial distribution patterns. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 34728202-6 2022 The 87Sr/86Sr ratios in human hair showed a significant and strong correlation with the ratios in tap water in eastern Korea, suggesting potential use of 87Sr/86Sr ratios in provenance studies. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 34728202-7 2022 However, tap water and hair samples from western Korea did not show significant correlation between them, overall reducing the predictive power of the hair 87Sr/86Sr ratios for provenance studies. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 34500280-7 2022 Furthermore, the DWTP and DWDS both prevented MPs from entering the tap water, thereby reducing their risk. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 34370193-11 2022 This study enriches environmental monitoring data of pharmaceuticals in drinking water sources and tap water, and provides scientific information for emerging pollutants management in drinking water system. Water 193-198 nuclear RNA export factor 1 Homo sapiens 99-102 34467478-7 2022 Bentazone was frequently detected (detection frequency: 96.3%) in 160 tap water samples (underwent conventional treatment) (median: 1.95 ng/L, range: <0.02-47.0 ng/L), while it was not detectable in tap water samples that underwent ozone combined with activated carbon. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 34467478-10 2022 The estimated daily intake of bentazone based on its median concentration in tap water (0.04 ng/kg-body weight (bw)/day) accounted for approximately 8% of that based on the median urinary concentration (0.48 ng/kg-bw/day). Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 34894436-0 2022 Porous electrospun microfibers for low flow-resistant solid phase extraction of fluoroquinolones in tap water, egg and milk samples. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 34894436-6 2022 Using the PEMF-SPE cartridges with ultra-performance liquid chromatography-fluorescence detector (UPLC-FLD), five fluoroquinolones (FQs) in tap water, egg and milk samples were extracted and quantified successfully. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 34894436-10 2022 The reliability of the developed method was validated by analyzing tap water, egg and milk samples, and the recovery values were found to be in the range of 74.8-116.6% under the optimized conditions. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 34370193-0 2022 Pharmaceuticals in drinking water sources and tap water in a city in the middle reaches of the Yangtze River: occurrence, spatiotemporal distribution, and risk assessment. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 34370193-4 2022 Only SMX and IBF were detected quantitatively with the highest concentrations of 0.69 ng/L and 1.28 ng/L in tap water, respectively. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 34370193-7 2022 The overall discrepancy of concentrations between drinking water sources and tap water might indicate the purification effect of drinking water treatment system. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 34370193-7 2022 The overall discrepancy of concentrations between drinking water sources and tap water might indicate the purification effect of drinking water treatment system. Water 138-143 nuclear RNA export factor 1 Homo sapiens 77-80 34370193-11 2022 This study enriches environmental monitoring data of pharmaceuticals in drinking water sources and tap water, and provides scientific information for emerging pollutants management in drinking water system. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 34627965-0 2022 Seasonal distribution of antibiotic resistance genes in the Yellow River water and tap water, and their potential transmission from water to human. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 34627965-0 2022 Seasonal distribution of antibiotic resistance genes in the Yellow River water and tap water, and their potential transmission from water to human. Water 132-137 nuclear RNA export factor 1 Homo sapiens 83-86 34627965-3 2022 Here, we employed 16S rRNA gene sequencing and high-throughput quantitative PCR techniques to explore the seasonal distribution of ARGs and opportunistic pathogens in the Yellow River water (source water) and tap water, as well as their relationships with healthy humans at Lanzhou, China. Water 213-218 nuclear RNA export factor 1 Homo sapiens 209-212 34627965-5 2022 The absolute abundance and diversity of ARGs in the Yellow River and tap water demonstrated distinct seasonal patterns. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 34627965-6 2022 In winter, the Yellow river water had the highest ARG abundance and diversity, while tap water owned the lowest. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 34627965-7 2022 Mobile genetic elements (MGEs) were the predominant driver of ARG profiles in both the Yellow river and tap water. Water 108-113 nuclear RNA export factor 1 Homo sapiens 104-107 34627965-8 2022 Null model analysis showed that ARG assembly in the Yellow River was more influenced by stochastic processes than tap water and this was independent of seasons. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 34627965-13 2022 Thus, it is crucial to protect sources of tap water from anthropogenic pollution and improve water treatment technologies to reduce the dissemination of ARGs and ensure drinking-water biosafety for human health. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 34396474-1 2022 Approximately 99.1% of South Koreans have access to drinkable tap water from river basins. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 34350580-3 2022 Tap water, ethanol solutions, and sodium chloride at different concentrations were used as densification medium. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 34396474-2 2022 Due to such a high access rate, the South Korean government has been running, since 2013, a long-term program for monitoring the quality of tap water for drinking. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 34396474-10 2022 Considering the potency of N-nitrosamines in tap water for drinking, the levels of these substances in the finished water of DWTPs in South Korea should be continuously monitored. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 34961483-14 2021 Sembule village had a token-operated water tap, which had broken down 1 month before the outbreak, forcing residents to obtain water from one of three wells (Wells A, B, C) or a public tap. Water 37-42 nuclear RNA export factor 1 Homo sapiens 43-46 34851473-8 2022 The method has been applied to honey and tap water samples and the recoveries were found to be in the range of 91.3 and 101.1 %. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 34961483-14 2021 Sembule village had a token-operated water tap, which had broken down 1 month before the outbreak, forcing residents to obtain water from one of three wells (Wells A, B, C) or a public tap. Water 37-42 nuclear RNA export factor 1 Homo sapiens 185-188 34961483-14 2021 Sembule village had a token-operated water tap, which had broken down 1 month before the outbreak, forcing residents to obtain water from one of three wells (Wells A, B, C) or a public tap. Water 127-132 nuclear RNA export factor 1 Homo sapiens 43-46 34961483-16 2021 Drinking water from a public tap (ORM-H = 0.07, 95% CI 0.014-0.304) was protective. Water 9-14 nuclear RNA export factor 1 Homo sapiens 29-32 34949441-0 2022 Work site access to fluoridated tap water and retail beverages: An assessment of the University of California, San Francisco campuses. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 34839790-2 2021 Synthetic stormwater was created by adding metal salts, oil and collected stormwater sediment to tap water. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 34467936-8 2021 The health risk assessment implied that estimated daily intake of these fungicides through tap water ingestion might pose a low risk to consumers, though risk associated with infant exposure to the fungicides requires further attention. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 34467936-9 2021 This study provides baseline data on the occurrence, removal efficiencies, and seasonal variations of the selected fungicides in tap water from central China. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 34949441-2 2022 The purpose of this study was to assess the availability, appeal, and promotion of fluoridated tap water in publicly accessible spaces compared with retail beverages at the University of California, San Francisco. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 34534832-8 2021 Although the estimated daily intake of NEOs were much lower than the reference dose, the potential health risk of NEOs via tap water consumption should raise more public concern considering the high detection rates of NEOs in tap water. Water 230-235 nuclear RNA export factor 1 Homo sapiens 123-126 34190981-5 2021 Results of water analysis indicated that fluoride content in tap water ranged from 0.267 to 0.336 mg/L (average 0.304 mg/L), and the levels of fluoride in purified water and bottled water were 0.068-0.317 mg/L (average 0.134 mg/L) and 0-0.120 mg/L (average 0.080 mg/L), respectively. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 34190981-7 2021 The low fluoride exposure for the population in the studied area was observed, and the replacement of tap water with purified and bottled water could further aggravate the deficient of fluoride intake for local residents. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 34534832-0 2021 A pilot nationwide baseline survey on the concentrations of Neonicotinoid insecticides in tap water from China: Implication for human exposure. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 34534832-2 2021 However, information on the NEO concentrations in tap water based on nationwide surveys is limited in China. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 34534832-3 2021 In this study, the levels of six NEOs were measured in tap water samples collected from 38 cities in China. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 34534832-4 2021 Across all sampling locations, the overall frequency of detection for at least one NEO was 100%, indicating that NEOs are ubiquitous in tap water from China. Water 140-145 nuclear RNA export factor 1 Homo sapiens 136-139 34534832-6 2021 Significantly positive correlations (r = 0.655-0.902, p < 0.001) among all pairs of NEOs were observed, which showed that the sources of NEOs in tap water were common or related. Water 149-154 nuclear RNA export factor 1 Homo sapiens 145-148 34534832-8 2021 Although the estimated daily intake of NEOs were much lower than the reference dose, the potential health risk of NEOs via tap water consumption should raise more public concern considering the high detection rates of NEOs in tap water. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 34534832-8 2021 Although the estimated daily intake of NEOs were much lower than the reference dose, the potential health risk of NEOs via tap water consumption should raise more public concern considering the high detection rates of NEOs in tap water. Water 127-132 nuclear RNA export factor 1 Homo sapiens 226-229 34862401-0 2021 Reducing the nanoparticles generated at the wheel-rail contact by applying tap water lubricant at subway train operational velocities. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 34862401-1 2021 The formation characteristics and the reduction of nanoparticles emitted from wheel-rail contacts at subway-train velocities of 73, 90, and 113 km/h under dry and water-lubricated conditions (using tap water) were studied using a twin-disk rig. Water 202-207 nuclear RNA export factor 1 Homo sapiens 198-201 34862401-6 2021 Adding water increased the NC of particles <= 35 nm in diameter, possibly owing to the increase in water vapor and mineral crystals from tap water. Water 7-12 nuclear RNA export factor 1 Homo sapiens 137-140 34862401-6 2021 Adding water increased the NC of particles <= 35 nm in diameter, possibly owing to the increase in water vapor and mineral crystals from tap water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 137-140 34862401-6 2021 Adding water increased the NC of particles <= 35 nm in diameter, possibly owing to the increase in water vapor and mineral crystals from tap water. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 34534832-8 2021 Although the estimated daily intake of NEOs were much lower than the reference dose, the potential health risk of NEOs via tap water consumption should raise more public concern considering the high detection rates of NEOs in tap water. Water 230-235 nuclear RNA export factor 1 Homo sapiens 226-229 34411946-5 2021 RESULTS: Participants without tap water were more likely to have depressive symptoms than participants with tap water (odds ratio (OR): 1.30; 95% confidence interval (CI): 1.19-1.42) (hazard ratio (HR): 1.18; 95% CI: 1.09-1.28). Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 34874901-0 2021 Assessment of radiation dose hazards caused by radon and its progenies in tap water by the human dosimetric model. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 34874901-2 2021 In this study, the radon concentration in the tap water of residential buildings was measured, and the average value was 543.33 mBq L-1, which was in line with the radon concentration limit recommended by USEPA (11.11 Bq L-1) and EURATOM (100 Bq L-1), and also within the range of the results of radon concentration measurements in tap water in other countries or regions. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 34874903-4 2021 We evaluated consumer perceptions of tap water using weekly social media data. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 34874907-0 2021 Demographic differences in use of household tap water in a representative sample of US adults, FallStyles 2019. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 34874907-1 2021 Tap water that is safe to consume may cause respiratory illness (e.g., Legionnaires" disease) when water conditions allow for proliferation and aerosolization of biofilm-associated pathogens. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 34874907-2 2021 This study assessed household tap water consumption, exposure to aerosolized tap water, and associated demographics. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 34874907-2 2021 This study assessed household tap water consumption, exposure to aerosolized tap water, and associated demographics. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 34874907-5 2021 Respondents were asked about self-reported use of household tap water for consumption (i.e., drinking, rinsing produce, or making ice) and use through water-aerosolizing devices (e.g., showerheads, humidifiers). Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 34874907-7 2021 Weighted analyses using complex sample survey procedures were used to assess tap water exposure by route and demographics. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 34874907-8 2021 Most US adults are exposed to aerosolized tap water through showering (80.6%), and one in five are exposed through other water-aerosolizing devices (20.3%). Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 34874907-10 2021 Aerosolized tap water can transmit waterborne pathogens and cause respiratory illness, especially among older age groups and people with weakened immune systems. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 34411946-6 2021 The lack of access to tap water in residence was positively related to the prevalence and incidence of symptoms of depression in almost all subgroups. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 34411946-7 2021 Changing the water source from non-tap to tap water decreased the risk of depressive symptoms (HR: 0.69; 95% CI: 0.60 - 0.79). Water 13-18 nuclear RNA export factor 1 Homo sapiens 35-38 34411946-7 2021 Changing the water source from non-tap to tap water decreased the risk of depressive symptoms (HR: 0.69; 95% CI: 0.60 - 0.79). Water 13-18 nuclear RNA export factor 1 Homo sapiens 42-45 34411946-7 2021 Changing the water source from non-tap to tap water decreased the risk of depressive symptoms (HR: 0.69; 95% CI: 0.60 - 0.79). Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 34411946-10 2021 Therefore, providing tap water in residence may help prevent depression. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 34468057-9 2021 When participants consumed 500mL of tap water, the enrichment of saliva specimens reached a new plateau value faster than urine. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 34789317-3 2021 However, it takes time to dissolve CO2 in tap water and because the dissolved CO2 concentration decreases over time, the actual CO2 concentration is likely lower than the stated target concentration. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 34789317-6 2021 Participants were first immersed for 15 min in a tap water bath at 40 C to raise body temperature. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 34789317-10 2021 RESULTS: Immersion in 40 C tap water caused Tac to rise 0.64 +- 0.25 C in the tap water session and 0.62 +- 0.27 C in the CO2-enriched water session (P > 0.05). Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 34385133-3 2021 The total mean concentrations of BSHs were 53.32 mug m-3, 36.29 mug m-3, and 26.88 mug L-1 in indoor air, ambient air, and tap water, respectively. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 34303235-0 2021 Hazardous inorganic disinfection by-products in Egypt"s tap drinking water: Occurrence and human health risks assessment studies. Water 69-74 nuclear RNA export factor 1 Homo sapiens 56-59 34303235-1 2021 This study is the first that monitored the presence and levels of chlorite, chlorate and bromate in tap drinking water of Egypt. Water 113-118 nuclear RNA export factor 1 Homo sapiens 100-103 34303235-9 2021 This study manifested the importance of routine monitoring, and implementing counter measures to control the levels of the hazardous inorganic DBPs in tap drinking water. Water 164-169 nuclear RNA export factor 1 Homo sapiens 151-154 34247071-3 2021 We estimated the health and environmental impacts of four drinking water scenarios for the Barcelona population: 1) currently observed drinking water sources; a complete shift to 2) tap water; 3) bottled water; or 4) filtered tap water. Water 186-191 nuclear RNA export factor 1 Homo sapiens 182-185 34247071-3 2021 We estimated the health and environmental impacts of four drinking water scenarios for the Barcelona population: 1) currently observed drinking water sources; a complete shift to 2) tap water; 3) bottled water; or 4) filtered tap water. Water 230-235 nuclear RNA export factor 1 Homo sapiens 226-229 34247071-6 2021 The scenario where the entire population consumed tap water yielded the lowest environmental impact on ecosystems and resources, while the scenario where the entire population drank bottled water yielded the highest impacts (1400 and 3500 times higher for species lost and resource use, respectively). Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 34247071-7 2021 Meeting drinking water needs using bottled or filtered tap water led to the lowest bladder cancer DALYs (respectively, 140 and 9 times lower than using tap water) in the Barcelona population. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 34247071-7 2021 Meeting drinking water needs using bottled or filtered tap water led to the lowest bladder cancer DALYs (respectively, 140 and 9 times lower than using tap water) in the Barcelona population. Water 156-161 nuclear RNA export factor 1 Homo sapiens 152-155 34785232-7 2022 Combinedly, our work reveals that metformin byproducts have been disseminated to urban water cycle and contaminated tap water, increasing potential toxic risk for drinking water. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 34785232-7 2022 Combinedly, our work reveals that metformin byproducts have been disseminated to urban water cycle and contaminated tap water, increasing potential toxic risk for drinking water. Water 172-177 nuclear RNA export factor 1 Homo sapiens 116-119 34694793-6 2021 The detection limits in deionized water and tap water were determined to be 1.07 and 0.75 ppb, respectively, which are lower than the US Environmental Protection Agency standard of the maximum contamination of uranium in drinking water. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 34694793-6 2021 The detection limits in deionized water and tap water were determined to be 1.07 and 0.75 ppb, respectively, which are lower than the US Environmental Protection Agency standard of the maximum contamination of uranium in drinking water. Water 230-235 nuclear RNA export factor 1 Homo sapiens 44-47 34470147-2 2021 As bulk water travels from source to tap, it may accumulate contaminants of emerging concern (CECs) such as antibiotics and heavy metals. Water 8-13 nuclear RNA export factor 1 Homo sapiens 37-40 34284015-2 2021 In this study, the leaching of PTEs including both heavy metals and metalloids (metal(loid)s) from CBs into deionized water (DW), tap water (TW), and seawater (SW) was checked during the different contact times (from 60 min to 60 days). Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 34850710-2 2021 In this regard, the goal of this research was to evaluate the overall physicochemical, phycological, and bacteriological properties of tap water samples taken periodically from 12 different Tanta city schools. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 34949329-6 2021 When spiked concentration was 1.0 mug/L for pure water and tap water, the recoveries were 81%-106% and 75%-117%, respectively, and relative standard deviations were both less than 4%. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 34949329-7 2021 When spiked concentration was 12 mug/L for pure water and tap water, the recoveries were 92%-101% and 86%-106%, respectively, and relative standard deviations were less than 4% and 2%, respectively. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 34714870-0 2021 Assessing tap water awareness: The development of an empirically-based framework. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 34714870-3 2021 To address this gap, we conceptualise, operationalise and assess tap water awareness, hereby differentiating between cognitive awareness (head), affectional awareness (heart), and behavioural awareness (hands). Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 34714870-4 2021 In parallel, we also differentiate between tap water quality, quantity and system. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 34714870-7 2021 Based on the analysis of the results of the first empirical application of our tap water awareness assessment framework, we conclude that-with a score 53.5 points out of 100-tap water awareness in the Netherlands shows ample room for improvement. Water 178-183 nuclear RNA export factor 1 Homo sapiens 174-177 34614460-4 2021 The heterotrophic plate counts with R2A media were high (> 100 CFU/mL) in some SWSS tank and tap water samples. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 34460232-6 2021 It subsequently was applied for the analysis of multi-SEs from three real samples in the environment including medical wastewater, river water, and tap water to provide a means to clarify the fate of multi-SEs in the process of migration and transformation. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 34669129-3 2022 Under the reclaimed water irrigation, the content of soil total salinity, chloride ions, and water soluble sodium in soil of most plants was averagely 160.3%, 83.3%, and 67.5% higher than that of tap water, respectively. Water 20-25 nuclear RNA export factor 1 Homo sapiens 196-199 34669129-3 2022 Under the reclaimed water irrigation, the content of soil total salinity, chloride ions, and water soluble sodium in soil of most plants was averagely 160.3%, 83.3%, and 67.5% higher than that of tap water, respectively. Water 200-205 nuclear RNA export factor 1 Homo sapiens 196-199 34669129-6 2022 Compared with the tap water irrigation, the content of alkaline nitrogen in 5 plants increased (averagely 25.8%) after 5-year irrigation with reclaimed water. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 34614460-5 2021 Propidium monoazide (PMA)-qPCR revealed a one magnitude higher abundance of viable bacteria in the tank and tap water samples (average 103.63+-1.10 and 103.65+-1.25 gene copies/mL, respectively) compared with the input water samples, and Enterococcus, Acanthamoeba, and Hartmannella vermiformis were only detected in the tanks. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 34614460-6 2021 In particular, the high detection frequency of Legionella in 35% tank and 21% tap water samples suggested it is a supplementary microbial safety indicator in SWSSs. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 34166938-4 2021 Therefore, our study aimed to examine whether the low level of fluoride exposure (measured in blood plasma and household tap water) was associated with the risk of dental fluorosis based on data of the National Health and Nutrition Examination Survey (NHANES) 2015-2016. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 34582491-1 2021 This study, based in San Bernardino County, Southern California, collected and examined tap water samples within the area to explore the feasibility of adopting non-industrial equipment and methods to reduce water hardness and total dissolved solids(TDS). Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 34582491-7 2021 When added to room temperature tap water, there is a continuous increase in TDS of 24.8% at the 30 mg/L mark. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 34582491-11 2021 The reduction of these solids will help lower water hardness and improve the taste of tap water. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 34582491-12 2021 These results will help direct residents to drink more tap water rather than bottled water with similar taste and health benefits for a cheaper price as well as a reduction on plastic usage. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 34682361-1 2021 The perceived safety of tap water is an important condition for consumers to drink it. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 34403678-5 2021 The emerged V2O5@Ch/Cu-TMA is regarded as an excellent nanobiosorbent for removal of inorganic contaminant as Cr(VI) from all natural water samples (tap, sea and wastewater) with percentages range 92.43%-96.95% and organic contaminant as LEVO drug from tap and wastewater (91.99%-97.20%). Water 134-139 nuclear RNA export factor 1 Homo sapiens 149-152 34375032-6 2021 Finally, the optimized method was applied for determining trace levels of carbazole and 11 polyhalogenated carbazoles in tap water and seawater samples with good recovery of 86.6-112.8%. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 34375032-7 2021 Carbazole and 3-7 polyhalogenated carbazoles were detected, and 3,6-dichlorocarbazole was the predominant congener both in tap water and seawater. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 34213495-4 2021 The participants drank 500 mL of purified tap water or AEW every day for 2 weeks. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 34410982-1 2021 BACKGROUND/AIM: To develop and validate an easy-to-use and cheap method capable of producing placebo from tap water for medicinal water efficacy trials. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 34371231-7 2021 The results showed that the BGPICC ratio between Tap-water/RO-water was ~7.5, whereas the BGPATP ratio was only ~4.5. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 34371231-7 2021 The results showed that the BGPICC ratio between Tap-water/RO-water was ~7.5, whereas the BGPATP ratio was only ~4.5. Water 62-67 nuclear RNA export factor 1 Homo sapiens 49-52 34371231-8 2021 Moreover, the YICC ratio between Tap-water/RO-water was ~2 (9.8 +- 0.6 x 106 vs. 4.6 +- 0.8 x 106 cells/microg-C), whereas the YATP ratio was ~1 (0.39 +- 0.12 vs. 0.42 +- 0.06 ng ATP/microg-C), resulting in a consistently higher ATP per cell in RO-water than that of Tap-water. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 34371231-8 2021 Moreover, the YICC ratio between Tap-water/RO-water was ~2 (9.8 +- 0.6 x 106 vs. 4.6 +- 0.8 x 106 cells/microg-C), whereas the YATP ratio was ~1 (0.39 +- 0.12 vs. 0.42 +- 0.06 ng ATP/microg-C), resulting in a consistently higher ATP per cell in RO-water than that of Tap-water. Water 248-253 nuclear RNA export factor 1 Homo sapiens 33-36 34371231-8 2021 Moreover, the YICC ratio between Tap-water/RO-water was ~2 (9.8 +- 0.6 x 106 vs. 4.6 +- 0.8 x 106 cells/microg-C), whereas the YATP ratio was ~1 (0.39 +- 0.12 vs. 0.42 +- 0.06 ng ATP/microg-C), resulting in a consistently higher ATP per cell in RO-water than that of Tap-water. Water 271-276 nuclear RNA export factor 1 Homo sapiens 267-270 34760235-2 2021 The comparative effects of acidic electrolyzed water (ACEW) and tap water (TW) on the triglyceride configuration, typical lipid concomitants, and antioxidant properties of flaxseed were conducted during 0-5 days of germination. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 34120199-4 2021 The prevalence in open well and tap water was recorded 33% and 20%, respectively. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 34087188-4 2021 Available historical residential tap water concentrations of THMs and nitrate, available from 3 countries for 86 cases and 352 controls and 85 cases and 343 for nitrate, respectively, were modelled and combined with the study subjects" personal consumption patterns to estimate ingestion and residential exposure levels in the study population (both pre- and postnatal). Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 34087188-9 2021 For nitrate, all ORs were above 1 (OR = 1.80 (0.91-3.55)) for postnatal average residential nitrate levels higher than 8.5 mg/L, with a suggestion of a trend of increased risk of neuroepithelial BTs with increasing residential nitrate levels in tap water, which appeared stronger in early in life. Water 249-254 nuclear RNA export factor 1 Homo sapiens 245-248 34410982-1 2021 BACKGROUND/AIM: To develop and validate an easy-to-use and cheap method capable of producing placebo from tap water for medicinal water efficacy trials. Water 130-135 nuclear RNA export factor 1 Homo sapiens 106-109 34410982-4 2021 Patients were asked four times during the bath to tell if they were treated with medicinal water, tap water, or could not decide. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 34410982-10 2021 CONCLUSION: The used method is appropriate for producing a validated placebo from tap water. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 34433206-12 2021 Significant association was found between disinfecting with tap water (5.98; 95% confidence interval (CI), 1.22 to 29.27; P = .03), heavy visual display terminal use (3.39; 95% CI, 1.01 to 11.34; P = .05), high water content (1.16; 95% CI, 1.02 to 1.33; P = .03), and contact lens discomfort. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 34072656-4 2021 Tap water supplemented with nutrients was fed to the two modules to enhance biofilm formation. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 34895791-0 2021 "The home, the bathroom, the taps, and hot water": The contextual characteristics of tap water scalds in Australia and New Zealand. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 34895791-1 2021 INTRODUCTION: Scalds from hot tap water can have devastating consequences and lifelong impact on survivors. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 34895791-2 2021 The aims of this study were to (i) describe the frequency, demographic profile, injury event characteristics, and in-hospital outcomes for people with tap water scalds admitted to Australian and New Zealand burn centres; and (ii) determine whether variation was present in the frequency and epidemiological characteristics of tap water scalds between jurisdictions. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 34895791-2 2021 The aims of this study were to (i) describe the frequency, demographic profile, injury event characteristics, and in-hospital outcomes for people with tap water scalds admitted to Australian and New Zealand burn centres; and (ii) determine whether variation was present in the frequency and epidemiological characteristics of tap water scalds between jurisdictions. Water 330-335 nuclear RNA export factor 1 Homo sapiens 326-329 34895791-3 2021 METHODS: Data were extracted from the Burns Registry of Australia and New Zealand for people with tap water scalds admitted to Australian or New Zealand burn centres between January 1, 2010 and December 31, 2018. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 34895791-5 2021 RESULTS: We included 650 people with tap water scalds admitted to Australian and New Zealand burn centres during the study period. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 34895791-6 2021 Australians with tap water scalds (median (IQR) 29 (1-69) years) were older than New Zealanders (2 (1-36) years). Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 34895791-7 2021 Most tap water scalds occurred in the home, and 92% of these occurred in the bathroom. Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 34895791-8 2021 More than 55% of injuries occurred due to the accidental alteration of water temperature at the tap fixture. Water 71-76 nuclear RNA export factor 1 Homo sapiens 96-99 34895791-11 2021 CONCLUSION: Tap water scalds remain a public health problem in Australia and New Zealand. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 34895791-12 2021 Our research highlights where gaps in current heated water regulations in residential homes perpetuate risks of tap water scalds, particularly in high-risk groups at the extremes of age. Water 53-58 nuclear RNA export factor 1 Homo sapiens 112-115 34895791-12 2021 Our research highlights where gaps in current heated water regulations in residential homes perpetuate risks of tap water scalds, particularly in high-risk groups at the extremes of age. Water 116-121 nuclear RNA export factor 1 Homo sapiens 112-115 34246959-0 2021 Sample preparation optimization by central composite design for multi class determination of 172 emerging contaminants in wastewaters and tap water using liquid chromatography high-resolution mass spectrometry. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 34246959-2 2021 To this end, a comprehensive workflow for the quantitative analysis of 172 anthropogenic organic compounds belonging to emerging contaminants (pharmaceuticals and personal care products, illicit drugs, organophosphate flame retardants and perfluoroalkyl substances) has been developed for application to wastewater and tap water, based on solid phase extraction (SPE) and Orbitrap high resolution mass spectrometry (HRMS). Water 323-328 nuclear RNA export factor 1 Homo sapiens 319-322 34188143-1 2021 We conducted a comprehensive overall tap water hardness assessment for Japan. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 34188143-2 2021 Tap water was collected from 665 points throughout Japan, and its standing position was quantitatively clarified by prefecture. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 34188143-3 2021 The mean and median hardness of tap water in Japan was 48.9 +- 25.8 (1sigma SD) and 46.0 mg/L, respectively. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 34188143-6 2021 The impact of the distribution system"s water pipes on tap water hardness is discussed using a unified index to evaluate variations in hardness from raw to tap water. Water 40-45 nuclear RNA export factor 1 Homo sapiens 55-58 34188143-6 2021 The impact of the distribution system"s water pipes on tap water hardness is discussed using a unified index to evaluate variations in hardness from raw to tap water. Water 160-165 nuclear RNA export factor 1 Homo sapiens 55-58 34188143-6 2021 The impact of the distribution system"s water pipes on tap water hardness is discussed using a unified index to evaluate variations in hardness from raw to tap water. Water 160-165 nuclear RNA export factor 1 Homo sapiens 156-159 34188143-7 2021 A comparison of the variations in hardness showed that hardness variations from raw to purified water and from purified to tap water exhibited a 20% variation range. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 34188143-8 2021 Furthermore, tap water hardness and its fluctuations in any region of Japan were found to be caused by raw water hardness. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 34114536-0 2022 Examining Recent Trends in the Racial Disparity Gap in Tap Water Consumption: NHANES 2011-2018. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 34114536-1 2022 OBJECTIVE: As tap water distrust has grown in the US with greater levels among Black and Hispanic households, we aimed to examine recent trends in not drinking tap water including the period covering the US Flint Water Crisis and racial/ethnic disparities in these trends. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 34114536-1 2022 OBJECTIVE: As tap water distrust has grown in the US with greater levels among Black and Hispanic households, we aimed to examine recent trends in not drinking tap water including the period covering the US Flint Water Crisis and racial/ethnic disparities in these trends. Water 18-23 nuclear RNA export factor 1 Homo sapiens 160-163 34114536-1 2022 OBJECTIVE: As tap water distrust has grown in the US with greater levels among Black and Hispanic households, we aimed to examine recent trends in not drinking tap water including the period covering the US Flint Water Crisis and racial/ethnic disparities in these trends. Water 164-169 nuclear RNA export factor 1 Homo sapiens 14-17 34114536-1 2022 OBJECTIVE: As tap water distrust has grown in the US with greater levels among Black and Hispanic households, we aimed to examine recent trends in not drinking tap water including the period covering the US Flint Water Crisis and racial/ethnic disparities in these trends. Water 164-169 nuclear RNA export factor 1 Homo sapiens 160-163 34114536-6 2022 RESULTS: Among US children and adults, respectively, in 2017-2018 there was a 63% (adjusted prevalence ratio (PR):1.63, 95%CI: 1.25-2.12, p<0.001) and 40% (PR:1.40, 95%CI: 1.16-1.69, p=0.001) higher prevalence of not drinking tap water compared to 2013-2014 (pre-Flint Water Crisis). Water 230-235 nuclear RNA export factor 1 Homo sapiens 226-229 34114536-7 2022 For Black children and adults, the probability of not drinking tap water increased significantly from 18.1% (95%CI: 13.4-22.8) and 24.6% (95%CI: 20.7-28.4) in 2013-14 to 29.3% (95%CI: 23.5-35.1) and 34.5% (95%CI: 29.4-39.6) in 2017-2018. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 34114536-8 2022 Among Hispanic children and adults, not drinking tap water increased significantly from 24.5% (95%CI: 19.4-29.6) and 27.1% (95%CI: 23.0-31.2) in 2013-14 to 39.7% (95%CI: 32.7-46.8) and 38.1% (95%CI: 33.0-43.1) in 2017-2018. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 34114536-11 2022 CONCLUSIONS: This study found persistent disparities in the tap water consumption gap from 2011-2018. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 34194514-5 2021 Results: Physicochemical qualities of the water samples from tap water sources were found to be pH (6.88 +- 0.05), turbidity (5.15 +- 0.006 NTU), electrical conductivity (170.6 +- 0.1 muS/cm), residual chlorine (0.19 +- 0.003 mg/L), and fluoride (1.17 +- 0.009 mg/L). Water 42-47 nuclear RNA export factor 1 Homo sapiens 61-64 34194514-5 2021 Results: Physicochemical qualities of the water samples from tap water sources were found to be pH (6.88 +- 0.05), turbidity (5.15 +- 0.006 NTU), electrical conductivity (170.6 +- 0.1 muS/cm), residual chlorine (0.19 +- 0.003 mg/L), and fluoride (1.17 +- 0.009 mg/L). Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 34194514-7 2021 Removal efficiency of the treatment plant for total coliforms up to 91.6% (15 +- 0.26 CFU/100 mL in tap water) and faecal coliforms up to 99% (1.51 +- 0.03 CFU/100 mL in tap water) was recorded. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 34194514-7 2021 Removal efficiency of the treatment plant for total coliforms up to 91.6% (15 +- 0.26 CFU/100 mL in tap water) and faecal coliforms up to 99% (1.51 +- 0.03 CFU/100 mL in tap water) was recorded. Water 174-179 nuclear RNA export factor 1 Homo sapiens 170-173 34194514-8 2021 Parameters of pH, temperature, and faecal coliform were statistically significant different at p < 0.05 in tap water source. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 34071256-8 2021 The fluoride content in tap water samples collected from public sources averaged from 0.35 to 1.11 ppm. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 34578876-0 2021 Tap Water Consumption and Perceptions in United States Latinx Adults. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 34578876-3 2021 While overall plain water intake is similar between Latinx and NH white adults, Latinx adults consistently consume significantly more bottled water and less tap water. Water 161-166 nuclear RNA export factor 1 Homo sapiens 157-160 34578876-4 2021 The purpose of this review is to identify factors that may contribute to low water intake and low tap water intake, particularly in Latinx adults. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 34578876-6 2021 Plain water preferences appear to be related, in part, to perceptions of tap water safety as Latinx adults are significantly more likely to perceive their tap water as unsafe compared to NH white adults. Water 6-11 nuclear RNA export factor 1 Homo sapiens 73-76 34578876-6 2021 Plain water preferences appear to be related, in part, to perceptions of tap water safety as Latinx adults are significantly more likely to perceive their tap water as unsafe compared to NH white adults. Water 6-11 nuclear RNA export factor 1 Homo sapiens 155-158 34578876-6 2021 Plain water preferences appear to be related, in part, to perceptions of tap water safety as Latinx adults are significantly more likely to perceive their tap water as unsafe compared to NH white adults. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 34578876-6 2021 Plain water preferences appear to be related, in part, to perceptions of tap water safety as Latinx adults are significantly more likely to perceive their tap water as unsafe compared to NH white adults. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 34578876-7 2021 Although recent investigations have not consistently or comprehensively evaluated the same factors, we have compiled their findings to describe the complex, interrelated determinants of tap water safety perceptions in Latinx adults. Water 190-195 nuclear RNA export factor 1 Homo sapiens 186-189 34578820-0 2021 Using a Community-Based Participatory Mixed Methods Research Approach to Develop, Evaluate, and Refine a Nutrition Intervention to Replace Sugary Drinks with Filtered Tap Water among Predominantly Central-American Immigrant Families with Infants and Toddlers: The Water Up @Home Pilot Evaluation Study. Water 171-176 nuclear RNA export factor 1 Homo sapiens 167-170 34578820-0 2021 Using a Community-Based Participatory Mixed Methods Research Approach to Develop, Evaluate, and Refine a Nutrition Intervention to Replace Sugary Drinks with Filtered Tap Water among Predominantly Central-American Immigrant Families with Infants and Toddlers: The Water Up @Home Pilot Evaluation Study. Water 264-269 nuclear RNA export factor 1 Homo sapiens 167-170 34578820-2 2021 This manuscript describes the explicit integration of mixed-methods in four stages of CBPR: (1) connecting and diagnosing, (2) prescribing-implementing, (3) evaluating, and (4) disseminating and refining an intervention that aimed to motivate Latino parents (predominantly Central American in the US) of infants and toddlers to replace sugary drinks with filtered tap water. Water 368-373 nuclear RNA export factor 1 Homo sapiens 364-367 34384513-6 2022 RESULTS: The consumption of tap water increased in the IG from baseline to T1 and then decreased again at T2, but this was similar in the CG (no statistically significant difference in the time trend between the IG and CG). Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 34384513-7 2022 Similar results were seen for tap water consumption in the mornings. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 34384513-8 2022 The proportion of children who only drank tap water on school mornings increased significantly from baseline to T1 in the IG compared to the CG (p=0.020). Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 34384513-10 2022 CONCLUSIONS: Not only the children in the IG but also those in the CG drank more tap water after 1 school year than at the beginning. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 34315942-3 2021 One-dimensional oedometer swell tests were conducted using distilled water, tap water, and municipal landfill leachate, resulting in the determination of the expansion indices. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 34091221-0 2021 Roles and Knowledge Gaps of Point-of-Use Technologies for Mitigating Health Risks from Disinfection Byproducts in Tap Water: A Critical Review. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 34306741-15 2021 According to binary and multivariate logistic regression analyses, the parents without awareness, pupils with a nail-biting habit, pupils not wearing shoes during play, lack of deworming, drinking direct tap water, and pupils with poor hand sanitation were more likely to be infested with intestinal parasitic infections. Water 208-213 nuclear RNA export factor 1 Homo sapiens 204-207 34080589-7 2021 The fluorescence imprinted sensor was applied to recognize ketoprofen in tap water, lake water, waste water and human urine samples rapidly with the recoveries of 97.3-103.7%. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 34230564-5 2021 Tap water had an average pH of 5.24 +- 1.63, ranging from 3.86 to 8.89, with the average concentrations of As and Pb of 0.77 microg/L and 0.004 microg/L, respectively. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 34230564-6 2021 The levels of both As and Pb in the hair, fingernails and urine of shallow groundwater-consuming residents were greater than those in the hair, fingernails and urine of tap water-consuming residents. Water 173-178 nuclear RNA export factor 1 Homo sapiens 169-172 34201160-2 2021 We examined the association between urinary fluoride adjusted for specific gravity (UFSG) and tap water fluoride levels, by age and sex, among individuals living in Canada. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 34100164-2 2021 This study investigated the presence and the quantity of microplastics in bottled and tap water from five regions in Saudi Arabia and estimated the dietary intake of microplastics. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 34063758-3 2021 Furthermore, the fluorescent probe L could be utilized for detection in real water samples with satisfactory recoveries in the range 99.20%~104.30% in lake water and 100.00%~104.80% in tap water by UV-Vis absorption spectrometry, and in the range 100.50%~108.60% in lake water and 102.70%~103.80% in tap water by fluorescence spectrophotometry. Water 77-82 nuclear RNA export factor 1 Homo sapiens 185-188 34063758-3 2021 Furthermore, the fluorescent probe L could be utilized for detection in real water samples with satisfactory recoveries in the range 99.20%~104.30% in lake water and 100.00%~104.80% in tap water by UV-Vis absorption spectrometry, and in the range 100.50%~108.60% in lake water and 102.70%~103.80% in tap water by fluorescence spectrophotometry. Water 77-82 nuclear RNA export factor 1 Homo sapiens 300-303 34063758-3 2021 Furthermore, the fluorescent probe L could be utilized for detection in real water samples with satisfactory recoveries in the range 99.20%~104.30% in lake water and 100.00%~104.80% in tap water by UV-Vis absorption spectrometry, and in the range 100.50%~108.60% in lake water and 102.70%~103.80% in tap water by fluorescence spectrophotometry. Water 189-194 nuclear RNA export factor 1 Homo sapiens 185-188 34063758-3 2021 Furthermore, the fluorescent probe L could be utilized for detection in real water samples with satisfactory recoveries in the range 99.20%~104.30% in lake water and 100.00%~104.80% in tap water by UV-Vis absorption spectrometry, and in the range 100.50%~108.60% in lake water and 102.70%~103.80% in tap water by fluorescence spectrophotometry. Water 304-309 nuclear RNA export factor 1 Homo sapiens 300-303 34136673-0 2021 Determination and health risk assessment of trace elements in the tap water of two Sub-Cities of Addis Ababa, Ethiopia. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 34136673-7 2021 Conversely, tap water from Akaki-Kality contained significantly higher levels of As than that from Gullele. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 34228620-3 2021 MATERIAL AND METHODS The presented study compared two groups; hand scrubbing with sensory tap was enrolled as group A and classic tap with running water was enrolled as group B. Water 147-152 nuclear RNA export factor 1 Homo sapiens 130-133 34228620-6 2021 Running water from a tap in 10 seconds was measured with the help of a measuring cup. Water 8-13 nuclear RNA export factor 1 Homo sapiens 21-24 35081754-10 2022 RESULTS: Overall, 36% of adults reported using a filter for drinking tap water at home; 14% did not drink tap water at home. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 34259433-8 2021 tap water (control group). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 35081754-13 2022 Using a water filter was associated with higher odds of drinking >3 cups/day of tap water (AOR=1.33, 95%CI=1.13-1.56) and lower odds of SSBs >=1 time/day (AOR=0.76, 95%CI=0.62-0.92). Water 8-13 nuclear RNA export factor 1 Homo sapiens 80-83 35081754-0 2022 Factors Related to Water Filter Use for Drinking Tap Water at Home and Its Association with Consuming Plain Water and Sugar-Sweetened Beverages among U.S. Water 19-24 nuclear RNA export factor 1 Homo sapiens 49-52 35081754-13 2022 Using a water filter was associated with higher odds of drinking >3 cups/day of tap water (AOR=1.33, 95%CI=1.13-1.56) and lower odds of SSBs >=1 time/day (AOR=0.76, 95%CI=0.62-0.92). Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 35081754-0 2022 Factors Related to Water Filter Use for Drinking Tap Water at Home and Its Association with Consuming Plain Water and Sugar-Sweetened Beverages among U.S. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 35081754-14 2022 Not drinking tap water at home was associated with higher odds of drinking >3 cups/day bottled water (AOR=3.46, 95%CI=2.70-4.44). Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 35081754-0 2022 Factors Related to Water Filter Use for Drinking Tap Water at Home and Its Association with Consuming Plain Water and Sugar-Sweetened Beverages among U.S. Water 108-113 nuclear RNA export factor 1 Homo sapiens 49-52 35081754-14 2022 Not drinking tap water at home was associated with higher odds of drinking >3 cups/day bottled water (AOR=3.46, 95%CI=2.70-4.44). Water 95-100 nuclear RNA export factor 1 Homo sapiens 13-16 35081754-2 2022 OBJECTIVE: To examine factors associated with water filter use (WFU) for drinking tap water at home and its association with consuming plain water and sugar-sweetened beverages (SSBs). Water 46-51 nuclear RNA export factor 1 Homo sapiens 82-85 35081754-15 2022 CONCLUSIONS: WFU was associated with higher tap water intake and lower SSB intake among U.S. adults. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 35561596-1 2022 Recent research findings have confirmed the presence of illicit drugs in tap water from some European Union (UE) member states. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 35081754-2 2022 OBJECTIVE: To examine factors associated with water filter use (WFU) for drinking tap water at home and its association with consuming plain water and sugar-sweetened beverages (SSBs). Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 35081754-2 2022 OBJECTIVE: To examine factors associated with water filter use (WFU) for drinking tap water at home and its association with consuming plain water and sugar-sweetened beverages (SSBs). Water 141-146 nuclear RNA export factor 1 Homo sapiens 82-85 35561596-2 2022 Contaminants in tap water come directly from drinking water sources such as rivers or lakes owing to inefficient removal at wastewater treatment and water purification plants. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 35561596-2 2022 Contaminants in tap water come directly from drinking water sources such as rivers or lakes owing to inefficient removal at wastewater treatment and water purification plants. Water 54-59 nuclear RNA export factor 1 Homo sapiens 16-19 35561596-2 2022 Contaminants in tap water come directly from drinking water sources such as rivers or lakes owing to inefficient removal at wastewater treatment and water purification plants. Water 149-154 nuclear RNA export factor 1 Homo sapiens 16-19 35098472-10 2022 Barreled water drinking was associated with a 30.4% (95% CI: 11.8%, 52.0%) increase in bis(1-chloro-2-propyl) 1-hydroxy-2-propyl phosphate (BCIPHIPP) compared to tap water drinking. Water 9-14 nuclear RNA export factor 1 Homo sapiens 162-165 35561596-3 2022 This work was aimed at setting a starting point for assessing the health risks of exposure to twelve drugs of abuse through consumption of tap water in the European population. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 35098472-10 2022 Barreled water drinking was associated with a 30.4% (95% CI: 11.8%, 52.0%) increase in bis(1-chloro-2-propyl) 1-hydroxy-2-propyl phosphate (BCIPHIPP) compared to tap water drinking. Water 166-171 nuclear RNA export factor 1 Homo sapiens 162-165 35561596-4 2022 For this purpose, a method using supramolecular solvents (SUPRAS) was developed to extract drugs in the opioid, amphetamine, cocaine and cannabinoid groups from tap water for their determination by liquid chromatography-tandem mass spectrometry (LC-MS/MS). Water 165-170 nuclear RNA export factor 1 Homo sapiens 161-164 35561596-5 2022 A total of 119 tap water samples were collected from eight EU countries for analysis. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 35561596-7 2022 The mean exposure to the drugs through consumption of tap water was calculated to be 0.0064-3.531 ng/kg day for adults and 0.0247-6.7580 ng/kg day for children, whereas that resulting from dermal contact was estimated to be 4-7 orders of magnitude lower. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 35570674-0 2022 Perceptions of Tap Water Associated with Low-Income Michigan Mothers" and Young Children"s Beverage Intake. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 35623187-3 2022 For instance, alkylphenols and phthalates have been frequently reported to be present both in bottled and tap water, affecting different human endpoints. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 35570674-1 2022 OBJECTIVE: To quantify perceptions of tap water among low-income mothers with young children residing in Michigan and examine associations between perceptions of tap water, mothers" and young children"s beverage intake, and mothers" infant feeding practices. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 35570674-5 2022 RESULTS: Two-thirds (66.2%) of mothers reported that their home tap water was safe to drink without a filter while 21.6% were unsure about the safety of their home tap water. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 35570674-6 2022 Mothers" perceptions of their home tap water were associated with their own tap and bottled water intake and their young children"s tap water and bottled water intake. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 35570674-6 2022 Mothers" perceptions of their home tap water were associated with their own tap and bottled water intake and their young children"s tap water and bottled water intake. Water 39-44 nuclear RNA export factor 1 Homo sapiens 76-79 35570674-6 2022 Mothers" perceptions of their home tap water were associated with their own tap and bottled water intake and their young children"s tap water and bottled water intake. Water 39-44 nuclear RNA export factor 1 Homo sapiens 132-135 35570674-6 2022 Mothers" perceptions of their home tap water were associated with their own tap and bottled water intake and their young children"s tap water and bottled water intake. Water 92-97 nuclear RNA export factor 1 Homo sapiens 35-38 35570674-6 2022 Mothers" perceptions of their home tap water were associated with their own tap and bottled water intake and their young children"s tap water and bottled water intake. Water 136-141 nuclear RNA export factor 1 Homo sapiens 35-38 35570674-6 2022 Mothers" perceptions of their home tap water were associated with their own tap and bottled water intake and their young children"s tap water and bottled water intake. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 35570674-6 2022 Mothers" perceptions of their home tap water were associated with their own tap and bottled water intake and their young children"s tap water and bottled water intake. Water 154-159 nuclear RNA export factor 1 Homo sapiens 35-38 35570674-7 2022 Mothers with more negative perceptions of tap water in general, independent of their perceptions about their home tap water, consumed more bottled water and sugar-sweetened beverages, and their young children drank bottled water and fruit drinks more frequently. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 35570674-7 2022 Mothers with more negative perceptions of tap water in general, independent of their perceptions about their home tap water, consumed more bottled water and sugar-sweetened beverages, and their young children drank bottled water and fruit drinks more frequently. Water 147-152 nuclear RNA export factor 1 Homo sapiens 42-45 35570674-9 2022 CONCLUSIONS: Uncertainty about tap water safety and negative perceptions of tap water are common among low-income Michigan mothers. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 35570674-9 2022 CONCLUSIONS: Uncertainty about tap water safety and negative perceptions of tap water are common among low-income Michigan mothers. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 35074388-1 2022 Around 90% of the energy requirement for urban water systems management is for heating domestic tap water. Water 47-52 nuclear RNA export factor 1 Homo sapiens 96-99 35627541-0 2022 A Participatory Science Approach to Evaluating Factors Associated with the Occurrence of Metals and PFAS in Guatemala City Tap Water. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 35627541-2 2022 To address this need, 113 participants among households served by a range of water providers across the Guatemala City metropolitan area were recruited as participatory scientists to collect first-draw and flushed tap water samples at their residence. Water 218-223 nuclear RNA export factor 1 Homo sapiens 214-217 35627541-9 2022 Overall, the high prevalence of arsenic above the MPL in Guatemala City tap water represents a potential health risk that current water treatment processes are not optimized to remove. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 35537674-8 2022 CONCLUSION: On average, students had negative school water security experiences, which decreased their consumption of water from tap water sources. Water 118-123 nuclear RNA export factor 1 Homo sapiens 129-132 35537674-8 2022 CONCLUSION: On average, students had negative school water security experiences, which decreased their consumption of water from tap water sources. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 35102375-9 2022 Adults who avoided their tap water consumed less tap and plain water, and significantly more bottled water and SSBs on a given day. Water 101-106 nuclear RNA export factor 1 Homo sapiens 25-28 35102375-10 2022 No tap intake and categories of tap water intake produced 77% and 78% areas under the ROC curve in predicting tap water avoidance. Water 36-41 nuclear RNA export factor 1 Homo sapiens 110-113 35102375-10 2022 No tap intake and categories of tap water intake produced 77% and 78% areas under the ROC curve in predicting tap water avoidance. Water 114-119 nuclear RNA export factor 1 Homo sapiens 3-6 35102375-10 2022 No tap intake and categories of tap water intake produced 77% and 78% areas under the ROC curve in predicting tap water avoidance. Water 114-119 nuclear RNA export factor 1 Homo sapiens 32-35 35102375-10 2022 No tap intake and categories of tap water intake produced 77% and 78% areas under the ROC curve in predicting tap water avoidance. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 35102375-11 2022 CONCLUSION: This study demonstrates that water intake variables from dietary recalls can be used to accurately predict tap water avoidance and provide a window into water insecurity. Water 41-46 nuclear RNA export factor 1 Homo sapiens 119-122 35102375-11 2022 CONCLUSION: This study demonstrates that water intake variables from dietary recalls can be used to accurately predict tap water avoidance and provide a window into water insecurity. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 35102375-12 2022 Growing reliance on bottled water may indicate increasing concerns about tap water. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 35305520-5 2022 Furthermore, the proposed "Turn-off" sensor could be employed to quickly and accurately quantify TCs residues even in milk, honey and tap water. Water 138-143 nuclear RNA export factor 1 Homo sapiens 134-137 35511329-5 2022 Although the NP concentrations measured in the drinking water sources of urban areas were significantly higher than those in rural areas (P < 0.05), the tap water and urine NP concentrations measured in urban areas were unexpectedly lower than those of rural areas (P < 0.05). Water 157-162 nuclear RNA export factor 1 Homo sapiens 153-156 35102375-1 2022 BACKGROUND: In the US, problems with the provision of safe, affordable water have resulted in an increasing number of adults who avoid their tap water, which may indicate underlying water insecurity. Water 71-76 nuclear RNA export factor 1 Homo sapiens 141-144 35102375-1 2022 BACKGROUND: In the US, problems with the provision of safe, affordable water have resulted in an increasing number of adults who avoid their tap water, which may indicate underlying water insecurity. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 35102375-1 2022 BACKGROUND: In the US, problems with the provision of safe, affordable water have resulted in an increasing number of adults who avoid their tap water, which may indicate underlying water insecurity. Water 182-187 nuclear RNA export factor 1 Homo sapiens 141-144 35102375-3 2022 OBJECTIVES: This article aims to demonstrate how water intake variables from dietary recall data relate to and predict a key water insecurity proxy, i.e., tap water avoidance. Water 49-54 nuclear RNA export factor 1 Homo sapiens 155-158 35102375-3 2022 OBJECTIVES: This article aims to demonstrate how water intake variables from dietary recall data relate to and predict a key water insecurity proxy, i.e., tap water avoidance. Water 125-130 nuclear RNA export factor 1 Homo sapiens 155-158 35102375-3 2022 OBJECTIVES: This article aims to demonstrate how water intake variables from dietary recall data relate to and predict a key water insecurity proxy, i.e., tap water avoidance. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 35102375-5 2022 Second, I use multiple linear and logistic regressions to test how tap water avoidance relates to plain water intake and sugar-sweetened beverage consumption. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 35102375-5 2022 Second, I use multiple linear and logistic regressions to test how tap water avoidance relates to plain water intake and sugar-sweetened beverage consumption. Water 104-109 nuclear RNA export factor 1 Homo sapiens 67-70 34982502-1 2022 BACKGROUND: Tap water iontophoresis (TWI) is an effective treatment option for palmoplantar hyperhidrosis (HH). Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 35074388-1 2022 Around 90% of the energy requirement for urban water systems management is for heating domestic tap water. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 35344356-0 2022 Point-of-Use Filters for Lead Removal from Tap Water: Opportunities and Challenges. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 35436640-8 2022 The designed sensor has a good recovery in two real samples of tap water and orange juice, indicating it can be used as an alternative detection method via comparison with other detection method. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 35440593-2 2022 Mapping where wells tap fossil aquifers is relevant for water quality and quantity management. Water 56-61 nuclear RNA export factor 1 Homo sapiens 20-23 35464881-0 2022 A batch microfabrication of a self-cleaning, ultradurable electrochemical sensor employing a BDD film for the online monitoring of free chlorine in tap water. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 35464881-1 2022 Free chlorine is one of the key water quality parameters in tap water. Water 32-37 nuclear RNA export factor 1 Homo sapiens 60-63 35464881-1 2022 Free chlorine is one of the key water quality parameters in tap water. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 35464881-2 2022 However, a free chlorine sensor with the characteristics of batch processing, durability, antibiofouling/antiorganic passivation and in situ monitoring of free chlorine in tap water continues to be a challenging issue. Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 35464881-10 2022 The interesting sensing and self-cleaning behavior of the as-proposed sensor indicate that this study of the mass production of free chlorine sensors by MEMS is successful in developing a competitive device for the online monitoring of free chlorine in tap water. Water 257-262 nuclear RNA export factor 1 Homo sapiens 253-256 35355372-0 2022 Tap water as a natural vehicle for microorganisms shaping the human gut microbiome. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 35326020-2 2022 Methods: A total of 39 healthy young adults ingested either 1000 mL (n = 21) or 500 mL (n = 18) of tap water in 5 min. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 35355372-3 2022 In the current study, an exhaustive shotgun metagenomics analysis of the tap water microbiome highlighted the occurrence of a highly genetic biodiversity of the microbial communities residing in fresh water and the existence of a conserved core tap water microbiota largely represented by novel microbial species, representing microbial dark matter. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 35355372-3 2022 In the current study, an exhaustive shotgun metagenomics analysis of the tap water microbiome highlighted the occurrence of a highly genetic biodiversity of the microbial communities residing in fresh water and the existence of a conserved core tap water microbiota largely represented by novel microbial species, representing microbial dark matter. Water 201-206 nuclear RNA export factor 1 Homo sapiens 73-76 35355372-3 2022 In the current study, an exhaustive shotgun metagenomics analysis of the tap water microbiome highlighted the occurrence of a highly genetic biodiversity of the microbial communities residing in fresh water and the existence of a conserved core tap water microbiota largely represented by novel microbial species, representing microbial dark matter. Water 249-254 nuclear RNA export factor 1 Homo sapiens 73-76 35355372-3 2022 In the current study, an exhaustive shotgun metagenomics analysis of the tap water microbiome highlighted the occurrence of a highly genetic biodiversity of the microbial communities residing in fresh water and the existence of a conserved core tap water microbiota largely represented by novel microbial species, representing microbial dark matter. Water 249-254 nuclear RNA export factor 1 Homo sapiens 245-248 35367430-1 2022 The increasing needs of drinking water due to population growth requires seeking for new tap water sources. Water 33-38 nuclear RNA export factor 1 Homo sapiens 89-92 35355372-5 2022 Accordingly, investigation of the fecal microbiota content of a subject that daily consumed tap water for three years provides proof for horizontal transmission and colonization of water bacteria in the human gut. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 35367430-1 2022 The increasing needs of drinking water due to population growth requires seeking for new tap water sources. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 35367430-2 2022 However, these large-scale tap water sources are oftentimes abundant with dissolved natural organic matter (NOM), such as tannic acid issue causing color in water. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 35367430-2 2022 However, these large-scale tap water sources are oftentimes abundant with dissolved natural organic matter (NOM), such as tannic acid issue causing color in water. Water 157-162 nuclear RNA export factor 1 Homo sapiens 27-30 35367430-4 2022 This study focuses on developing and testing a suite of cost-effective, scalable, adaptable, and sustainable sorption media that can be implemented near the source locations of tap water as a pretreatment option to remove color for a long-distance interbasin transfer. Water 181-186 nuclear RNA export factor 1 Homo sapiens 177-180 35355372-5 2022 Accordingly, investigation of the fecal microbiota content of a subject that daily consumed tap water for three years provides proof for horizontal transmission and colonization of water bacteria in the human gut. Water 181-186 nuclear RNA export factor 1 Homo sapiens 92-95 35466232-4 2022 The results showed that family education, education expectation, books, education participation, social communication, and tap water had a positive impact on both the Chinese and math cognitive ability of children, while children"s age, gender, and family size had a negative impact on cognitive ability, and the impact of genes was attenuated by family capital. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 35434460-1 2022 A simulation-based bias analysis of haloacetic acids in tap water and hypospadias. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 35434460-5 2022 In this bias analysis, we used a uniform distribution to randomly select 11%-14% of employed women that were assumed to change municipal water systems between home and work and imputed new contaminant exposures for tap water beverages consumed at work among the selected women using resampled values from the control population. Water 219-224 nuclear RNA export factor 1 Homo sapiens 215-218 35168727-3 2022 The developed flexible sensor affords rapid, accurate and stable response for the Ni (II) ions monitoring at its trace level in the biological fluids including human saliva and sweat samples in addition to tap water as an environmental sample without any preconditioning steps over pH range of 2-8 with detection limit of 2.7 x 10-6. Water 210-215 nuclear RNA export factor 1 Homo sapiens 206-209 35260622-1 2022 Harvesting of flow current through implanted hydrophobic surface within silicone pipe as liquid nanogenerators where Tap water (TW), and DI water (DIw) as liquid reservoirs to successfully convert induced mechanical energy into electrical energy. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 35206375-3 2022 In addition, the daily exposure and cumulative health risk of susceptible populations due to drinking tap water were evaluated by using four different reference dose (RfDs) sources. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 35206375-4 2022 The maximum concentrations of PAEs in raw water were between 1.68 and 4.84 and 0.52 and 1.24 microg/L in tap water. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 35206375-5 2022 Moreover, the levels of PAEs in the tap water samples indicated the poor PAEs removal efficiency of the conventional treatment process (59.9-69.1%). Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 35206375-11 2022 However, we recommend a future cumulative risk assessment of vulnerable groups considering their simultaneous exposure to all chemicals that have antiandrogenic effects via tap water. Water 177-182 nuclear RNA export factor 1 Homo sapiens 173-176 35186964-16 2021 Conclusion: Drinking tap water was associated with a low risk of OA among older adults in China. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 35185853-4 2022 The co-occurrence networks showed distinct interconnective characteristics in different MPBs: The structure of MPB incubated in the lake water sample was more robust under environmental stresses, and bacteria in the tap water MPB interacted more cooperatively. Water 220-225 nuclear RNA export factor 1 Homo sapiens 216-219 35185853-5 2022 Regarding this cooperative interaction, the analysis of functional prediction, in this study, also showed that more symbionts and parasites colonized on microplastics in the tap water than in the lake water. Water 178-183 nuclear RNA export factor 1 Homo sapiens 174-177 35185853-6 2022 Moreover, it was suggested that MPBs were more easily formed in the tap water sample. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 35259861-0 2022 (The Safety of Bladder Irrigation with Solution G Prepared with Tap Water). Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 35100286-9 2022 Tap water consumption was the only common risk factor identified. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 35204856-0 2022 Association of Consuming Tap Water or Purified Water during Infancy with Irritable Bowel Syndrome in Children. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 34982023-11 2022 CONCLUSION: There is a broad range in the minerals found in tap water between the different production sites in the nine distribution regions in Flanders. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 35126529-4 2022 A Chi-square test was conducted to examine the association between various demographic factors and having latrine/tap water. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 35126529-7 2022 Water service (solely tap water) coverage was very low (7.6%) as a result of deficient water sources and nonfunctioning pipelines. Water 0-5 nuclear RNA export factor 1 Homo sapiens 22-25 35126529-7 2022 Water service (solely tap water) coverage was very low (7.6%) as a result of deficient water sources and nonfunctioning pipelines. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 35126529-8 2022 The zones, age, educational status, marital status, and family size of the participants were statistically significantly associated with having latrine or tap water, p < 0.05. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 35425275-11 2022 Tap water samples from a residential area were tested using these sensors, which showed good agreement with standard colorimetric measurement methods. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 34982023-0 2022 Could the region you live in prevent or precipitate kidney stone formation due to mineral intake through tap water? Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 34982023-3 2022 METHODS: Data from six water companies providing tap water to nine regions in Flanders regarding calcium, magnesium, potassium, sodium and sulphate content in tap water was retrieved. Water 23-28 nuclear RNA export factor 1 Homo sapiens 49-52 34982023-3 2022 METHODS: Data from six water companies providing tap water to nine regions in Flanders regarding calcium, magnesium, potassium, sodium and sulphate content in tap water was retrieved. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 34982023-3 2022 METHODS: Data from six water companies providing tap water to nine regions in Flanders regarding calcium, magnesium, potassium, sodium and sulphate content in tap water was retrieved. Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 35204856-1 2022 OBJECTIVE: The objective of this study was to analyze the effect of consuming formula powder prepared with tap water or purified water during the first 4 to 6 months of life on the subsequent development of irritable bowel syndrome (IBS). Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 35204856-8 2022 RESULTS: After weighting, there were 73,355 children in the tap water group and 73,351 in the purified water group. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 2533676-3 1989 Especially if the manufacturers" guidelines are not followed strictly and the device is operated with tap water, indoor particle concentrations may reach up to 50 times US outdoor standards for toxic particle concentration. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 35055730-0 2022 Returning Individual Tap Water Testing Results to Research Study Participants after a Wildfire Disaster. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 35100166-8 2022 Our survey results suggest that orderly cleanliness encourages the choice of tap water filtered through water purifier, while aversive cleanliness urges the choice of bottled water. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 34995313-6 2022 We validate the groundwater isoscape against an independent data set of tap water values and show that the model accurately predicts tap water values in communities known to use groundwater resources. Water 137-142 nuclear RNA export factor 1 Homo sapiens 72-75 34995313-6 2022 We validate the groundwater isoscape against an independent data set of tap water values and show that the model accurately predicts tap water values in communities known to use groundwater resources. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 2592208-7 1989 A mean tap water 222Rn content of 38.3 Bq L-1 and 10.4 Bq L-1 was measured in 31 villages with a crystalline subsoil and 73 villages with a sedimentary subsoil, respectively. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 2592496-6 1989 This washing procedure however is more effective for tap-water than for surface water samples. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 2592496-8 1989 Detection limits in surface water samples are 0.1-0.5 micrograms/l whereas those in tap water are 10-50 ng/l. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 2690408-1 1989 Human exposure to volatile organic compounds (VOCs) in tap water is often assumed to be dominated by ingestion of drinking water. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 2690408-3 1989 A three-compartment model is used to simulate the 24-h concentration history of VOCs in the shower, bathroom, and remaining household volumes as a result of tap water use. Water 161-166 nuclear RNA export factor 1 Homo sapiens 157-160 2592208-8 1989 Radon-222 degasing from the tap water into the indoor air leads to an additional exposure of about 0.11 mSv y-1 and 0.03 mSv y-1 in homes with a crystalline subsoil and homes with a sedimentary subsoil, respectively. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 2810505-2 1989 The magnesium-to-calcium ratio in tap water correlated negatively with the incidence of urolithiasis. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 2787112-6 1989 Tap water drinkers whose home source of water included ground water had the greatest risk (13.8) and, after controlling for confounders, their hazard ratio was 1.7. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 2758720-3 1989 The lead source was ultimately traced to the daily administration of powdered formula which was prepared with home tap water having a first-draw lead content of 130 parts per billion. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 2758720-4 1989 This case suggests that whenever infants are fed powdered formula, consideration should be given to analysis of the home tap water for lead content. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 2787112-1 1989 A previous study of pregnant women whose water supply was potentially contaminated revealed a significant increase in spontaneous abortions among those drinking tap as opposed to bottled water, regardless of exposure to the contamination. Water 41-46 nuclear RNA export factor 1 Homo sapiens 161-164 2601607-3 1989 Delineate the effect of tap water pressure and temperature on the quality of contamination wash-out from medical appliances as well as tap water consumption required for different designs of the nozzles at varying water pressures and temperatures. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 2768486-1 1989 The efficacy of a strategy to prevent tap water scalds was evaluated in a population at risk. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 2787112-6 1989 Tap water drinkers whose home source of water included ground water had the greatest risk (13.8) and, after controlling for confounders, their hazard ratio was 1.7. Water 40-45 nuclear RNA export factor 1 Homo sapiens 0-3 2787112-6 1989 Tap water drinkers whose home source of water included ground water had the greatest risk (13.8) and, after controlling for confounders, their hazard ratio was 1.7. Water 40-45 nuclear RNA export factor 1 Homo sapiens 0-3 2787112-7 1989 Based on external data from comparable studies, bottled water drinkers appeared to have had unusually low risks, and tap water drinkers who received ground water may have had slightly high risks. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 2787112-7 1989 Based on external data from comparable studies, bottled water drinkers appeared to have had unusually low risks, and tap water drinkers who received ground water may have had slightly high risks. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 2745781-1 1989 Computed tomography of the gastric wall after ingestion of 500-700 ml of pure tap water, followed by rapid intravenous injection of contrast medium, was performed on 24 patients with known gastric tumors. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 2729877-2 1989 Samples of tap water from Sudbury contained 109 +/- 46 micrograms Ni per L (P less than 0.01 vs 0.4 +/- 0.2 micrograms Ni per L in corresponding water samples from Hartford, Connecticut). Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 2738794-12 1989 Aerosol equipment cleansed with tap water and the showers were implicated as means of exposure by patients to contaminated potable water. Water 131-136 nuclear RNA export factor 1 Homo sapiens 32-35 2530654-1 1989 Tap water fluoridation was juxtaposed to the incidence of dental caries among children residents of Stavropol Territory. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 2503642-8 1989 Further study with a larger sample is needed to determine the effects of using tap water rather than sterile water as diluent. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 2743728-6 1989 Increasing the electrical conductivity of the tap water by adding NaCl (0.2% in weight) resulted in a decrease in amplitude to 1/100 of the direct measurement. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 2715833-4 1989 We therefore gave the patient 99mTc-labeled sulfur colloid and tap water through his nasogastric tube. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 2721007-1 1989 Trihalomethanes (THM) present in tap water were also found in dialysis fluid because they were not eliminated by water treatment. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 2647415-4 1989 Patients with chronic renal failure are also exposed to aluminum in domestic tap-water supplies used either for drinking or, in those on dialysis treatment, in the preparation of their dialysate. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 2607010-1 1989 Drinking bottled water has become a popular substitute for tap water because of the concern over the contamination of municipal water supplies. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 2607010-1 1989 Drinking bottled water has become a popular substitute for tap water because of the concern over the contamination of municipal water supplies. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 2463199-6 1989 The analysis (performed by the patient) involves 1) collecting urine for 24 h in a 4-L container, 2) diluting the urine with tap water to a total urine of 4 L, and 3) placing a drop of this dilution onto a slide. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 2463199-8 1989 The reliability of this system has been tested for wide changes of urine pH, volume of the drop applied to the slide, and tap water from different sources. Water 126-131 nuclear RNA export factor 1 Homo sapiens 122-125 2568061-0 1989 Treatment of hyperhidrosis manuum by tap water iontophoresis. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 2568061-1 1989 In a randomised, double-blind, controlled clinical trial of the effect of treatment with tap water iontophoresis, 11 patients with palmar hyperhidrosis were treated actively on one hand and with placebo on the other. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 2488958-2 1989 ECG from the pacemaker implanted patients in the bathtub with tap water was recorded through three silver/silver chloride electrodes (4 x 4 cm) fitted on the inside wall of bathtub. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 2554099-6 1989 If the finger was moistened with tap water or saliva, there was a 100% recovery rate of virus after touching dried out droplets, as well as after touching droplets in a liquid state. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 3221068-2 1988 Current Danish treatment includes prolonged tap water irrigation of burns, which largely replaces the use of narcotics for pain control in both the inpatient and outpatient settings. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 3220764-0 1988 [Home treatment of hyperhidrosis of the hands and feet tap water iontophoresis]. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 20539438-4 1988 Streak camera recordings of the emission from laser-induced plasmas were taken in distilled and tap water in controlled irradiation conditions. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 3052347-4 1988 Tap water had to be heated above 65 degrees C to reliably kill all bacterial enteropathogens. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 22148669-0 1988 Indoor particle concentrations associated with use of tap water in portable humidifiers. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 3168427-2 1988 Potential risk factors included corticosteroid therapy and the use of warm tap water compresses at the site of intravenous catheter-related phlebitis. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 18964577-2 1988 The suggested procedure has been used for the determination of iron(III) in tap water and the accuracy investigated both by analysing standard solutions and by comparison with results obtained by atomic-absorption spectrometry. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 3618853-0 1987 Prevention of tap water scald burns: evaluation of a multi-media injury control program. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 2965296-0 1988 Hospitalizations due to tap water scalds, 1978-1985. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 18964517-0 1988 Determination of Mo(VI) in tap-water and sea-water by differential-pulse polarography and co-flotation. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 3346617-3 1988 The extremities to be treated are placed in tanks containing tap water ensuring conduction fo current between epidermis and electrode. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 3191800-0 1988 [A study on the carcinogenic risk of organic concentrates from tap water in H city]. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 3480378-0 1987 Bladder cancer, drinking water source, and tap water consumption: a case-control study. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 3480378-3 1987 Risk of bladder cancer increased with intake level of beverages made with tap water. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 3480378-4 1987 The odds ratio (OR) for the highest vs. lowest quintile of tap water consumption was 1.43 [95% confidence interval (CI) = 1.23, 1.67; chi 2 for trend = 26.3, P less than .001]. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 3480378-8 1987 Among non-smoking respondents with tap water consumption above the population median, the OR increased with exposure duration to a level of 3.1 (CI = 1.3, 7.3; chi 2 for trend = 6.3, P = .01) for greater than or equal to 60 years of residence at places served by chlorinated surface water (vs. non-chlorinated ground water users). Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 3480378-8 1987 Among non-smoking respondents with tap water consumption above the population median, the OR increased with exposure duration to a level of 3.1 (CI = 1.3, 7.3; chi 2 for trend = 6.3, P = .01) for greater than or equal to 60 years of residence at places served by chlorinated surface water (vs. non-chlorinated ground water users). Water 283-288 nuclear RNA export factor 1 Homo sapiens 35-38 3480378-8 1987 Among non-smoking respondents with tap water consumption above the population median, the OR increased with exposure duration to a level of 3.1 (CI = 1.3, 7.3; chi 2 for trend = 6.3, P = .01) for greater than or equal to 60 years of residence at places served by chlorinated surface water (vs. non-chlorinated ground water users). Water 283-288 nuclear RNA export factor 1 Homo sapiens 35-38 3662252-2 1987 Tap water in this industrial city comes from the Llobregat river and is extremely hard, with an excessive level of salts. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 3613009-5 1987 Control was easily obtained by insertion of a 0.2-micron polymer filter into the outflow tubing of our pathology tap water-deionizing unit and the tap water source in the bronchoscopy suite. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 3613009-5 1987 Control was easily obtained by insertion of a 0.2-micron polymer filter into the outflow tubing of our pathology tap water-deionizing unit and the tap water source in the bronchoscopy suite. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 3664327-1 1987 Severe hyponatraemia, hyperkalaemia and pre-renal uraemia were seen in two burn victims who were treated with repeated submersion in tap-water. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 3654446-7 1987 The level of the water may be adjusted to any desired level by means of a waste line or an inlet of tap water. Water 17-22 nuclear RNA export factor 1 Homo sapiens 100-103 3654446-7 1987 The level of the water may be adjusted to any desired level by means of a waste line or an inlet of tap water. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 2888811-7 1987 Our findings suggest that filling bubble humidifiers or underwater chest drains with tap water is a potential hazard and should be avoided. Water 61-66 nuclear RNA export factor 1 Homo sapiens 85-88 3301614-4 1987 The tap-water enema group was, therefore, suspended but the rest of the study continued after rerandomization for lactose and lactitol groups. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 3301614-8 1987 These data suggest that acidifying agents like lactose and lactitol are effective and superior to tap-water enemas for the treatment of acute nitrogenous portal-systemic encephalopathy. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 3606215-3 1987 Median consumption of tap water consumed alone and tapwater alone plus that used in beverages (ml per day) was 36.5 (range 0-791) and 171.5 (range 0-1036), respectively. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 3296767-1 1987 The Blairex Water Purifier (previously called The Blairex Deionizer) is a filtration unit designed to purify tap water for uses that require distilled or deionized water. Water 12-17 nuclear RNA export factor 1 Homo sapiens 109-112 3296767-1 1987 The Blairex Water Purifier (previously called The Blairex Deionizer) is a filtration unit designed to purify tap water for uses that require distilled or deionized water. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 3472669-1 1987 Tap water use. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 3109156-1 1987 Water conducting systems in hospitals (endoscopes, nebulizers, tap water systems, dental units etc.) Water 0-5 nuclear RNA export factor 1 Homo sapiens 63-66 3556437-6 1987 In some cases, several zymotypes were isolated simultaneously from the same tap water. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 3588503-6 1987 For birds raised on tap water, unilateral sodium infusion caused a significant unilateral reduction in the glomerular filtration rate. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 3653460-0 1987 Long-term efficacy and side effects of tap water iontophoresis of palmoplantar hyperhidrosis--the usefulness of home therapy. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 3441015-8 1987 Cool tap water immersion initially provided more relief while vegetable oil provided better long-term relief from the pain of "chile burns". Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 3467419-1 1986 The present study was undertaken in a community, where the tap water has been optimally fluoridated since 1959 (1.0-1.2 ppm). Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 3570320-0 1986 Use of tap water instead of electrode jelly for recording electrocardiograms. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 3606215-1 1987 Tap water consumption was estimated from 3 day weighed dietary records in 102 Canadian preschool children (4-5 yr of age; 58 males, 44 females). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 3606215-7 1987 Hard tap water provided less than 8% of the Canadian Recommended Nutrient Intake (RNI) for magnesium, less than 3% for calcium, and less than 1% for zinc. Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 3457525-7 1986 Intensity of aerosolization directly correlated with the degree of L. pneumophila contamination of the tap water used to fill the humidifier. Water 107-112 nuclear RNA export factor 1 Homo sapiens 103-106 3958498-0 1986 Washing of ELISA plates with running tap water. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 3457525-8 1986 Rinsing of ventilation bag apparatus with tap water led to isolation of L. pneumophila from culture plates after the ventilation bags were squeezed. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 3707186-4 1986 Scalds usually followed spillage from kitchen containers in accidents and forced tap water immersion in cases of abuse. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 3953506-2 1986 This method, using an unmodified microwave oven and a tap-water environment, decreases thawing time from 37.5 minutes for the standard 37 degrees C water bath to approximately 11 minutes for either one or two units of FFP. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 3953506-2 1986 This method, using an unmodified microwave oven and a tap-water environment, decreases thawing time from 37.5 minutes for the standard 37 degrees C water bath to approximately 11 minutes for either one or two units of FFP. Water 148-153 nuclear RNA export factor 1 Homo sapiens 54-57 3697522-0 1986 Chloroform in tap water and human blood. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 3634759-2 1986 In our hospital, patients are immersed in a tub of warm, continuously-flowing tap water. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 2424148-8 1986 Wash in running tap water for 1 hr. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 3947759-0 1986 Potential formation of bromophenols in Barcelona"s tap water due to daily salt mine discharges and occasional phenol spills. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 3514385-0 1986 [Deficiencies in the method for the sanitary bacteriological analysis of chlorinated tap water]. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 3512655-8 1986 The root surface must not be handled, scraped, brushed, or have any part removed; it can be rinsed with sterile water, saline, or tap water but not with caustic solutions, disinfectants, or medicaments to clean the surface. Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 3752932-6 1986 We have shown the influence of the geographical origin of the tap water on the Ca and F intake, as well as the influence of individual behaviour with respect to the selection of his main drink. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 3720354-2 1986 Provocative testing with tap water produced transient edema and pruritus. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 3908086-10 1985 Some domestic tap-water supplies contain aluminum in high concentration, either naturally or because aluminum has been added as a flocculant in the purification process. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 3720354-4 1986 After several weeks, the angioedema gradually subsided, the reaction to tap water became negative, and the patient was able to swim again without reactions. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 3805713-8 1986 M. xenopi was found in tap water of 5 persons with M. xenopi in their sputum and in one of the two healthy persons. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 3743230-8 1986 Preliminary analysis of the geographical variation in the Si content of tap water suggests that uraemic hypersilicaemia may protect haemodialysed patients from the development of aluminium dementia. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 4062363-6 1985 Tap water and infant blood lead levels correlated minimally (r = .11, P = .10). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 4076075-4 1985 Both As and Se appear to be mobilized from household plumbing into tap water by the corrosive action of soft, mildly acidic water, while surface water catchment systems in areas impacted by acidic deposition may contain elevated soluble As levels. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 3000086-5 1985 In the field, the developed method was used for testing water specimens from various water bodies (sewage, river water, tap water). Water 56-61 nuclear RNA export factor 1 Homo sapiens 120-123 3842880-4 1985 Over one half of these burns were caused by tap water. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 30943617-1 1985 One hundred thirty-two pork carcasses were used with 36 of these receiving a wash with tap water and 96 receiving a wash with tap water plus 200 ppm of sodium hypochlorite. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 4004231-9 1985 In addition, the quality of swimming pool water also depends on the quality of its source tap water. Water 42-47 nuclear RNA export factor 1 Homo sapiens 90-93 4004231-9 1985 In addition, the quality of swimming pool water also depends on the quality of its source tap water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 4004238-3 1985 In brief, a 100- to 1,000-ml sample of tap water is drawn through a large surface, customized filter housed in the device, and bacteria, rust, and humic acid in the water are concentrated thereon. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 3995774-2 1985 The aluminium content found for tap water was 6-36 micrograms/l. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 2580366-4 1985 The quality of silver impregnation in methods using tap water in the reducing solutions varies in different laboratories. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 3995409-5 1985 Drinking water from the tap was tested in parallel with lake water, and its mutagenicity tended to fluctuate with the mutagenicity of the lake water. Water 9-14 nuclear RNA export factor 1 Homo sapiens 24-27 3995409-5 1985 Drinking water from the tap was tested in parallel with lake water, and its mutagenicity tended to fluctuate with the mutagenicity of the lake water. Water 61-66 nuclear RNA export factor 1 Homo sapiens 24-27 2859326-5 1985 On the basis of these results, tap water is a likely source of the aeromonads found in human intestinal flora. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 2984992-0 1985 Modified membrane-filter procedure for concentration of enteroviruses from tap water. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 2984992-2 1985 Viruses in tap water at pH 3.5 were first adsorbed to 10-in. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 2984992-9 1985 45% of several types of enteroviruses added to 114 liters of tap water could be recovered in the final 16-ml sample. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 3895827-4 1985 A comparison of the transit times for tablets taken together with 100 ml of cold carbonated water and 100 ml of lukewarm tap water showed a significantly better passage when the tablets were taken with cold carbonated water (p = 0.01). Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 3895827-4 1985 A comparison of the transit times for tablets taken together with 100 ml of cold carbonated water and 100 ml of lukewarm tap water showed a significantly better passage when the tablets were taken with cold carbonated water (p = 0.01). Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 3895827-5 1985 A similar advantage of carbonated liquids was seen when tablets were taken with 25 ml of lukewarm tap water as compared with 25 ml of cold carbonated water (p = 0.01). Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 18963639-5 1984 The proposed method has been tested in the determination of lead in tap water. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 6741939-6 1984 Over a 12-month period in which the tap water aluminum content averaged over 10 mumol/L (270 micrograms/L), the product water had an aluminum content consistently under 2 mumol/L, being under 1 mumol/L (27 micrograms/L) on 19 out of 20 occasions. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 28164872-6 1985 The dermographic grade varied at different body sites and local applications of oil, talcum powder and even tap water lowered the dermographic grade. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 6569854-2 1984 The same organism was recovered from the dialysate produced by the machine and from its tap water supply. Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 6205334-5 1984 Solutions of lactose, fructose, glucose and galactose were preferred to plain tap water. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 6715169-0 1984 [Tap water iontophoresis in the treatment of hyperhidrosis of the hands and feet]. Water 5-10 nuclear RNA export factor 1 Homo sapiens 1-4 6721017-2 1984 Stratification of illness by consumption of municipal tap water showed a striking dose-response, with an attack rate of 42 per cent among persons who drank six or more glasses of water per day. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 6721017-2 1984 Stratification of illness by consumption of municipal tap water showed a striking dose-response, with an attack rate of 42 per cent among persons who drank six or more glasses of water per day. Water 179-184 nuclear RNA export factor 1 Homo sapiens 54-57 16346487-3 1984 The salt content of the tap water and sewage water promoted virus adsorption, but evidently the organic compounds in sewage retarded adsorption. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 6322223-4 1984 It is assumed that the remainder of water in the tissue has a relaxation rate that is independent of frequency, as is characteristic of bulk tap water. Water 36-41 nuclear RNA export factor 1 Homo sapiens 141-144 6322223-4 1984 It is assumed that the remainder of water in the tissue has a relaxation rate that is independent of frequency, as is characteristic of bulk tap water. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 6087436-2 1984 Tap water contained high amounts of lead and biopsy confirmed the intoxication. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 6706577-10 1984 However, tap water iontophoresis is gaining increasing significance as an effective and safe treatment in palmar and plantar hyperhidrosis. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 6540678-2 1984 When faced with this problem, we have had the patient ingest 250 cc of tap water. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 6866309-6 1983 d) Results in a characteristic change in certain coagulation parameters when compared with saline solution and tap water. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 6663066-2 1983 The disease was caused by repeated exposures to tap water aerosol. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 6412968-0 1983 [Various renal reactions to immersion in tap water and carbonic water]. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 7144671-0 1982 Heinz-body haemolysis in haemodialysed patients caused by chloramines in Sydney tap water. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 6309878-4 1983 The adsorbed viruses from both tap water and secondary sewage were most efficiently eluted with 4% beef extract - 0.5 M NaC1, pH 9.5. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 6309878-6 1983 of tap water ranged between 32 and 98%, 67 and 100% and 69 and 100%, respectively. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 6851157-0 1983 Volatile halocarbons in tap water as a problem in haemodialysis therapy. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 6851157-1 1983 The concentrations of volatile halocarbons in the tap water of Turku and of Turku University Central Hospital are quite high and are reduced but not eliminated during water treatment at the hospital. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 6851522-1 1983 Nickel analyses of tap water from several sources in Copenhagen gave up to 490 X 10(-6) g X 1(-1) in the first 250 ml portions. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 7149035-4 1982 Wall motions resembling peristaltic ring contractions were induced in dialysis tubing filled with a concentrated salt solution and immersed in tap water. Water 147-152 nuclear RNA export factor 1 Homo sapiens 143-146 6762189-5 1982 To remove pyrogens and bacteria, tap water was subjected to activated charcoal, ion exchange and reverse osmosis treatment, followed by preparation of the dialysate. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 6875437-3 1983 Individual blood lead can be considerably increased by raised household tap water lead concentrations. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 6875437-4 1983 Mean blood lead is estimated to be 43% higher for men when the concentration of lead in first-draw domestic tap water is 100 micrograms/l compared with a zero concentration. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 6357734-0 1983 [Safety of tap water]. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 6343010-0 1983 [Treatment of tap water with chlorine dioxide]. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 6121245-0 1982 Legionnaires" disease related to gastric lavage with tap water. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 6288805-0 1982 Nosocomial Legionnaires" disease caused by aerosolized tap water from respiratory devices. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 6288805-2 1982 Chart review showed that during the two- to 10-day incubation period before the onset of illness, all of the patients inhaled aerosolized tap water from jet nebulizers (four patients) or from a portable room humidifier (one patient), and all received high dosages of corticosteroids or adrenocorticotropic hormone. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 6288805-4 1982 Environmental cultures yielded Legionella pneumophila from tap water and from reservoirs of tap water-filled respiratory devices. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 6288805-5 1982 The yield was highest from hot tap water, in which the free chlorine level was less than 0.05 parts per million. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 6288805-6 1982 Thus, Legionnaires" disease may be caused by contaminated aerosols from respiratory devices, and the use of contaminated tap water in such devices represents a previously unrecognized hazard to which corticosteroid-treated patients should not be exposed. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 7103256-8 1982 Among never smokers, tap water copper was significantly and positively related to levels of both FVC (p = 0.014) and FEV1 (p = 0.027). Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 6962075-5 1982 The tap water of the region was found to be heavily polluted. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 7253184-8 1981 This resulted from refilling with tap water. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 7085278-1 1982 A young blond woman developed green tinted hair from exposure to tap water containing excessive amounts of copper. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 6274030-2 1981 The dialysate was made up from a high level aluminium tap water. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 7184129-0 1982 [Hydrobiological study of tap water]. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 7440043-4 1980 The symptoms appeared to be associated with exposure to water vapour derived from tap water. Water 56-61 nuclear RNA export factor 1 Homo sapiens 82-85 7246839-4 1981 Since the difference in 24-hour dietary sodium consumption was 300 milligrams between the communities, an intake of one liter of high sodium tap water represented approximately 25 per cent of the difference in total sodium intake between the two communities. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 6171052-3 1981 Final staining was by immersion in 2% potassium ferrocyanide which was followed by washing in tap water. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 7240080-4 1981 The basic principle of the procedure is product saturation with brine, followed by trapping of the filth elements from tap water with oliver oil. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 7223825-3 1981 Prompt rinsing of the contaminated tonometer in running tap water for ten seconds proved sufficient to remove all detectable hepatitis B surface antigen from the tonometer. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 7344059-0 1981 [Occurrence of aqueous organisms in tap water. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 7344059-2 1981 Comparative studies of the tap water fed from a surface source and an infiltration well]. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 7441139-1 1980 A retrospective case-control study was conducted to test the hypothesis that there is an association between the trace element content of domestic tap water and neural tube malformations in infants. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 16345688-2 1981 The isolate was able to multiply in tap water without substrates added, but addition of starch and glucose in amounts as low as 1 mug of substrate C per liter clearly enhanced growth. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 7214691-6 1980 Zinc levels were less affected by the dialysis process; before dialysis: tap-water patients, 952 +/- 131 micrograms/L; distilled-water patients, 932 +/- 119 micrograms/L; after dialysis: 1001 +/- 137 micrograms/L, and 934 +/- 121 micrograms/L, respectively. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 7417155-0 1980 Tap water, an efficient method for cooling heatstroke victims--a model in dogs. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 7007558-4 1980 Occasionally tap water high in copper may be an important supplement to a diet low in copper. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 7440043-7 1980 Despite many efforts the specific causative agent in the tap water has not been identified. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 6258472-1 1980 Simple, reliable, and efficient concentration of poliovirus from tap water was obtained with two types of electropositive filter media, one of which is available in the form of a pleated cartridge filter (Virozorb 1MDS). Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 6258472-2 1980 Virus adsorption from tap water between pH 3.5 and 7.5 was more efficient with electropositive filters than with Filterite filters. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 6258472-5 1980 Recovery of poliovirus from 1,000-liter tap water volumes was approximately 30% efficient with both Virozorb 1MDS and Filterite pleated cartridge filters, but the former were much simpler to use. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 6258472-6 1980 The virus adsorption behavior of these filters appears to be related to their surface charge properties, with more electropositive filters giving more efficient virus adsorption from tap water at higher pH levels. Water 187-192 nuclear RNA export factor 1 Homo sapiens 183-186 7403275-0 1980 Transmissiveness of ultrasound through tap water, glycerin, and mineral oil. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 7421106-5 1980 Tap water as well as water with a salt concentration of 100 mg/lg occupy an intermediate position between desirable and undesirable waters but lie closer to the optimal variant. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 7462923-4 1980 A tap water grab sample was collected from each participant"s residence and analyzed for 80 inorganic chemical constituents. Water 6-11 nuclear RNA export factor 1 Homo sapiens 2-5 6988107-0 1980 An epidemic of extrinsic allergic alveolitis caused by tap water. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 7369842-4 1980 Felt-pad electrodes soaked in tap water or saline produced the highest mean torque and lowest electrical impedance, which made them excellent choices for single session stimulation. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 7356323-4 1980 Positively charged microporous filters were found to efficiently adsorb these coliphages from tap water, sewage, and lake water at neutral pH. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 7356323-6 1980 Using this method, coliphages could be concentrated from 17-liter volumes of tap water with recoveries ranging from 34 to 100%. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 466318-0 1979 Tap water instead of electrode jelly for electrocardiographic recording. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 30812313-2 1979 The Milli-Q system fed by distilled water and the Milli-R/Q system fed by tap water both produced water acceptable for microbiological use as measured by the DWST. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 30812313-2 1979 The Milli-Q system fed by distilled water and the Milli-R/Q system fed by tap water both produced water acceptable for microbiological use as measured by the DWST. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 524564-0 1979 Tap water calcium and its relationship to renal calculi and 24 h urinary calcium output in Great Britain. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 447594-6 1979 The analysis of 300 L Ottawa tap water showed no detectable amounts (less than 1 ng/L) of any of the 16 organophosphorus pesticides. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 505712-0 1979 A quantitative morphological and ecological study of protozoa polluting tap water in Mexico City. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 466981-5 1979 Urine arsenic levels in Ajo children correlated positively with amount of tap-water consumed (r = .32, p less than. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 466981-7 1979 Tap-water drinkers had significantly higher urine arsenic levels than bottled water drinkers (t = 4.21 p less than .001). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 466195-0 1979 Tap water for electrocardiographic recording. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 226761-0 1979 [Hemolytic anemia in chronically dialyzed patients induced by free chlorine in tap water (author"s transl)]. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 379049-3 1979 The active compound was available as a powder; the rinse consisted of 1.7 g powder dissolved in 30 ml hot tap water. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 699406-1 1978 Chloramines, compounds made up of chlorine and ammonia, when present in tap water used for dialysis cause methemoglobinemia and hemolysis. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 427405-0 1979 Tap water instead of electrode jelly for electrocardiographic recording. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 699406-9 1978 We conclude that addition of ascorbic acid to neutralize chloramines in tap water is also effective when using the proportioning dialysis delivery system. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 97011-1 1978 Breeding of Pleurodeles waltii larvae with female gentotype was carried out in 29,5-30 degrees C tap water within 4 months after hatching. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 709813-2 1978 Tap water is initially treated employing reverse osmosis, followed by treatment with activated charcoal and mixed anion/cation exchange resins. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 211753-3 1978 Using concentrations up to 10(4) infectious units per ml representing a multiple quantity of the virus demonstrable in contaminated environmental waters all the viruses investigated could be inactivated reliably and rationally when suspended in tap water, more easily however in water of improved conductivity, by passing the current leading unit once. Water 249-254 nuclear RNA export factor 1 Homo sapiens 245-248 566775-5 1978 Two of the 5 patients showed definite inhibition by concentrated tap water (TW) of IgG antibody against HW. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 683765-0 1978 Tap water scald burns in children. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 683765-1 1978 Tap water scald burns account for 7% to 17% of all childhood scald burns that require hospitalization. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 652514-9 1978 These finding indicate the need of a routine measure of metal content - mainly aluminium and manganese - in tap water used for dialysis, in order to treat this water if necessary. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 25048-0 1978 Concentration of poliovirus from tap water onto membrane filters with aluminum chloride at ambient pH levels. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 25048-1 1978 A method is described for the concentration of an enterovirus from large volumes of tap water by addition of small amounts of aluminum chloride to enhance virus removal by membrane filters. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 25048-2 1978 Tap water treated with 2 X 10(-5) M aluminum chloride showed a slight decrease in pH (less than 0.5), a slight increase in turbidity, and enhanced removal of poliovirus by membrane filters. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 205175-5 1978 With this procedure, poliovirus in large volumes of tap water, seawater, and sewage could be concentrated with an average efficiency of 52, 53, and 50%, respectively. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 80847-4 1978 Staining procedure: wash formalin-fixed brain slices overnight in running tap water. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 80847-6 1978 Wash in running tap water. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 80847-8 1978 Wash in running tap water. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 643590-0 1978 [The tap water dressing]. Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 20174369-1 1978 A laser beam of 1-mrad divergence in water focuses to a thin horizontal line when propagating down a horizontal plastic tube filled with aerated tap water of temperature less than ambient. Water 149-154 nuclear RNA export factor 1 Homo sapiens 145-148 33469-2 1978 The interaction of elementts found in tap water and in aquarium water is also investigated. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 356509-3 1978 The original feature was a motor driven by water from an ordinary water tap. Water 43-48 nuclear RNA export factor 1 Homo sapiens 72-75 356509-3 1978 The original feature was a motor driven by water from an ordinary water tap. Water 66-71 nuclear RNA export factor 1 Homo sapiens 72-75 20174369-1 1978 A laser beam of 1-mrad divergence in water focuses to a thin horizontal line when propagating down a horizontal plastic tube filled with aerated tap water of temperature less than ambient. Water 37-42 nuclear RNA export factor 1 Homo sapiens 145-148 652514-9 1978 These finding indicate the need of a routine measure of metal content - mainly aluminium and manganese - in tap water used for dialysis, in order to treat this water if necessary. Water 160-165 nuclear RNA export factor 1 Homo sapiens 108-111 1005927-4 1976 Intraduodenal application of tap water amounting to 0.5, 1,0 or 2,0% body weight lead to extremely variable reactions both in time course and dimension of AVD. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 596900-1 1977 Two silver-blond young women developed green, tinted hair from exposure to tap water containing excessive amounts of copper. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 30731532-5 1977 Under comparable conditions of application, both sodium hypochlorite (200 to 250 mg/liter) and tap water reduced counts by about 90%. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 328126-6 1977 However, their absorption and toxicity in the newborn are unknown and, unless use of a skin disinfectant is warranted, routine bathing of newborns with tap water appears to be satisfactory. Water 156-161 nuclear RNA export factor 1 Homo sapiens 152-155 329637-2 1977 Moreover, brown or black flakes were often present in tap water, as well as in the water lines of dental equipment. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 406283-0 1977 Ultrasonic contrast study to indentify stomach tap water microbubbles. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 406283-2 1977 By giving the patient a drink of two or three ounces of freshly drawn water, multiple strong echoes are produced from the fundus and the body of the stomach because of the microbubbles contained in recently agitated tap water and the microbubbles produced by the mixing effect of swallowing. Water 70-75 nuclear RNA export factor 1 Homo sapiens 216-219 406283-2 1977 By giving the patient a drink of two or three ounces of freshly drawn water, multiple strong echoes are produced from the fundus and the body of the stomach because of the microbubbles contained in recently agitated tap water and the microbubbles produced by the mixing effect of swallowing. Water 220-225 nuclear RNA export factor 1 Homo sapiens 216-219 18088-5 1977 Reconcentration methods described previously for eluates from filters that process tap water or treated wastewater were inadequate when applied to eluates from filters used to process estuarine water containing large amounts of organic compounds. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 559960-5 1977 Spinal tap showed an opening pressure of 90 mm of water and clear CSF with 62 mg/dl of protein content. Water 50-55 nuclear RNA export factor 1 Homo sapiens 7-10 192145-0 1977 Regeneration of pleated filters used to concentrate enteroviruses from large volumes of tap water. Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 192145-1 1977 Pleated cartridge filters are capable of concentrating enteroviruses from large volumes (well over 2,000 liters) of tap water. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 602442-4 1977 Prerinsing for 2 min with cold tap water removes 91.25 percent of the quantity of casein originally present. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 588857-0 1977 Mortality and the concentration of elements in tap water in county boroughs in England and Wales. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 202896-3 1977 Samples of household tap water showed increased mercury concentrations (median 0.001 micromol/L). Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 843454-0 1977 Tap water iontophoresis in palmo-plantar hyperhidrosis. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 600956-1 1977 In two dialysis centres in the same city, with a total of 56 patients on regular dialysis treatment, it has been shown that the tap water used for the production of the dialysate contains chloramines. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 18961935-2 1976 One of the resins was used for concentration of trace metal ions from dimineralized water, tap-water, and sea-water. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 10841-0 1976 Organic flocculation: an efficient second-step concentration method for the detection of viruses in tap water. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 1067489-4 1976 Dialysate calcium ranged between 5.7 and 7.3 mg/100 ml depending on the calcium content of local tap water. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 59074-1 1976 Blood and tap-water lead levels were examined in 135 hypertensives and 135 age and sex matched normotensives. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 59074-3 1976 A positive correlation was found between blood-lead and tap-water lead. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 5917-0 1976 Atomic-absorption determination of vanadium and molybdenum in tap water and mineral waters after anion-exchange separation. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 769540-4 1976 Epidemiologic investigation showed that consumption of tap water was associated with illness in the initial cases of affected families. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 1254680-2 1976 This procedure has allowed for the analysis of volatile organics in the low parts-per-billion range from 1 liter or less of tap water. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 1027342-2 1976 a) In a first analytical chapter, we have made the schedule and the critical examination of the different reproaches given to conditioned waters on considering successively: 1) Special drawbacks (although these are of an other category than microbiology) which were given, whichever type of supply (loose, at the tap, or splitted up when the water is conditioned), to some categories of waters (carbonated and mineral) because of their nature by the fact that these waters do not show the charactheristics of potability with regard to the legislation and administration. Water 138-143 nuclear RNA export factor 1 Homo sapiens 313-316 949571-1 1976 The concentrations of 20 trace elements were determined by atomic absorption spectrophotometry on representative samples of tap-water collected from 48 local authority areas in South Wales. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 59418-2 1976 Preliminary dissolution in tap water proved impractical. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 769752-3 1976 Approximately 10 plaque forming units, concentrated from a volume of 40 liters of seeded tap water could be demonstrated by the rapid method. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 1262774-2 1976 Data are presented for the factors which govern the adherence to the skin and the range of initial impedance and the values obtained at 2, 5, 10 and 20 minutes and with tap water under the electrodes. Water 173-178 nuclear RNA export factor 1 Homo sapiens 169-172 1262774-4 1976 Tap water placed under the electrodes dramatically reduces the initial range of impedance. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 187115-0 1976 Concentration of viruses from large volumes of tap water using pleated membrane filters. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 187115-1 1976 A method is described for the efficient concentration of viruses from large volumes of tap water in relatively short time periods. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 187115-2 1976 Virus in acidified tap water in the presence of aluminum chloride is adsorbed to a 10-inch (ca. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 187115-4 1976 This filter series is capable of efficiently adsorbing virus from greater than 19,000 liters (5,000 gallons) of treated tap water. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 187115-7 1976 Using this procedure, viruses in 1,900 liters (500 gallons) of tap water can be concentrated 100,000-fold in 3 h with an average recovery of 40 to 50%. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 1054766-6 1975 As humidifying fluid only sterile water, possibly fresh tap water, are recommended. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 49948-9 1975 Wash in running tap water for 1 minute. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 1103307-7 1975 The use of tap water for enemas has produced morbidity both from thermal injuries and from electrolyte depletion. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 1055449-0 1975 [Dental health from the water tap? Drinking water fluoridation not illegal any more]. Water 24-29 nuclear RNA export factor 1 Homo sapiens 30-34 4779084-0 1973 Radiostrontium in tap water, January-December 1972. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 1114295-0 1975 [Determination of lead and copper content in tap water in the Poznan Province]. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 4518359-1 1973 In laboratory experiments the acute eye irritation produced by exposure to tap water was not significantly increased when chlorine compounds were added to the water at concentrations of 1 mg./l. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 4748252-1 1973 A defect potentiated by tap water hemodialysis. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 5076790-0 1972 The determination of part-per-billion levels of citric and nitrilotriacetic acids in tap water and sewage effluents. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 4512087-0 1973 A study on the corrosivity of the tap water in central Taiwan. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 4695691-2 1973 Fourteen out of 96 "overnight" tap water samples from five soft water and five hard water towns in England and Wales and from Glasgow (soft water) had lead concentrations of over 0.1 p.p.m. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 4337928-2 1972 Improvement of methodology and application to tap water. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 5066829-0 1972 Treatment of idiopathic hyperhidrosis with iontophoresis of tap water and poldine methosulphate. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 4679882-0 1972 Hemolysis in dialyzed patients: tap water-induced red blood cell metabolic deficiency. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 5198048-0 1969 Radiostrontium in milk and tap water. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 5523836-0 1970 [Preparation of tap-water for irrigation in urology]. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 5122510-0 1971 Radiostrontium in tap water, July-December 1970. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 4324193-5 1971 When tap water was sampled, the amounts of virus adsorbed by the gauze pads were very small, about 2% of the total number of virus particles flowing through the device. Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 4324193-7 1971 Addition of NaCl to tap water produced a much better effect on virus adsorption and recovery by this device, i.e., 47% of the total virus particles in each sample. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 17746032-2 1970 Potential applications include production of potable water from brackish sources or of highly purified water from tap water. Water 103-108 nuclear RNA export factor 1 Homo sapiens 114-117 5988163-0 1966 [An ionite method for obtaining desalted apyrogenic water from tap water]. Water 52-57 nuclear RNA export factor 1 Homo sapiens 63-66 5686206-0 1968 [Acquired methemoglobinemia in infants due to tap water]. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 5187196-0 1967 Radiostrontium in milk and tap water. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 5379483-0 1969 [Hygienic characteristics of organic admixtures in tap water]. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 5993394-0 1966 [To the problem of apyrogenicity of demineralized water obtained from tap-water by means of the ion exchange method]. Water 50-55 nuclear RNA export factor 1 Homo sapiens 70-73 5993394-0 1966 [To the problem of apyrogenicity of demineralized water obtained from tap-water by means of the ion exchange method]. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 5988163-0 1966 [An ionite method for obtaining desalted apyrogenic water from tap water]. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 14155121-3 1964 A simple system is described in which cooled tap water is circulated through an extragastric reservoir, using an applicator modified slightly from the original design described by Wangensteen. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 4160071-0 1965 Staining cells on a membrane filter with Giemsa stock and tap water. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 5858016-2 1965 Iron bacteria in tap water and in the sediment of pipes system]. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 13763653-0 1961 A practical method for culturing coccidial oocysts in tap water. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 13998499-1 1963 Estimates of daily total fluid intake and of tap-water consumption of normal children were made in four dissimilar geographic areas in the United States. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 13998499-2 1963 (Total fluid intake increased and, relatively speaking, tap-water consumption decreased, with age.) Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 13998499-3 1963 Of basic importance in fluoridation programs was the observation that even older children rarely drank as much as 500 ml (about 1 pint) of tap water daily. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 13750878-0 1960 [Bactericidal property of iodine in tap water]. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 13362229-0 1956 Detection of cysts of Endamoeba histolytica in tap water by the use of membrane filter. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 13594017-0 1958 Water intoxication following tap-water enemas. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 13422660-0 1957 [Acid-alcohol resistant non-tuberculous bacilli in tap water]. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 13238123-0 1954 [Determination of the fluorine content of tap water by means of the aquatester]. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 13385813-2 1956 Effect on the pyrogenicity of tap water. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 19993665-16 1947 (c) When the whole cable is wound around the vessel, the concentration of the electrolyte becomes the factor determining the way in which the energy will be dissipated: (1) with tap-water, it is found that no eddy currents can be demonstrated whereas coaxial currents exist; (2) with strong saline solutions the converse holds good; (3) with electrolytes of intermediate concentration both types of currents can be shown to coexist at the periphery while at the centre only coaxial currents can be demonstrated.The fact that eddy currents and coaxial currents could be detected simultaneously and did not, as might be expected, give rise to a resultant, could only be explained by assuming that although eddy currents and coaxial currents coexisted as far as their effects on the pilot lamp were concerned, these two phenomena were not coincident as regards their phase relations. Water 182-187 nuclear RNA export factor 1 Homo sapiens 178-181 18858171-0 1948 An arrangement by which a single water tap may be used to run a distillation in vacuo, a condenser, a constant-level water-bath. Water 33-38 nuclear RNA export factor 1 Homo sapiens 39-42 18152199-0 1949 Some chemical properties of Manila tap water and their relation to corrosion of the distribution system. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 19871071-4 1941 From this fraction the reactive protein separates out on dialysis against tap water. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 18858171-0 1948 An arrangement by which a single water tap may be used to run a distillation in vacuo, a condenser, a constant-level water-bath. Water 117-122 nuclear RNA export factor 1 Homo sapiens 39-42 17732764-0 1946 Semi-continuous Tap-water Aerator. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 21009088-0 1946 Semi-continuous tap-water aerator. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 19871071-5 1941 Following removal of the alcohol-ether-soluble lipids from acute phase serum the reactive protein becomes soluble in tap water, and is no longer precipitable by traces of calcium but still retains its precipitability with the C polysaccharide. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 33962237-0 2021 Field study on the transportation characteristics of PFASs from water source to tap water. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 19599518-0 1910 Note on an Organism Isolated from Washington Tap Water, Aggluginated Readily by the Serum of Typhoid Fever Patients. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 33652280-1 2021 Aluminum (Al) release and deposition in drinking water distribution systems (DWDS) are highly detrimental to tap water quality. Water 49-54 nuclear RNA export factor 1 Homo sapiens 109-112 33652280-1 2021 Aluminum (Al) release and deposition in drinking water distribution systems (DWDS) are highly detrimental to tap water quality. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 33652280-3 2021 The two cities were selected based on the wide disparity reported in pH and turbidity in the finished and tap water qualities, with higher fluctuation of pH (average 8.0) and turbidity (average 0.78 NTU) reported in the northern and southern cities, respectively. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 19872542-9 1930 Leakage around the cell is small because the wall is imbibed with tap water. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 34025370-8 2021 In the other (control) session, they received tap water labeled as tap water. Water 50-55 nuclear RNA export factor 1 Homo sapiens 67-70 33571763-0 2021 New methods based on back propagation (BP) and radial basis function (RBF) artificial neural networks (ANNs) for predicting the occurrence of haloketones in tap water. Water 161-166 nuclear RNA export factor 1 Homo sapiens 157-160 33736356-7 2021 Tap water supply had the lowest global warming impact (0.17 kg CO2-eq. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 33736356-9 2021 The most efficient strategy to reduce the environmental impact of household"s water use is to shift the water consumption from bottled to tap water consumption. Water 78-83 nuclear RNA export factor 1 Homo sapiens 138-141 33736356-9 2021 The most efficient strategy to reduce the environmental impact of household"s water use is to shift the water consumption from bottled to tap water consumption. Water 104-109 nuclear RNA export factor 1 Homo sapiens 138-141 33736356-9 2021 The most efficient strategy to reduce the environmental impact of household"s water use is to shift the water consumption from bottled to tap water consumption. Water 104-109 nuclear RNA export factor 1 Homo sapiens 138-141 33736356-11 2021 day-1 in case of groundwater-based tap water. Water 23-28 nuclear RNA export factor 1 Homo sapiens 35-38 33736356-12 2021 These results provide insights into sustainable water use for multiple consumption patterns and can be used to better frame the environmental benefits of tap water use. Water 48-53 nuclear RNA export factor 1 Homo sapiens 154-157 33736356-12 2021 These results provide insights into sustainable water use for multiple consumption patterns and can be used to better frame the environmental benefits of tap water use. Water 158-163 nuclear RNA export factor 1 Homo sapiens 154-157 34025370-7 2021 The participants drank tap water that was labeled "Lourdes water" (placebo) before a 15-min resting-state scan in one session. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 33736143-7 2021 The concentration in the first flush water tended to decrease with time since the tap installation, and this was significant after 10 years for nickel but not significant for lead. Water 37-42 nuclear RNA export factor 1 Homo sapiens 82-85 34025370-8 2021 In the other (control) session, they received tap water labeled as tap water. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 33885638-0 2021 A fluorescent aptasensor based on berberine for ultrasensitive detection of bisphenol A in tap water. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 33949893-8 2021 RESULTS: Spontaneous preterm birth at 20-31 wk was increased in association with tap water nitrate concentrations during pregnancy of 5 to <10mg/L [odds ratio (OR)=1.47; 95% confidence interval (CI): 1.29, 1.67] and >=10mg/L (OR=2.52; 95% CI: 1.49, 4.26) compared with <5mg/L (as nitrogen). Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 33949893-12 2021 Notably, we estimated modestly increased odds associated with tap water nitrate concentrations of 5 to <10mg/L (below the federal drinking water standard of 10mg/L) relative to <5mg/L. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 33949893-12 2021 Notably, we estimated modestly increased odds associated with tap water nitrate concentrations of 5 to <10mg/L (below the federal drinking water standard of 10mg/L) relative to <5mg/L. Water 139-144 nuclear RNA export factor 1 Homo sapiens 62-65 33585670-3 2021 However, water overuse during hand scrubbing with soap keeping the tap on may put enormous pressure on the already overstretched groundwater resources and households" economic well-being. Water 9-14 nuclear RNA export factor 1 Homo sapiens 67-70 33585670-4 2021 Therefore, this study aimed to determine the overuse of water while scrubbing hands with soap for handwashing when the tap is on amid the COVID-19 pandemic in Bangladesh. Water 56-61 nuclear RNA export factor 1 Homo sapiens 119-122 33585670-8 2021 A single participant, who kept his tap on throughout the handwashing process, overused approximately 1.7L of water per handwash and 14.9L of water per day. Water 109-114 nuclear RNA export factor 1 Homo sapiens 35-38 33585670-8 2021 A single participant, who kept his tap on throughout the handwashing process, overused approximately 1.7L of water per handwash and 14.9L of water per day. Water 141-146 nuclear RNA export factor 1 Homo sapiens 35-38 33585670-9 2021 Hand scrubbing with soap keeping the tap on, raised the overuse of water 13-fold during this pandemic compared to the non-pandemic situation which cost an extra 224.95 BDT (2.65$) per day for 1980 participants. Water 67-72 nuclear RNA export factor 1 Homo sapiens 37-40 33585670-10 2021 Minimize the speed of tap, using automatic taps, and using taps operated by legs might be an effective solution to reduce the water overuse. Water 126-131 nuclear RNA export factor 1 Homo sapiens 22-25 33885638-5 2021 The proposed fluorescent sensing system also exhibited excellent recoveries of 92.4-102.3% in tap water samples and showed good application prospects for the analysis and detection of BPA. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 33508258-5 2021 Notably, the decreased consumption of tap water in the community was significantly associated with increased worry, but time-on-the land was not. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 33523638-3 2021 The results showed that the total concentration level of measured DBPs in wastewater effluents (78.3 mug/L) was higher than that in tap water (56.0 mug/L, p = 0.05), followed by surface water (8.0 mug/L, p < 0.01). Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 33921966-6 2021 Gastrointestinal symptoms predominated and were associated with drinking of contaminated water like tap water or water from communal mobile water tanks, probably because of the contamination of clean water, the disruption of water sanitation, and the inability to maintain home hygiene practices. Water 89-94 nuclear RNA export factor 1 Homo sapiens 100-103 33921966-6 2021 Gastrointestinal symptoms predominated and were associated with drinking of contaminated water like tap water or water from communal mobile water tanks, probably because of the contamination of clean water, the disruption of water sanitation, and the inability to maintain home hygiene practices. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 33921966-6 2021 Gastrointestinal symptoms predominated and were associated with drinking of contaminated water like tap water or water from communal mobile water tanks, probably because of the contamination of clean water, the disruption of water sanitation, and the inability to maintain home hygiene practices. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 33921966-6 2021 Gastrointestinal symptoms predominated and were associated with drinking of contaminated water like tap water or water from communal mobile water tanks, probably because of the contamination of clean water, the disruption of water sanitation, and the inability to maintain home hygiene practices. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 33921966-6 2021 Gastrointestinal symptoms predominated and were associated with drinking of contaminated water like tap water or water from communal mobile water tanks, probably because of the contamination of clean water, the disruption of water sanitation, and the inability to maintain home hygiene practices. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 33921966-6 2021 Gastrointestinal symptoms predominated and were associated with drinking of contaminated water like tap water or water from communal mobile water tanks, probably because of the contamination of clean water, the disruption of water sanitation, and the inability to maintain home hygiene practices. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 33871557-8 2021 Compared with low intakes, high intakes of plain and tap water were associated with lower odds of high BPA concentration (OR: 0.65; 99.95% CI: 0.47, 0.91 and OR: 0.70; 99.95% CI: 0.50, 0.99, respectively). Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 33837446-12 2021 The identification of microplastics larger than 100 microm in size in the treated tap water indicated potential contamination from microplastics in the treatment system, particularly after the sand filtration unit. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 33837446-13 2021 The major characteristics of the microplastics found in treated tap water were similar to those found in freshwater, with 85.6% fragments, 85.1% colorless, and 47.9% made of polyethylene polymer. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 33648644-4 2021 Moreover, the biosensor was successfully employed to determine FN concentration in blind tap water samples obtaining excellent recovery percentages with a time-to-result of only 20 min without any sample pre-treatment. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 33500024-9 2021 Moreover, the PEI-CQDs are also successfully utilized for monitoring the Co2+ content of tap water. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 33751067-2 2021 OBJECTIVE: Two eco-friendly spectrofluorimetric methods were proposed for the determination of three unexpected contaminants in drinking tap water. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 33883730-5 2021 Poly(caprolactone) and poly(lactic acid) containing less than 2 weight per cent enzymes are depolymerized in days, with up to 98 per cent polymer-to-small-molecule conversion in standard soil composts and household tap water, completely eliminating current needs to separate and landfill their products in compost facilities. Water 219-224 nuclear RNA export factor 1 Homo sapiens 215-218 33338936-8 2021 The proposed methods have an admissible precision and accuracy for determination of the two isomers in their binary mixtures in tap water as a real sample. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 33751067-14 2021 HIGHLIGHTS: Both methods were found to be eco-friendly and were successfully applied for the determination of the emerging contaminants in drinking tap water. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 33180282-3 2021 The present study aimed to provide a survey of the existence of enteric viruses: human adenovirus (HAdV), human enteroviruses (hEV), and genotype A rotavirus (GARV) in tap water. Water 172-177 nuclear RNA export factor 1 Homo sapiens 168-171 32631738-10 2021 RESULTS: Tap water did not change spine phantom measurements, but did increase (p < 0.05) total body phantom lean mass 46 g and 89 g with 45 mL and 90 mL, respectively. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 33465449-13 2021 CLINICAL SIGNIFICANCE: Drinking fluoridated tap water is as effective in dental caries prevention as bottled water with acceptable levels of fluoride, with the advantage of being accessible to all. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 33128701-0 2021 Rotavirus Surveillance in Tap Water, Recycled Water, and Sewage Sludge in Thailand: A Longitudinal Study, 2007-2018. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 33128701-1 2021 The objective of this study was to describe the epidemiological and molecular surveillance of rotaviruses in tap water, recycled water, and sewage sludge in Thailand from 2007 to 2018. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 33746392-6 2021 Results revealed that risk factors including drinking tap water and attendance of nurseries, affected the rate of parasitic infection among humans. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 33614462-6 2021 The easiest and readily available rinsing solution is tap water, which fulfils the crucial criteria conveniently in most industrialized countries: purity, sterility, and neutral pH. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 33571202-6 2021 We identified lack of access to tap water (<=98%) as an important risk factor for dengue virus IgG sero-positivity (adjusted Odds Ratio 4.69, 95% C.I. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 33571202-12 2021 Control strategies based on improved access to a reliable supply of tap water plus focal intervention in intra-urban heat islands prior to the dengue season could not only lead to a reduction in mosquito abundance but also eliminate the reservoir of dengue virus clearly circulating at low levels in winter in socio-economically disadvantaged areas. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 33547895-4 2021 RESULTS: High incidence rates were significantly associated with precarious water service index (0-25% coverage) and offstandard faecal coliforms index for tap water (5-50% and 75-100% of samples tested). Water 160-165 nuclear RNA export factor 1 Homo sapiens 156-159 33758757-1 2021 Background: The main objective of this study was to investigate the logics behind tendencies towards bottled drinking water usage in spite of availability of treated tap water. Water 170-175 nuclear RNA export factor 1 Homo sapiens 166-169 33758757-9 2021 The perceived unreliability of tap water quality was the main reason of bottled water consumption among 74% of the respondents. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 33758757-9 2021 The perceived unreliability of tap water quality was the main reason of bottled water consumption among 74% of the respondents. Water 80-85 nuclear RNA export factor 1 Homo sapiens 31-34 33045559-0 2021 Tap water contamination: Multiclass endocrine disrupting compounds in different housing types in an urban settlement. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 33265044-0 2021 Combined effects of seasonality and stagnation on tap water quality: Changes in chemical parameters, metabolic activity and co-existence in bacterial community. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 33265044-1 2021 In drinking water distribution pipeline systems, the tap water quality is regulated by several biotic and abiotic factors, which can threaten the health of consumers. Water 12-17 nuclear RNA export factor 1 Homo sapiens 53-56 33265044-1 2021 In drinking water distribution pipeline systems, the tap water quality is regulated by several biotic and abiotic factors, which can threaten the health of consumers. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 33265044-2 2021 Stagnation is inevitable in the water distribution pipeline however, the combined effects of seasonal changes and stagnation on tap water quality are not well understood. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 33265044-4 2021 The results showed that the tap water quality deteriorated after overnight stagnation, with up to a 2.7-fold increase in the total iron concentrations. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 33265044-12 2021 Altogether, the overall findings from the present work provide novel insights into how the quality of tap water quality impacted by the seasonal changes and overnight stagnation. Water 106-111 nuclear RNA export factor 1 Homo sapiens 102-105 33045559-1 2021 Contamination of endocrine disrupting compounds (EDCs) in tap water is an emerging global issue, and there are abundant influencing factors that have an ambivalent effect on their transportation and fate. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 33045559-3 2021 Thus, this study analyzed 18 multiclass EDCs in tap water from different housing types (i.e., landed and high-rise) and the associated health risks. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 33045559-4 2021 Sample analyses revealed the presence of 16 EDCs, namely hormones (5), pharmaceuticals (8), a pesticide (1), and plasticizers (2) in tap water, with the prevalent occurrence of bisphenol A up to 66.40 ng/L in high-rise housing. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 33045559-5 2021 The presence of caffeine and sulfamethoxazole distribution in tap water was significantly different between landed and high-rise housings (t(152) = -2.298, p = 0.023 and t(109) = 2.135, p = 0.035). Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 33045559-6 2021 Moreover, the salinity and conductivity of tap water in high-rise housings were significantly higher compared to those in landed housings (t(122) = 2.411, p = 0.017 and t(94) = 2.997, p = 0.003, respectively). Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 33279831-0 2021 Application of Capsid Integrity (RT-)qPCR to Assessing Occurrence of Intact Viruses in Surface Water and Tap Water in Japan. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 33279831-6 2021 In the tap water samples, most of the target viruses were not detected by conventional (RT-)qPCR, except for PMMoV (9%) and AiV (5%). Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 33279831-9 2021 In addition to being abundant in surface water, PMMoV was detected in tap water, including PMMoV with intact capsids. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 33279831-10 2021 Thus, the absence of intact PMMoV may be used to guarantee the viral safety of tap water produced from surface water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 33279831-10 2021 Thus, the absence of intact PMMoV may be used to guarantee the viral safety of tap water produced from surface water. Water 111-116 nuclear RNA export factor 1 Homo sapiens 79-82 32889273-1 2021 As a new type of potentially threatening pollutant, microplastics are widely distributed in water and may come into contact with the humans through tap water. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 33499674-3 2022 About 72% of the population used tap water for drinking and cooking. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 33499674-6 2022 These data indicated that fluoride concentration in tap water is higher than bottled water and estimated micronutrients intake is related to urinary fluoride. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 32911162-10 2021 Tap water with MIB had the lowest acceptability mean score (3.43 +- 1.74), while flavorless bottled water had the highest acceptability mean score (6.23 +- 1.47). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32721640-8 2021 Besides, we also demonstrated that this system is able to detect PCB77 in tap water, environmental water and milk. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 33438270-4 2021 Overall, 81.5% of respondents reported daily well water consumption (i.e., tap water). Water 50-55 nuclear RNA export factor 1 Homo sapiens 75-78 33438270-4 2021 Overall, 81.5% of respondents reported daily well water consumption (i.e., tap water). Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 32854008-0 2021 Addition of lemon before boiling chlorinated tap water: A strategy to control halogenated disinfection byproducts. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 33390526-0 2021 Characteristics of Raw and Acid-Activated Bentonite and Its Application for Improving Electrical Conductivity of Tap Water. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 33390526-1 2021 This study aimed to investigate the characteristics of acid-activated bentonite by focusing on its capability of improving the quality of tap water used during wire electrical discharge machining. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 33390526-6 2021 The electrical conductivity of tap water was decreased significantly due to bentonite activated with sulfuric acid, nitric acid, and phosphoric acid solution (removal percentage of approximately 31-39%), as compared to that due to RB. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 33390526-9 2021 These results indicated that acid-activated bentonite can be produced from RB via acid activation and that it can be used to decrease electrical conductivity of tap water. Water 165-170 nuclear RNA export factor 1 Homo sapiens 161-164 32854008-2 2021 A previous study has reported that the addition of ascorbate to tap water before boiling could significantly decrease the concentration of overall halo-DBPs in the boiled water. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 32854008-2 2021 A previous study has reported that the addition of ascorbate to tap water before boiling could significantly decrease the concentration of overall halo-DBPs in the boiled water. Water 171-176 nuclear RNA export factor 1 Homo sapiens 64-67 32854008-3 2021 Since the fruit lemon is rich in vitamin C (i.e., ascorbic acid), adding it to tap water followed by heating and boiling in an effort to decrease levels of halo-DBPs was investigated in this study. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 32854008-6 2021 Our results show that the "Lemon + Boiling" approach substantially decreased the concentrations of halo-DBPs and the cytotoxicity of tap water. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 32854008-7 2021 This strategy could be applied to control halo-DBPs, as well as to lower the adverse health effects of halo-DBPs on humans through tap water ingestion. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 33068851-3 2021 Perfluorooctanoic acid (PFOA) was found to be predominant, concentrations of which ranged from 40.4 to 845 ng/mL in serum, from 2.88 to 19.3 ng/L in tap water, from 4.40 to 189 ng/g in soil, and accounting for 84.1-98.6%, 15.9-79.8%, and 73.8-96.7% of the total PFASs, respectively. Water 153-158 nuclear RNA export factor 1 Homo sapiens 149-152 33317121-6 2020 The participants who consumed fluoridated (>=0.7 mg/L) tap water (n = 560, 16%) versus those who did not had 36% (95% CI: 22, 51) higher plasma fluoride. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 33374345-11 2020 Recoveries calculated for pharmaceutical products and tap water measurements were in the range 102-105%, which confirms the accuracy of the developed. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 33374345-12 2020 The applicability of the method was confirmed by analysis of pharmaceutical products and tap water samples. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 33322071-6 2020 In the case of the modified composition, it is noted that the samples immersed in tap water were characterized by a higher strength than in acidic environments. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 33104816-8 2021 Whereas, tap water and effervescent tablets had 15% and 49% efficiency, respectively. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 32841807-5 2021 Higher concentrations (median: 39.3 ng/L; range: 1.20-127) of selected pesticides were found in tap water from Hanoi than those from four other provinces studied (5.49 ng/L; 4.73-66.8 ng/L). Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 32841807-7 2021 The calculated risks from pesticide exposure through ingestion of tap water by the general populations were low. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 33396394-5 2020 About 70% of responding households possessed their own water sources, mostly shallow tube-wells, and owners were less likely to choose tap water for drinking purpose than nonowners. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 33317121-9 2020 The consumption of fluoridated tap water and tea substantially increases plasma fluoride concentrations in children. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 32919261-2 2020 The aim of this work was to characterize the bacterial communities in tap water and bottled mineral water, the two predominant sources of drinking water in modern societies. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 32919261-7 2020 Significant differences were observed between mineral and tap water, with a general dominance of Alphaproteobacteria (mainly the genus Blastomonas) in tap water and Gammaproteobacteria in mineral water with Acidovorax being the dominant genus in 3 out of 7 mineral water brands. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 32919261-7 2020 Significant differences were observed between mineral and tap water, with a general dominance of Alphaproteobacteria (mainly the genus Blastomonas) in tap water and Gammaproteobacteria in mineral water with Acidovorax being the dominant genus in 3 out of 7 mineral water brands. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 32919261-7 2020 Significant differences were observed between mineral and tap water, with a general dominance of Alphaproteobacteria (mainly the genus Blastomonas) in tap water and Gammaproteobacteria in mineral water with Acidovorax being the dominant genus in 3 out of 7 mineral water brands. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 32631653-0 2020 Association of availability of tap water system with admission rate after 30 days among burn injury patients: A nationwide population-based study. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 32593940-11 2020 This approach also shows excellent performance in monitoring Pb2+ in tap water and lake water. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 32631653-1 2020 BACKGROUND: We investigated whether the availability of a tap water supply system is associated with lowering the admission rate 30 days after burn injury. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 32631653-10 2020 The advantageous effect of a well-equipped tap water system on a lower admission rate in burn patients was independent of comorbidities. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 32631653-11 2020 CONCLUSIONS: The results of this study demonstrated the association between lowering the admission rate at 30 days in burn patients in Taiwan and using a well-equipped tap water system. Water 172-177 nuclear RNA export factor 1 Homo sapiens 168-171 32631653-12 2020 It also could offer important information to the government for enhancing the availability of tap water system in those areas lack adequate tap water supply which is useful to protect burn patients from following admission. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 32631653-12 2020 It also could offer important information to the government for enhancing the availability of tap water system in those areas lack adequate tap water supply which is useful to protect burn patients from following admission. Water 98-103 nuclear RNA export factor 1 Homo sapiens 140-143 32631653-12 2020 It also could offer important information to the government for enhancing the availability of tap water system in those areas lack adequate tap water supply which is useful to protect burn patients from following admission. Water 144-149 nuclear RNA export factor 1 Homo sapiens 94-97 32631653-12 2020 It also could offer important information to the government for enhancing the availability of tap water system in those areas lack adequate tap water supply which is useful to protect burn patients from following admission. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 33312665-0 2020 Health risk assessment of selected metals through tap water consumption in Upper Silesia, Poland. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 33028492-6 2020 In the OP rats, the plasma concentrations in the groups given erlotinib in apple juice and in HCl (pH 3.7) were significantly higher than in the tap water group in the initial phase of absorption. Water 149-154 nuclear RNA export factor 1 Homo sapiens 145-148 33254200-5 2020 Tap water was administered through the sheath to create sufficient intraluminal pressure to manipulate devices and acquire digital subtraction angiography (DSA). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32227362-0 2020 Prevalence and seasonal variation of Acanthamoeba in domestic tap water in greater Sydney, Australia. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 32227362-1 2020 BACKGROUND: This study examined the prevalence of free-living Acanthamoeba in domestic tap water in the greater Sydney region, Australia, and determined any seasonal variation in prevalence. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 32227362-12 2020 CONCLUSION: The prevalence of free-living Acanthamoeba characterised morphologically in domestic tap water of the greater Sydney region was higher than expected, especially considering the low incidence of Acanthamoeba keratitis in Australia. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 32574922-8 2020 IMI and its degradates were found in the tap water samples treated conventionally (range: 1.17-32.0 ng/L for IMI; 0.57-7.00 ng/L for DN-IMI; 0.58-4.50 ng/L for IMI-urea; 0.04-0.65 ng/L for DN-IMI-olefin; < method detection limit [MDL]-0.80 ng/L for IMI-olefin; < MDL-0.35 ng/L for 5-OH-IMI). Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 32707319-11 2020 Therefore, boiling and domestic filtering of tap water may be recommended for the removal of HALs prior to consuming tap water. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 32707319-11 2020 Therefore, boiling and domestic filtering of tap water may be recommended for the removal of HALs prior to consuming tap water. Water 49-54 nuclear RNA export factor 1 Homo sapiens 117-120 32707319-11 2020 Therefore, boiling and domestic filtering of tap water may be recommended for the removal of HALs prior to consuming tap water. Water 121-126 nuclear RNA export factor 1 Homo sapiens 45-48 32707319-11 2020 Therefore, boiling and domestic filtering of tap water may be recommended for the removal of HALs prior to consuming tap water. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 33328368-3 2020 The goal of this project was to assess the cost-benefit of POU water treatment at the tap in terms of protection from microbes in drinking water. Water 63-68 nuclear RNA export factor 1 Homo sapiens 86-89 33328368-3 2020 The goal of this project was to assess the cost-benefit of POU water treatment at the tap in terms of protection from microbes in drinking water. Water 139-144 nuclear RNA export factor 1 Homo sapiens 86-89 32641662-0 2020 Non-tuberculous Mycobacterial Pseudo-outbreak of an Intestinal Culture Specimen Caused by a Water Tap in an Endoscopy Unit. Water 92-97 nuclear RNA export factor 1 Homo sapiens 98-101 32641662-8 2020 NTM were detected in the tap water used to prepare the antifoaming solution in the endoscopy unit. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 33312665-1 2020 The research focused on assessing the risk to human health resulting from the content of selected Cr, Co, Mn, Cu, Ni, Pb, As, Zn and Sr metals in tap water supplied by Upper Silesia Water Plant to the inhabitants of the Upper Silesia region (Poland). Water 150-155 nuclear RNA export factor 1 Homo sapiens 146-149 33312665-1 2020 The research focused on assessing the risk to human health resulting from the content of selected Cr, Co, Mn, Cu, Ni, Pb, As, Zn and Sr metals in tap water supplied by Upper Silesia Water Plant to the inhabitants of the Upper Silesia region (Poland). Water 182-187 nuclear RNA export factor 1 Homo sapiens 146-149 33312665-6 2020 The chronic daily intake (CDI), hazard quotient (HQ) and hazard index (HI) results for non-carcinogenic risk assessment of metals in tap water has been assessed. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 33312665-9 2020 HI values were also less than 1, that meaning that the analyzed tap water is safe for human consumption. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 33312665-10 2020 The concentration of As, Cr, Cu, Mn and Ni in analyzed tap water is in accordance with Polish and international requirements. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 33195405-0 2020 Highlighting the Importance of Water Alkalinity Using Phosphate Buffer Diluted With Deionized, Double Distilled and Tap Water, in Lowering Oxidation Effects on Human Hemoglobin Ozonated at High Ozone Concentrations in vitro. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 32563866-0 2020 The identification of halogenated disinfection by-products in tap water using liquid chromatography-high resolution mass spectrometry. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 32563866-1 2020 In this paper, a comprehensive method for the identification of the unknown halogenated DBPs (X-DBPs, X = Cl, Br, and I) in the tap water of Wuhan, China via liquid chromatography-high resolution mass spectrometry (LC-HRMS) was developed. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 32758933-0 2020 Associations between UK tap water and gut microbiota composition suggest the gut microbiome as a potential mediator of health differences linked to water quality. Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 32758933-0 2020 Associations between UK tap water and gut microbiota composition suggest the gut microbiome as a potential mediator of health differences linked to water quality. Water 148-153 nuclear RNA export factor 1 Homo sapiens 24-27 32758933-1 2020 Tap water composition has been widely linked to differences in human health, however the biological pathways underlying this association are less clearly defined. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32758933-9 2020 These results support the hypothesis that the gut microbiota could mediate the effects of tap water composition on host health, warranting further investigation into tap-water as an influencer of microbiota composition. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 32758933-9 2020 These results support the hypothesis that the gut microbiota could mediate the effects of tap water composition on host health, warranting further investigation into tap-water as an influencer of microbiota composition. Water 170-175 nuclear RNA export factor 1 Homo sapiens 166-169 33195405-8 2020 This could be explained by the presence of water alkalinity or bicarbonate ions in tap water, which can scavenge free radicals and reduce Hb oxidation/oligomerization. Water 43-48 nuclear RNA export factor 1 Homo sapiens 83-86 33195405-8 2020 This could be explained by the presence of water alkalinity or bicarbonate ions in tap water, which can scavenge free radicals and reduce Hb oxidation/oligomerization. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 33195405-9 2020 Therefore, it was concluded that Hb could best withstand high concentrations of ozone in the presence of the undiluted 50 mM phosphate buffer followed by phosphate buffer diluted with tap water, containing bicarbonate ions. Water 188-193 nuclear RNA export factor 1 Homo sapiens 184-187 33082440-4 2020 Triclosan (an antimicrobial agent) and 4-octylphenol (a plasticizer) were only detected in the tap water (up to 9.74 and 0.44 ng/L, respectively). Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 33082440-6 2020 Bisphenol A was observed to be highest in tap water at 66.40 ng/L (detection: 100%; median concentration: 0.28 ng/L). Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 33082440-7 2020 There was a significant difference in triclosan contamination between the river and tap water (p < 0.001). Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 33098340-4 2020 Ultralow PFS concentrations (0.5 ng/L of PFOS; 0.4 ng/L of PFHxS) were detected in preconcentrated tap water containing PFSs. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 32623220-9 2020 Consumers may unknowingly be degrading their indoor air quality when using tap water of acceptable drinking water quality as humidifier fill water. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 32897055-7 2020 We validate our methods by demonstrating the measurement of the acidity of fruit-flavored drinks, the alkalinity of tap water and the carboxylate content of nanocellulose dispersions. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 33020393-6 2020 Moreover, in Bissau, the levels of faecal contamination in piped water increased from the holes to the consumer (tap/fountain). Water 65-70 nuclear RNA export factor 1 Homo sapiens 113-116 32556996-0 2020 National screening study investigating nine phthalates and one adipate in raw and treated tap water in France. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 32556996-9 2020 In tap water, the most frequently detected compound was DBP, at a maximum concentration of 1300 ng/L. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 32623220-9 2020 Consumers may unknowingly be degrading their indoor air quality when using tap water of acceptable drinking water quality as humidifier fill water. Water 108-113 nuclear RNA export factor 1 Homo sapiens 75-78 32623220-9 2020 Consumers may unknowingly be degrading their indoor air quality when using tap water of acceptable drinking water quality as humidifier fill water. Water 108-113 nuclear RNA export factor 1 Homo sapiens 75-78 33095189-3 2020 In order to make up for this deficiency, tap water was selected to carry out RBW and PBW experiments independently. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 32673906-12 2020 N-desmethyl-acetamiprid was more likely to be detected in children who drank more tap water. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 32673906-15 2020 Tap water and fresh vegetables were potential sources. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 33095189-4 2020 The quality changes of RBW and PBW show very similar trends that are not as great as might be imagined, and both are impacted by the tap water quality and the physiochemical effects. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 33095189-6 2020 The results show that tap water will be still safe and potable after being frequently boiled or after having undergone prolonged boiling, as long as it satisfies the sanitary standards of drinking water prior to heating. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 33095189-6 2020 The results show that tap water will be still safe and potable after being frequently boiled or after having undergone prolonged boiling, as long as it satisfies the sanitary standards of drinking water prior to heating. Water 197-202 nuclear RNA export factor 1 Homo sapiens 22-25 32940115-4 2021 Fluoride content in youth"s household tap water samples was measured electrometrically with ion-specific electrodes and designated low (<0.6 mg/L) or about optimal (0.6 to 1.2 mg/L). Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 32940115-0 2021 Associations between Household Water Fluoridation Status and Plain Tap or Bottled Water Consumption. Water 31-36 nuclear RNA export factor 1 Homo sapiens 67-70 32940115-6 2021 We used binomial regression models to estimate adjusted prevalence ratios (APRs) and 95% CIs for consuming plain tap water (including tap only or both tap and bottled) and consuming only bottled water as related to household water fluoride content (low or about optimal) and sociodemographic characteristics. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 32917102-6 2021 The mean lead concentration in tap water was 8.3 parts per billion, with 6% of sample testing above the Environmental Protection Agency"s action level. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 32940115-11 2021 CONCLUSION: Half of youth consumed plain tap water on a given day. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 32940115-14 2021 KNOWLEDGE TRANSFER STATEMENT: Half of US youth consumed plain tap water on a given day. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 32940115-17 2021 Our findings add support for the need to identify and address barriers to tap water consumption and promote health benefits of fluoridation. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 32957290-0 2020 Effects of ascorbate and carbonate on the conversion and developmental toxicity of halogenated disinfection byproducts during boiling of tap water. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 32957290-2 2020 Humans are unavoidably exposed to halogenated DBPs via tap water ingestion. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 32957290-3 2020 Boiling of tap water has been found to significantly reduce the concentrations of halogenated DBPs. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 32957290-5 2020 Adding ascorbate removed the chlorine residual in tap water and thus prevented the formation of more halogenated DBPs in the boiling process. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 32957290-6 2020 Adding carbonate elevated pH of tap water and consequently enhanced the hydrolysis (dehalogenation) of halogenated DBPs or led to the formation of more trihalomethanes that might volatilize to air during the boiling process. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 32957290-8 2020 The results showed that adding a tiny amount of sodium ascorbate or carbonate (2.5-5.0 mg/L) to tap water followed by boiling for 5 min reduced the developmental toxicity of tap water to a substantially lower level than boiling only. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 32957290-8 2020 The results showed that adding a tiny amount of sodium ascorbate or carbonate (2.5-5.0 mg/L) to tap water followed by boiling for 5 min reduced the developmental toxicity of tap water to a substantially lower level than boiling only. Water 100-105 nuclear RNA export factor 1 Homo sapiens 174-177 32957290-8 2020 The results showed that adding a tiny amount of sodium ascorbate or carbonate (2.5-5.0 mg/L) to tap water followed by boiling for 5 min reduced the developmental toxicity of tap water to a substantially lower level than boiling only. Water 178-183 nuclear RNA export factor 1 Homo sapiens 96-99 32957290-8 2020 The results showed that adding a tiny amount of sodium ascorbate or carbonate (2.5-5.0 mg/L) to tap water followed by boiling for 5 min reduced the developmental toxicity of tap water to a substantially lower level than boiling only. Water 178-183 nuclear RNA export factor 1 Homo sapiens 174-177 32957290-9 2020 The addition of sodium ascorbate or carbonate to tap water in household could be realized by preparing them in tiny pills. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 32957290-10 2020 This study suggests simple and effective methods to reduce the adverse effects of halogenated DBPs on humans through tap water ingestion. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 33911351-8 2020 About 40 ml of tap water was collected in each chamber. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 32100241-2 2020 The traditional method to control dust problem is to spray roads with tap water. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 32100241-5 2020 In addition, the saved tap water can be used for production and life, thereby obtaining additional benefits. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 32100241-9 2020 The total benefit of using reclaimed water was about 1.30-1.80 times that of using tap water, and the net benefit was 4.65-7.17 times. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 32717657-5 2020 Furthermore, 151 tap water samples from 51 locations range between 0.70404 to 0.71385 (DeltaSrmax-min=0.00981). Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 32717657-6 2020 Overall, small variations in the hair and tap water samples collected from individual locations were recorded (DeltaSrmax-min=0.00041 and 0.00034 respectively). Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 32717657-7 2020 Despite the fact that Mexico is one of the largest bottled water consumers in the world, the 87Sr/86Sr ratios of human hair and tap water correlated strongly (R2=0.87 for location averages and R2=0.80 when using individual data points). Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 32829397-0 2021 Tap Water Avoidance Decreases Rates of Hospital-Onset Pulmonary Nontuberculous Mycobacteria. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32662596-8 2020 It was successfully applied to detect trace polycyclic aromatic hydrocarbons in some real water samples, including tap water, snow water and domestic sewage. Water 90-95 nuclear RNA export factor 1 Homo sapiens 115-118 32662596-8 2020 It was successfully applied to detect trace polycyclic aromatic hydrocarbons in some real water samples, including tap water, snow water and domestic sewage. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 32662596-8 2020 It was successfully applied to detect trace polycyclic aromatic hydrocarbons in some real water samples, including tap water, snow water and domestic sewage. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 32829391-0 2021 Tap Water Avoidance Decreases Rates of Hospital-Onset Pulmonary Nontuberculous Mycobacteria - a call for water Management in Healthcare. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32829391-0 2021 Tap Water Avoidance Decreases Rates of Hospital-Onset Pulmonary Nontuberculous Mycobacteria - a call for water Management in Healthcare. Water 105-110 nuclear RNA export factor 1 Homo sapiens 0-3 32770131-2 2020 Promoting the efficient use of tap water can contribute to sustainable drinking water management and progress towards Sustainable Development Goals. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 32361454-5 2020 Tap water 87Sr/86Sr from the Netherlands range from 0.70837 to 0.71278 (DeltaSrmax-min = 0.0044) and modern human enamel from 0.70847 to 0.70995 (DeltaSrmax-min = 0.0015). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32831847-12 2020 These findings not only indicate the presence of antibiotic-resistant virulent Vibrio species from dam, borehole, and tap water samples that could pose a health risk to humans who either come in contact with or consume water but also present these lytic phages as alternative agents that can be exploited for biological control of these pathogenic strains. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 32770131-2 2020 Promoting the efficient use of tap water can contribute to sustainable drinking water management and progress towards Sustainable Development Goals. Water 80-85 nuclear RNA export factor 1 Homo sapiens 31-34 32770131-5 2020 The presence of residual chlorine in tap water, connected to municipal water supply, inactivates pathogenic microorganisms and prevents recontamination. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 32770131-5 2020 The presence of residual chlorine in tap water, connected to municipal water supply, inactivates pathogenic microorganisms and prevents recontamination. Water 71-76 nuclear RNA export factor 1 Homo sapiens 37-40 32770131-6 2020 However, adding chlorine to tap water may affect the organoleptic properties of drinking water. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 32770131-6 2020 However, adding chlorine to tap water may affect the organoleptic properties of drinking water. Water 89-94 nuclear RNA export factor 1 Homo sapiens 28-31 32770131-7 2020 On the other hand, the use of point-of-use (POU) water dispensers, which provides an additional treatment step on tap water, is not energy-efficient. Water 49-54 nuclear RNA export factor 1 Homo sapiens 114-117 32770131-7 2020 On the other hand, the use of point-of-use (POU) water dispensers, which provides an additional treatment step on tap water, is not energy-efficient. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 32770131-8 2020 A randomized, double-blind water taste test was conducted in the Taipei metropolis to assess whether tap water from public drinking fountains and filtered water from POU water dispensers have similar organoleptic properties. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 32770131-8 2020 A randomized, double-blind water taste test was conducted in the Taipei metropolis to assess whether tap water from public drinking fountains and filtered water from POU water dispensers have similar organoleptic properties. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 32770131-8 2020 A randomized, double-blind water taste test was conducted in the Taipei metropolis to assess whether tap water from public drinking fountains and filtered water from POU water dispensers have similar organoleptic properties. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 32220691-1 2020 The present work reported a high-throughput strategy for the analysis of 21 perfluorinated compounds (PFCs) in drinking water, tap water, river water and plant effluent from southern China by supramolecular solvent (SUPARS) vortex-mixed microextraction combined with high performance liquid chromatography-Orbitrap high resolution mass spectrometry (HPLC-Orbitrap HRMS). Water 131-136 nuclear RNA export factor 1 Homo sapiens 127-130 32199168-0 2020 Occurrence and identification of microplastics in tap water from China. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 32199168-2 2020 However, up to now, microplastic contamination in tap water has only been investigated by few studies. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 32199168-5 2020 The amount of microplastics in tap water varied from 440 +- 275 particles L-1. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 32199168-6 2020 Particles smaller than 50 mum significantly predominated in most of the tap water samples. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 32199168-7 2020 Further, according to the shape of these particles, fragments, fibers and spheres were found in tap water samples, while fragments were the most abundant morphotype in most samples. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 32199168-9 2020 Based on this investigation, drinking water treatment plants seemingly have to face the problem of microplastic pollution in tap water due to their potential eco-toxicological effects on humans. Water 38-43 nuclear RNA export factor 1 Homo sapiens 125-128 32199168-9 2020 Based on this investigation, drinking water treatment plants seemingly have to face the problem of microplastic pollution in tap water due to their potential eco-toxicological effects on humans. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 32533304-2 2020 While many studies have investigated microorganisms in the air and dust, tap water, another major input of microbial propagules, has received far less attention. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 32533304-12 2020 Microbiota of water-related indoor habitats mainly originates from tap water. Water 14-19 nuclear RNA export factor 1 Homo sapiens 67-70 32533304-12 2020 Microbiota of water-related indoor habitats mainly originates from tap water. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 32430919-1 2020 Microplastics are ubiquitous in our environment and are found in rivers, streams, oceans, and even tap water. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 32484124-0 2020 The Legionella contamination of tap water in a brand-new hospital in Japan before patients move in. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 32217410-2 2020 A nationwide survey about ATZ and its degradates (ATZs) in tap water from 31 provinces in 7 regions of mainland China and Hong Kong was conducted during June 2019. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 32217410-5 2020 The predominant compounds of ATZs in tap water were ATZ and DEA, with a detection frequency of 99.5% and 98.0%, respectively, followed by ATZ-OH (87.3%), DACT (84.0%), and DIA (78.1%). Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 32793876-0 2020 An overlooked route of inhalation exposure to tap water constituents for children and adults: Aerosolized aqueous minerals from ultrasonic humidifiers. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 32793876-5 2020 When filled with tap water, water evaporated from emitted aerosols to form submicron particles that became essentially "dried tap water" with median size 146 nm and mean concentration of 211 mug-total elements/m3-air including 35 mug-calcium/m3-air in a room of 33.5 m3 and air exchange rate at ~0.8 hr-1. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 32793876-5 2020 When filled with tap water, water evaporated from emitted aerosols to form submicron particles that became essentially "dried tap water" with median size 146 nm and mean concentration of 211 mug-total elements/m3-air including 35 mug-calcium/m3-air in a room of 33.5 m3 and air exchange rate at ~0.8 hr-1. Water 28-33 nuclear RNA export factor 1 Homo sapiens 17-20 32793876-5 2020 When filled with tap water, water evaporated from emitted aerosols to form submicron particles that became essentially "dried tap water" with median size 146 nm and mean concentration of 211 mug-total elements/m3-air including 35 mug-calcium/m3-air in a room of 33.5 m3 and air exchange rate at ~0.8 hr-1. Water 28-33 nuclear RNA export factor 1 Homo sapiens 126-129 32793876-5 2020 When filled with tap water, water evaporated from emitted aerosols to form submicron particles that became essentially "dried tap water" with median size 146 nm and mean concentration of 211 mug-total elements/m3-air including 35 mug-calcium/m3-air in a room of 33.5 m3 and air exchange rate at ~0.8 hr-1. Water 28-33 nuclear RNA export factor 1 Homo sapiens 17-20 32793876-5 2020 When filled with tap water, water evaporated from emitted aerosols to form submicron particles that became essentially "dried tap water" with median size 146 nm and mean concentration of 211 mug-total elements/m3-air including 35 mug-calcium/m3-air in a room of 33.5 m3 and air exchange rate at ~0.8 hr-1. Water 28-33 nuclear RNA export factor 1 Homo sapiens 126-129 32498189-0 2020 Spatial variation of 2,4-D and MCPA in tap water and groundwater from China and their fate in source, treated, and tap water from Wuhan, Central China. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 32498189-6 2020 The cumulative concentration of CPHs (SigmaCPHs) in tap water in China was up to 125 ng/L (median: 1.38 ng/L), and regional variations were found for SigmaCPHs. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 32498189-12 2020 Seasonal variations were found in SigmaCPHs in tap water from Wuhan, with the highest found in July (median: 21.2 ng/L), and the lowest in October (1.96 ng/L). Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 32498189-15 2020 Moreover, this study provides an overview of SigmaCPHs in tap water for many areas in China. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 32608904-0 2020 [Occurrence and Prediction Model of Disinfection By-Products in Tap Water]. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 32608904-3 2020 The purpose of the work was to obtain knowledge on the occurrence of DBPs in tap water and boiled water taken from the same pipe, to establish a statistical model to predict DBPs information in tap water based on physicochemical parameters, and to evaluate carcinogenic and non-carcinogenic risks caused by DBPs on a predictional level. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 32608904-5 2020 The detection rate of target DBPs in tap water was 100% and the concentrations varied in the ranges of 10.12-28.39, 0.98-5.19, and 2.65-7.83 mug L-1, respectively. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 32608904-11 2020 Based on the correlation between the physicochemical parameters and DBPs, a multiple linear regression prediction model of THMs was established, with deviation less than 10.00%, which can be used for the prediction of THMs in tap water. Water 230-235 nuclear RNA export factor 1 Homo sapiens 226-229 32608904-14 2020 The carcinogenic risk caused mainly by THMs and bromodicloromethane (BDCM) contributed the highest cancer risk in tap water, while for boiled water, trichloromethane (TCM) was found to contribute the highest cancer and non-carcinogenic risk. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 32593289-1 2020 BACKGROUND: Most studies have reported that suicide mortality rates are negatively associated with lithium levels in tap water; however, a few studies showed either no association or a positive association. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 32145576-0 2020 Spatial variation of fipronil and its derivatives in tap water and ground water from China and the fate of them during drinking water treatment in Wuhan, central China. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 32145576-4 2020 The sum concentrations of FPs (SigmaFPs) in the tap water in China ranged from not detected (ND) to 5.07 (median: 0.03 ng/L), with FP found in 55.3% of the samples, and other targets <= 50.0%. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 32145576-6 2020 Similar SigmaFPs values were found for ground water and tap water. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 32145576-10 2020 Higher concentration of SigmaFPs in tap water was observed in July (median: 0.04 ng/L) compared to that in October (ND). Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 32997445-6 2020 She proved the efficiency of tap water fluoridation in caries prevention through a comparative study on children from schools in Wroclaw and Malbork, where the fluoride concentrations were 0.1 mg/L and 3.2 mg/L, respectively. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 32593289-2 2020 Thus, the association between suicide mortality and lithium levels in tap water remains controversial. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 32593289-3 2020 To clarify the association, our study evaluated the association between lithium levels in tap water and suicide mortality rates in Miyazaki Prefecture of Japan, after adjusting for confounding factors. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 32593289-6 2020 Weighted least-squares regression analysis, adjusted for the size of each municipality"s population, was used to investigate the association between lithium levels in tap water and suicide SMRs. Water 171-176 nuclear RNA export factor 1 Homo sapiens 167-170 32641201-10 2020 Conclusions: Sequence type, virulence properties, and antibiotic resistance vary in Aeromonas isolates from clinical patients, tap water systems, and food. Water 131-136 nuclear RNA export factor 1 Homo sapiens 127-130 32208246-0 2020 Perception of tap water quality: Assessment of the factors modifying the links between satisfaction and water consumption behavior. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 32208246-0 2020 Perception of tap water quality: Assessment of the factors modifying the links between satisfaction and water consumption behavior. Water 104-109 nuclear RNA export factor 1 Homo sapiens 14-17 32208246-1 2020 Perception of tap water is subject to a wide range of factors and interactions. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 32208246-7 2020 Results show that drinking water quality could be loosely linked with overall satisfaction with tap water. Water 27-32 nuclear RNA export factor 1 Homo sapiens 96-99 32208246-7 2020 Results show that drinking water quality could be loosely linked with overall satisfaction with tap water. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 32208246-8 2020 The water consumption profile was strongly linked with satisfaction levels related to the taste, odor and color of tap water. Water 4-9 nuclear RNA export factor 1 Homo sapiens 115-118 32208246-8 2020 The water consumption profile was strongly linked with satisfaction levels related to the taste, odor and color of tap water. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 32203798-7 2020 More importantly, the sensor has a high recovery rate when it is used to detect nitrite in tap water, mineral water, and sausage, indicating the feasibility of using this sensor in practical applications. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 32414133-7 2020 Tap-water samples were analyzed for the determination of metals by standard addition methodology with good accuracy, by using a low-cost and easily disposable paper-based electrochemical platform. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32538598-8 2020 Wound irrigation with normal saline or tap water is recommended after foreign body removal. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 33313440-0 2020 Tapping Out: Influence of Organoleptic and Perceived Health Risks on Bottled Versus Municipal Tap Water Consumption Among Obese, Low Socioeconomic Status Pediatric Patients. Water 98-103 nuclear RNA export factor 1 Homo sapiens 0-3 33313440-3 2020 We evaluated drinking water consumption habits in a cohort of obese pediatric patients to determine the percentage that might avoid exposure to EDCs from drinking municipal tap water. Water 177-182 nuclear RNA export factor 1 Homo sapiens 173-176 33313440-8 2020 "Taste" and "Health Concerns" were the most commonly endorsed reasons for eschewing tap water. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 33313440-9 2020 Bottled water consumption among low socioeconomic status patients may reduce their risk for exposure to EDCs in municipal tap water. Water 8-13 nuclear RNA export factor 1 Homo sapiens 122-125 33313440-9 2020 Bottled water consumption among low socioeconomic status patients may reduce their risk for exposure to EDCs in municipal tap water. Water 126-131 nuclear RNA export factor 1 Homo sapiens 122-125 32208246-9 2020 We observed that the association between an individual"s tap water satisfaction and water consumption behavior was mediated by the water treatment strategies applied at home (filtering, cooling), knowledge about drinking water quality and its production, and risk perception. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 32208246-9 2020 We observed that the association between an individual"s tap water satisfaction and water consumption behavior was mediated by the water treatment strategies applied at home (filtering, cooling), knowledge about drinking water quality and its production, and risk perception. Water 84-89 nuclear RNA export factor 1 Homo sapiens 57-60 32208246-9 2020 We observed that the association between an individual"s tap water satisfaction and water consumption behavior was mediated by the water treatment strategies applied at home (filtering, cooling), knowledge about drinking water quality and its production, and risk perception. Water 84-89 nuclear RNA export factor 1 Homo sapiens 57-60 32208246-9 2020 We observed that the association between an individual"s tap water satisfaction and water consumption behavior was mediated by the water treatment strategies applied at home (filtering, cooling), knowledge about drinking water quality and its production, and risk perception. Water 84-89 nuclear RNA export factor 1 Homo sapiens 57-60 32208246-10 2020 The mediating effects were shown to be significant mainly among bottled-water-only and tap-water-only consumers. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 32208246-11 2020 Future interventions that aim to encourage the population"s use of tap water as a primary source should prioritize cooling and filtering tap water in their messaging, in order to improve population satisfaction. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 32208246-11 2020 Future interventions that aim to encourage the population"s use of tap water as a primary source should prioritize cooling and filtering tap water in their messaging, in order to improve population satisfaction. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 32596197-0 2020 Physical Measures to Reduce Exposure to Tap Water-Associated Nontuberculous Mycobacteria. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 32596197-1 2020 Nontuberculous mycobacteria (NTM) that cause human disease can be isolated from household tap water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 32596197-5 2020 First, suspensions of tap water-adapted Mycobacterium smegmatis were passed through either a point-of-use, disposable, 7-day or 14-day Pall-Aquasafe filter. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 32596197-8 2020 Third, suspensions of tap water-adapted M. abscessus, M. avium, and M. chimaera ("MycoCocktail") were passed through the "LifeStraw GO" hollow-fiber, two-stage membrane filtration system. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 32693901-0 2020 [Simultaneous determination of 16 polycyclic aromatic hydrocarbons in source water and tap water by performance liquid chromatography with ultraviolet detector tandem fluorescence detector combined with solid phase extraction]. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 32693901-1 2020 OBJECTIVE: To establish a rapid method for simultaneous determination of 16 polycyclic aromatic hydrocarbons(PAHs) in source water and tap water by performance liquid chromatography(HPLC) with ultraviolet detector(UV) tandem fluorescence detector(FLR). Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 32693901-2 2020 METHODS: Source water was filtered by GF/C glass fiber filters and tap water were added ascorbic acid of 60 mg per liter to remove the residual chlorine when sampling. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 32693901-21 2020 Then the established method was used for the determination of 17 water samples, 8 kinds, 6 kinds and 7 kinds of PAHs were detected in source water, tap water and pipe net tap water, respectively. Water 65-70 nuclear RNA export factor 1 Homo sapiens 148-151 32693901-21 2020 Then the established method was used for the determination of 17 water samples, 8 kinds, 6 kinds and 7 kinds of PAHs were detected in source water, tap water and pipe net tap water, respectively. Water 65-70 nuclear RNA export factor 1 Homo sapiens 171-174 32693901-22 2020 CONCLUSION: The method is rapid, sensitive and selective, and has been successfully applied for determination of 16 PAHs in source water and tap water. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 32701494-8 2020 Furthermore, this method exhibited good feasibility in tap water and lake water. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 32100538-2 2020 A commercially available activated carbon felt has been found to effectively capture lead from tap water, and partnered with X-Ray fluorescence (XRF) spectrometry, it provides quantitative measurement of aqueous lead in drinking water. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 32100538-3 2020 Specifically, for a 2-liter volume of tap water, the linear range of detection was found to be from 1 - 150 ppb, encompassing the current EPA limit for lead in drinking water (15 ppb). Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 32550691-6 2020 We found that epinephrine can be safely used for nail surgery, hydrogen peroxide and tap water is recommended for wound cleansing, prophylactic topical antibiotics should be avoided, calcium alginate, or amniotic membrane dressings are valuable dressing alternatives, and digital dressings have a low risk profile with precise technique. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 31704528-2 2020 Tap water from a drinking water distribution system and ultrafiltrated water were collected and disinfected with four disinfectants (concentrations were set 0.2-1 mg/L as Cl2. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 31704528-10 2020 The level of THM/th and DeltaTHM were lower in ultrafiltrated water than those in tap water. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 32270289-0 2020 Development of a sensitive and accurate method for the simultaneous determination of selected insecticides and herbicide in tap water and wastewater samples using vortex-assisted switchable solvent-based liquid-phase microextraction prior to determination by gas chromatography-mass spectrometry. Water 128-133 nuclear RNA export factor 1 Homo sapiens 124-127 32270289-1 2020 In this study, a switchable solvent-based liquid-phase microextraction method was developed to preconcentrate selected pesticides from tap water and wastewater matrices for determination by gas chromatography-mass spectrometry. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 32270289-7 2020 Tap water, municipal wastewater and medical wastewater were spiked at three different concentrations and analyzed under the method"s optimum conditions. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32418389-0 2020 Identification of Free-Living Amoebas in Tap Water of Buildings with Storage Tanks in Korea. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 32418389-6 2020 Five hundred milliliters of tap water from each building was collected and filtered with 0.2 microm pore filter paper. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 32418389-8 2020 We found that 12.9% of tap water from buildings with storage tanks in Korea was contaminated with FLAs. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 32418389-12 2020 Although cases of human infection by V. vermiformis are very rare, we must pay attention to the fact that one-third of tap water supplies in highway service areas have been contaminated. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 32570997-5 2020 The concentration of Pb and Cd in tap water samples ranged from ND-0.0250 mg/L and ND-0.0042 mg/L, respectively, from ND-0.005 mg/L and ND- 0.0021 mg/L, respectively, in filtered tap water samples and from ND-0.0400 mg/L and ND-0.0049 mg/L, respectively, in raw water samples. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 32570997-6 2020 The summation of the total hazardous index (HI)-values of bottled water samples, tap water samples, filtered tap water, and raw water samples were less than 1, was considered health-protective. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 32570997-6 2020 The summation of the total hazardous index (HI)-values of bottled water samples, tap water samples, filtered tap water, and raw water samples were less than 1, was considered health-protective. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 32570997-6 2020 The summation of the total hazardous index (HI)-values of bottled water samples, tap water samples, filtered tap water, and raw water samples were less than 1, was considered health-protective. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 31868639-4 2020 With regard to the nature of water, the degradation rate varied in the order: ultrapure > superficial > tap water. Water 29-34 nuclear RNA export factor 1 Homo sapiens 104-107 31868639-4 2020 With regard to the nature of water, the degradation rate varied in the order: ultrapure > superficial > tap water. Water 108-113 nuclear RNA export factor 1 Homo sapiens 104-107 31868639-5 2020 This is due to the presence of organic and inorganic matter (bicarbonates, nitrates, and chlorides) in surface and tap water, that react with the radicals generated, which reduces the availability of radical species, generating competitive kinetics. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 31943512-16 2020 Periodic addition of an effervescent tablet into tap water may be recommended to patients that wear implant retained overdentures with Locator attachments. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 32019602-8 2020 During immersion, tap water or CO2 water was stirred slowly with a pump. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 31943512-11 2020 Following NaOCl (blue; 33.31 +- 4.72 N, clear; 52.3 +- 8.5 N), tap water decreased the retention value of blue (41.14 +- 3.93 N) and clear (76.72 +- 8.42 N) Locator attachments at T3 . Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 31943512-15 2020 Also, tap water remarkably decreased retentive ability of all attachments. Water 10-15 nuclear RNA export factor 1 Homo sapiens 6-9 32019602-12 2020 RESULTS: Skin blood flow of the immersed forearms was higher in CO2 water than in tap water during immersion. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 32019602-13 2020 The blood flow in the last 5 min (average at rest was 100%) was significantly higher in CO2 water (290.85 +- 84.81%) than in tap water (104.80 +- 21.99%). Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 32019602-15 2020 Ear canal temperature significantly declined more in CO2 water (- 0.56 +- 0.31 C) than in tap water (- 0.48 +- 0.30 C) during immersion. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 32405304-0 2020 Comprehensive Risk Assessment of Health-Related Hazardous Events in the Drinking Water Supply System from Source to Tap in Gaza Strip, Palestine. Water 81-86 nuclear RNA export factor 1 Homo sapiens 116-119 31708174-5 2020 Bromate was found in almost all tap water samples with a mean concentration of 19.6 mug/L, which is higher than the maximum acceptable contaminant level (MCL) of 10 mug/L. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 31708174-6 2020 The mean concentration of bromide in tap water samples was 46.2 mug/L. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 31708174-11 2020 The excess cancer risk due to ingestion of bromate in tap water was estimated to be 3.92 x 10-4, which is approximately one order of magnitude higher than the maximum acceptable level of risk (2x 10-5). Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 31996207-4 2020 Water was categorized as tap or bottled (plain). Water 0-5 nuclear RNA export factor 1 Homo sapiens 25-28 31996207-11 2020 The main sources of water were tap at home (288 mL/d), tap away from home (301 mL/d), and bottled water from stores (339 mL/d). Water 20-25 nuclear RNA export factor 1 Homo sapiens 31-34 31996207-13 2020 Higher tap water consumption was associated with higher incomes, but bottled water was not. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 32405304-2 2020 Therefore, the transition to a systematic approach in drinking water supply systems management from the source to the consumer tap was taken as a water safety plan (WSP). Water 146-151 nuclear RNA export factor 1 Homo sapiens 127-130 31318730-9 2020 The range of thyroid doses to Iitate Village residents was similar to that to Iwaki City residents even though the I concentration in tap water was much higher in Iitate Village than Iwaki City. Water 138-143 nuclear RNA export factor 1 Homo sapiens 134-137 32030182-0 2019 Human health risk assessment of trace elements in drinking tap water in Zahedan city, Iran. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 31419468-8 2020 Typing of 1,515 isolates from 373 patients and 375 isolates from 81 tap water samples identified 296 pulsotypes. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 31419468-10 2020 The pulsotype identified was previously isolated from another patient and from a tap water sample for 86 and 29 patients respectively. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 32213722-5 2020 Control samples were taken before and after the prescribed flushing from another high-speed handpiece (HS-2) that is directly supplied with tap water in the same dental unit. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 32213722-9 2020 RESULTS: SAEW always showed a higher free chlorine concentration than tap water during the observation period of 7 years. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 32213722-10 2020 In HS-2 supplied with tap water, the free chlorine concentration increased significantly owing to the prescribed flushing. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 32213722-11 2020 SAEW always showed a significantly smaller number of heterotrophic bacteria than tap water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 31505354-11 2020 The results showed that some of the technique, if implemented as part of the water safety management, can detect rapidly the most common waterborne pathogens and fecal pollution indicators and therefore have a great early warning potential; can improve water safety for the consumer; can validate whether mitigation methods are working as intended; and can confirm the quality of the water at source and at the tap. Water 77-82 nuclear RNA export factor 1 Homo sapiens 411-414 31505354-11 2020 The results showed that some of the technique, if implemented as part of the water safety management, can detect rapidly the most common waterborne pathogens and fecal pollution indicators and therefore have a great early warning potential; can improve water safety for the consumer; can validate whether mitigation methods are working as intended; and can confirm the quality of the water at source and at the tap. Water 137-142 nuclear RNA export factor 1 Homo sapiens 411-414 31505354-11 2020 The results showed that some of the technique, if implemented as part of the water safety management, can detect rapidly the most common waterborne pathogens and fecal pollution indicators and therefore have a great early warning potential; can improve water safety for the consumer; can validate whether mitigation methods are working as intended; and can confirm the quality of the water at source and at the tap. Water 137-142 nuclear RNA export factor 1 Homo sapiens 411-414 32248159-6 2020 CONCLUSION: Conclusions: Results of sociological survey shown that among rural residents increased the demand for a consumption of pre-treated drinking water, due to the deterioration quality of tap water in the rural area. Water 152-157 nuclear RNA export factor 1 Homo sapiens 195-198 32248159-6 2020 CONCLUSION: Conclusions: Results of sociological survey shown that among rural residents increased the demand for a consumption of pre-treated drinking water, due to the deterioration quality of tap water in the rural area. Water 199-204 nuclear RNA export factor 1 Homo sapiens 195-198 31491637-1 2019 Although human exposure to perfluoroalkyl acids (PFAAs) through tap water is an ongoing concern, knowledge of the PFAAs occurrence in the tap water and the associated transport behaviors of PFAAs in drinking water distribution systems (DWDSs) are scarce. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 31491637-1 2019 Although human exposure to perfluoroalkyl acids (PFAAs) through tap water is an ongoing concern, knowledge of the PFAAs occurrence in the tap water and the associated transport behaviors of PFAAs in drinking water distribution systems (DWDSs) are scarce. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 31491637-1 2019 Although human exposure to perfluoroalkyl acids (PFAAs) through tap water is an ongoing concern, knowledge of the PFAAs occurrence in the tap water and the associated transport behaviors of PFAAs in drinking water distribution systems (DWDSs) are scarce. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 31491637-3 2019 Tap water samples both along trunk pipelines and at the distal ends were collected to display the PFAAs occurrence scenarios. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 31491637-5 2019 The results showed that perfluorooctanoic acid (PFOA) and perfluorobutanoic acid (PFBA) widely existed in tap water samples, and were the predominant PFAAs in eastern China areas. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 31491637-11 2019 When water quality conditions change or hydraulic disturbance occur, loose deposits may enter tap water bringing accumulated PFAAs with it, which may result in potential health risks. Water 5-10 nuclear RNA export factor 1 Homo sapiens 94-97 31491637-11 2019 When water quality conditions change or hydraulic disturbance occur, loose deposits may enter tap water bringing accumulated PFAAs with it, which may result in potential health risks. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 31856722-5 2019 Same time bacterial diversity of tap water, connected to the dishwashers was investigated. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 31856722-11 2019 The bacterial diversity of tap water was also lower, 23 genera compared to 39 genera on dishwasher rubber seals. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 31856722-12 2019 Only 13 out of 49 genera identified by metagenomics approach was found in both environments, of those Gordonia was enriched while half of 13 genera were depleted in dishwashers compared to tap water. Water 193-198 nuclear RNA export factor 1 Homo sapiens 189-192 32030182-2 2019 Although the health risk assessment of heavy metals in different water sources has extensively carried out in various studies, the effect of age and the concentration of all trace elements in drinking tap water have neglected. Water 205-210 nuclear RNA export factor 1 Homo sapiens 201-204 32030182-4 2019 Moreover, this is the first research in Iran that has also been dedicated to complete investigation on daily intakes of trace elements in tap water. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 32782938-3 2020 Tacrolimus is topically active, water soluble, and has minimal systemic toxicity when administered rectally; we therefore tested a simple tap water-based enema formulation. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 31394442-6 2019 Moreover, the degradation of FLU in different water matrices were also explored, and the removal followed the order of Tap water > Ultrapure water > River water > Secondary clarifier effluent. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 31394442-6 2019 Moreover, the degradation of FLU in different water matrices were also explored, and the removal followed the order of Tap water > Ultrapure water > River water > Secondary clarifier effluent. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 31394442-6 2019 Moreover, the degradation of FLU in different water matrices were also explored, and the removal followed the order of Tap water > Ultrapure water > River water > Secondary clarifier effluent. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 31504580-0 2019 Detection of a novel mcr-5.4 gene variant in hospital tap water by shotgun metagenomic sequencing. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 31390577-0 2019 Sources of and solutions to mistrust of tap water originating between treatment and the tap: Lessons from Los Angeles County. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 31390577-0 2019 Sources of and solutions to mistrust of tap water originating between treatment and the tap: Lessons from Los Angeles County. Water 44-49 nuclear RNA export factor 1 Homo sapiens 88-91 31390577-1 2019 Tap water mistrust has adverse impacts on health and welfare. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 31390577-2 2019 This study identifies, defines and motivates attention to cases of mistrust of tap water which originate between the treatment plant and the tap where people ultimately consume it. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 31390577-2 2019 This study identifies, defines and motivates attention to cases of mistrust of tap water which originate between the treatment plant and the tap where people ultimately consume it. Water 83-88 nuclear RNA export factor 1 Homo sapiens 141-144 31390577-3 2019 Between treatment and the tap, water quality contamination can be introduced within two segments of the built environment with two distinct responsible parties- community water system"s distributional networks and property owner"s premise plumbing. Water 31-36 nuclear RNA export factor 1 Homo sapiens 26-29 31390577-3 2019 Between treatment and the tap, water quality contamination can be introduced within two segments of the built environment with two distinct responsible parties- community water system"s distributional networks and property owner"s premise plumbing. Water 171-176 nuclear RNA export factor 1 Homo sapiens 26-29 31390577-5 2019 We use examples from Los Angeles County, an area with high resident tap water mistrust especially among disadvantaged communities, despite there being relatively few health-related water quality violations. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 31390577-8 2019 Findings suggest that there are numerous instances where the distributional network, and secondarily premise plumbing, introduce water quality contamination which contributes to tap mistrust in urban communities by making water unclean, but not necessarily unsafe per existing regulation. Water 129-134 nuclear RNA export factor 1 Homo sapiens 178-181 31390577-8 2019 Findings suggest that there are numerous instances where the distributional network, and secondarily premise plumbing, introduce water quality contamination which contributes to tap mistrust in urban communities by making water unclean, but not necessarily unsafe per existing regulation. Water 222-227 nuclear RNA export factor 1 Homo sapiens 178-181 31474661-0 2019 Preparation of a Reference Material for the Determination of Hexavalent Chromium in Tap Water. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 31310699-0 2019 Water to prevent kidney stones: tap vs bottled; soft vs hard - does it matter? Water 0-5 nuclear RNA export factor 1 Homo sapiens 32-35 31398650-4 2019 The optimized method was applied to analyze VOCs in tap water samples collected from Wuhan City, China. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 31398650-8 2019 Untargeted analysis of the tap water samples identified 75-200 VOCs, including 67 highly prevalent compounds. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 31400719-10 2019 While those are some differences among tap waters inlet from the same water sources. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 31472335-3 2019 This study investigated the bacterial growth through a POU water dispenser fed with chlorinated tap water; specifically, the heterotrophic plate count increased from 0.01 to 20.01 x 103 of colony-forming units per ml. Water 59-64 nuclear RNA export factor 1 Homo sapiens 96-99 31472335-3 2019 This study investigated the bacterial growth through a POU water dispenser fed with chlorinated tap water; specifically, the heterotrophic plate count increased from 0.01 to 20.01 x 103 of colony-forming units per ml. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 31717290-4 2019 Water was categorized as tap or bottled. Water 0-5 nuclear RNA export factor 1 Homo sapiens 25-28 31409458-5 2019 Excellent predictions were obtained for the determination of hydroquinone and catechol in the direct analysis of spiked tap water samples with EIS and complex numbers-PLS. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 31158313-4 2019 Tap water arsenic concentrations and risk perception data were collected from two Saskatchewan communities. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 31124831-8 2019 The annual effective doses calculated from radionuclides in the water are 0.11, 0.09, 0.09, and 0.11 mSv for borehole, stream, tap, and well, respectively. Water 64-69 nuclear RNA export factor 1 Homo sapiens 127-130 30646797-1 2019 Objective: Tap water iontophoresis as a treatment for focal hyperhidrosis is given as an initial series of treatments in hospital, followed by home maintenance treatments. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 30646797-12 2019 Conclusion: In conclusion, tap water iontophoresis can result in a significant improvement in perceived severity of hyperhidrosis and quality of life. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 31158313-9 2019 The probability of drinking tap water perceived as safe (77%) or as not safe (11%) suggested households in BOFN contradicted their perception and consumed water perceived as unsafe. Water 155-160 nuclear RNA export factor 1 Homo sapiens 28-31 31759341-0 2019 Helicobacter Pylori Detected in Tap Water of Peruvian Patients with Gastric Cancer. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 31759341-1 2019 OBJECTIVE: To evaluate the correlation between the presence of H. pylori in paired samples of tap water and gastric cancer (GC) lesion in Lima city (Peru). Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 31759341-7 2019 H. pylori was detected in 69.5% of gastric tissues and in 12.2% of analyzed tap-water. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 31759341-9 2019 Conclusion & Impact: H. pylori was found in tap-water samples, however, detection rates were lower than in gastric cancer samples. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 31377524-7 2019 Soluble anions and cations in tap water were also present in the aerosols emitted from humidifiers. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 31158313-8 2019 The probability of consuming tap water perceived as safe (92%) or not safe (0%) suggested that households in RM184 were unlikely to drink water perceived as not safe. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 31158313-9 2019 The probability of drinking tap water perceived as safe (77%) or as not safe (11%) suggested households in BOFN contradicted their perception and consumed water perceived as unsafe. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 31671709-0 2019 Comparison of Culture- and Quantitative PCR-Based Indicators of Antibiotic Resistance in Wastewater, Recycled Water, and Tap Water. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 31441298-8 2019 In the following test of real spiked samples of tap water and lake water, the recovery ratios of formaldehyde with the concentrations from 0.010 to 0.045 mM are tested to be between 95 and 100% by both measuring the variance in short circuit current and analyzing the color change of the cathode digitally. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 31532667-0 2019 One-Step Facile Synthesis of Nitrogen-Doped Carbon Dots: A Ratiometric Fluorescent Probe for Evaluation of Acetylcholinesterase Activity and Detection of Organophosphorus Pesticides in Tap Water and Food. Water 189-194 nuclear RNA export factor 1 Homo sapiens 185-188 31532667-2 2019 In this study, a highly selective and sensitive ratiometric fluorescent probe was innovatively fabricated for the evaluation of AChE activity and the determination of OPs in tap water and food on the basis of the inner filter effect (IFE) between nitrogen-doped carbon dots (N-CDs) and 2,3-diaminophenazine (DAP). Water 178-183 nuclear RNA export factor 1 Homo sapiens 174-177 31532667-10 2019 Practical application of this ratiometric fluorescent probe to detect OPs was further verified in tap water and food samples with satisfying results that were highly consisted with the results obtained by GC-MS. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 31421451-9 2019 According to the toxicological information about PFAS that is so far available, the current health risks for the regular consumers of municipal/tap water do not seem to be of concern according to the levels considered as acceptable for various regulatory institutions. Water 148-153 nuclear RNA export factor 1 Homo sapiens 144-147 31283422-5 2019 The average Pb and Cd intakes from food and drinking (tap) water ranged for children from 0.90 to 1.021 microg/kg bw/day and 4.65 to 5.65 microg/kg bw/week, respectively, and for adults, including adolescents, from 0.40 to 0.53 microg/kg bw/day and 1.98 to 2.82 microg/kg bw/week, respectively. Water 59-64 nuclear RNA export factor 1 Homo sapiens 54-57 31503468-1 2019 The detection of hypochlorite (ClO-) content in tap water is extremely important because excess amounts of hypochlorite can convert into highly toxic species and inadequate amounts of hypochlorite cannot fully kill bacteria and viruses. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 31254804-5 2019 When validated for practical and quantitative detection of tap water and milk samples, both sensing methods performed well with detection limits of <260 nM and measurement times of <40 min. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 31018907-13 2019 Several patients admitted to exposing their CL to unsterile water either via swimming, showering or tap water. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 31486902-12 2019 In addition, good recoveries of 91.3-119.0% were found for tap water, river water and artificial urine spiked with OFL with relative standard deviation (RSD) of <=11.6%. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 31424532-12 2019 Women living in areas with fluoridated tap water (n = 141) compared with nonfluoridated water (n = 228) had significantly higher mean (SD) MUFSG concentrations (0.69 [0.42] mg/L vs 0.40 [0.27] mg/L; P = .001; to convert to millimoles per liter, multiply by 0.05263) and fluoride intake levels (0.93 [0.43] vs 0.30 [0.26] mg of fluoride per day; P = .001). Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 31517119-1 2019 Fluoride intake from tap water supplied by fluoride-containing groundwater has been the primary cause of fluorosis among the residents of Buak Khang Subdistrict, Chiang Mai Province, Thailand. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 31517119-9 2019 The fluoride intake from using tap water for drinking and cooking was estimated to be 0.18 +- 0.10 mg/kg-body weight/day and 5.55 +- 3.52 mg/capita/day, respectively, whereas using bottled water for drinking and cooking reduced the fluoride intake to 0.002 +- 0.002 mg/kg-body weight/day and 0.07 +- 0.05 mg/capita/day, respectively. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 31464621-9 2019 Effective compliance rate with safe drinking water practices, either by storing clean drinking water or boiling tap water, after a water outage was 72% among those who remembered receiving a notification. Water 45-50 nuclear RNA export factor 1 Homo sapiens 112-115 31238205-9 2019 Women assigned to the intervention group received warm compresses made from clean washcloths or perineal pads immersed in warm tap water. Water 131-136 nuclear RNA export factor 1 Homo sapiens 127-130 31464621-11 2019 The main reason for respondents" non-compliance with safe water practices was that they perceived the water to be safe to drink after letting it flush through the tap until it became clear. Water 58-63 nuclear RNA export factor 1 Homo sapiens 163-166 31464621-11 2019 The main reason for respondents" non-compliance with safe water practices was that they perceived the water to be safe to drink after letting it flush through the tap until it became clear. Water 102-107 nuclear RNA export factor 1 Homo sapiens 163-166 31298842-6 2019 Concentrations in tap water samples ranged from 0.07 mug/L to 11.5 mug/L while the HMSA concentrations in surface waters were in the range of 100 ng/L. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 31071669-2 2019 However, the SVOC occurrence and influence of pipe materials on SVOC levels in the tap water have received little attention. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 31071669-7 2019 12 PCB congeners were detected in Hangzhou tap water samples, with hepta-CBs (68% of samples) as the most frequently detected PCBs. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 31071669-8 2019 Nearly all tap water samples contained measurable o, p"-DDE, p, p"-DDT, and p, p"-DDD, and DDTs had significantly (p < 0.05) higher concentrations than HCHs. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 31071669-9 2019 All target PAHs had high detection frequencies (>72%) in tap water samples, with their mean concentrations in the range of 2.1-41 ng/L. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 31071669-10 2019 Tap water from steel pipes had relatively lower SVOC concentrations than that from either reinforced concrete, gray cast iron, or ductile iron pipes. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 31071669-11 2019 Although no carcinogenic risks originating from exposure to SVOCs through ingestion and bathing were observed, the tap water from steel pipes showed relatively low exposure risks than that from other materials. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 31283199-10 2019 The integration of the wastewater systems with ultrafiltration, AOP, and RO was effective to reduce the toxicity to levels comparable to, or better than, tap water samples. Water 28-33 nuclear RNA export factor 1 Homo sapiens 154-157 31026539-7 2019 We therefore calculated the allowable concentration in water by allocating a small percentage of the indoor air guideline value to indirect inhalation exposure via volatilization from tap water. Water 55-60 nuclear RNA export factor 1 Homo sapiens 184-187 30731184-3 2019 It can easily be produced locally in small generators, and dissolved in tap water, and quickly transmits into ordinary O2 in the surrounding air. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 30731184-13 2019 CONCLUSION: Ozonized tap water is an effective decontaminant of E. coli, and it could be an alternative to traditional alcohol-fluid hand disinfectants both in healthcare institutions and public places. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 31026539-7 2019 We therefore calculated the allowable concentration in water by allocating a small percentage of the indoor air guideline value to indirect inhalation exposure via volatilization from tap water. Water 188-193 nuclear RNA export factor 1 Homo sapiens 184-187 31031576-1 2019 A full-scale reproduction of an aircraft drinking water system was conditioned using municipal tap water with a mixture of free chlorine and chloramines, and subsequently contaminated with coliforms. Water 50-55 nuclear RNA export factor 1 Homo sapiens 95-98 31031576-1 2019 A full-scale reproduction of an aircraft drinking water system was conditioned using municipal tap water with a mixture of free chlorine and chloramines, and subsequently contaminated with coliforms. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 31477627-5 2019 The concentration of Cl<sup>-</sup> was 0.7mg/L in tap water and 0.1mg/L in RO water, while the concentration of SiO<sub>4</sub><sup>4-</sup> was 0.3mg/L in both the tap and RO water. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 30930351-2 2019 Special care was taken for the validation of the proposed ID-ICPMS method using CRM 7203-a, a certified reference material for elemental analysis of tap water. Water 153-158 nuclear RNA export factor 1 Homo sapiens 149-152 31030157-7 2019 At least three NNIs were detected in all tap water samples with the highest sum concentration of NNIs observed in July (median: 96.2ng/L, range: 16.7-138ng/L) among the studied months (median: 15.4, range: 2.59-138ng/L). Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 31030157-9 2019 The concentrations observed in tap water are elevated in China relative to previous studies that were conducted in the USA and in Canada. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 31009894-9 2019 KNTs were applied successfully in realistic purification of tap water, groundwater, and sewage water from the inspected metals. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 30527279-0 2019 Tap water: A possible source of nontuberculous mycobacterial infection in patients with T cell deficiency. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 32184700-9 2019 The decrease of the dissolved mass of Ag+ in tap water could be due to the reaction between Ag+ and Cl-, forming AgCl and affecting their dissolution. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 31334211-7 2019 Positive trends were observed for knowing that tap water with fluoride prevents cavities and that poor oral health of parents affects their children"s dental health. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 31334211-10 2019 Significant positive improvements were found regarding caregiver"s favorable attitude that fluoridated water can help prevent cavities, disagreeing that tap water is dangerous, and agreeing that a parent"s dental health affects their children"s dental health. Water 157-162 nuclear RNA export factor 1 Homo sapiens 153-156 31460168-4 2019 Additionally, the sensitivity of NGOD- and AA-originated signal recovery from the Hg(II)-NGODs mixture has been successfully tested in Hg2+ ion-spiked tap water from three different places. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 31074186-6 2019 The developed method was applied for the determination of the emerging contaminants in tap water, municipal water, ground water, sewage water, and sludge water samples. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 30415431-6 2019 Most used tap water (89%) in an enema bottle (50%) or rubber bulb (43%), and douched for cleanliness (97%), to avoid smelling bad (65%), and to enhance pleasure (24%). Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 31197617-8 2019 It was applied to spiked tap water samples and gave recoveries around 95 +- 5%. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 31205847-3 2019 This stability translates into increasing time efficiency of the synthesis and makes the protocol experimentally less demanding ("fast addition" not required, tap water can be used in the final steps) as compared to previously reported procedures, without compromising the size and shape monodispersity of the product. Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 31170009-0 2019 Tap Water Contributions to Plasma Concentrations of Poly- and Perfluoroalkyl Substances (PFAS) in a Nationwide Prospective Cohort of U.S. Women. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 30818190-5 2019 NP-PS system worked better in bottled water (96.46%) and tap water (85.14%) than river water (31.28%). Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 30826705-8 2019 Third, compared with the iodoacetic acid sample and the simulated tap water sample without ammonolysis, the developmental toxicity of the corresponding samples with ammonolysis decreased by up to 10.4% and 32.1%, respectively. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 30826705-9 2019 The ammonolysis was thus demonstrated to be a detoxification process for both individual HAAs and DBP mixture in chlorinated tap water. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 30826705-10 2019 In practice, the ammonolysis of haloacid DBPs in tap water may be realized by simply adding an appropriate amount of an aminating agent during cooking. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 31170009-3 2019 OBJECTIVES: This study estimates the RSC of tap water to overall PFAS exposure among members of the general U.S. POPULATION: METHODS: We measured concentrations of 15 PFAS in home tap water samples collected in 1989-1990 from 225 participants in a nationwide prospective cohort of U.S. women: the Nurses" Health Study (NHS). Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 31170009-4 2019 We used a one-compartment toxicokinetic model to estimate plasma concentrations corresponding to tap water intake of PFAS. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 31170009-6 2019 RESULTS: Tap water perfluorooctanoic acid (PFOA) and perfluorononanoic acid (PFNA) were statistically significant predictors of plasma concentrations among individuals who consumed [Formula: see text] cups of tap water per day. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 31170009-6 2019 RESULTS: Tap water perfluorooctanoic acid (PFOA) and perfluorononanoic acid (PFNA) were statistically significant predictors of plasma concentrations among individuals who consumed [Formula: see text] cups of tap water per day. Water 13-18 nuclear RNA export factor 1 Homo sapiens 209-212 31170009-6 2019 RESULTS: Tap water perfluorooctanoic acid (PFOA) and perfluorononanoic acid (PFNA) were statistically significant predictors of plasma concentrations among individuals who consumed [Formula: see text] cups of tap water per day. Water 213-218 nuclear RNA export factor 1 Homo sapiens 9-12 31170009-6 2019 RESULTS: Tap water perfluorooctanoic acid (PFOA) and perfluorononanoic acid (PFNA) were statistically significant predictors of plasma concentrations among individuals who consumed [Formula: see text] cups of tap water per day. Water 213-218 nuclear RNA export factor 1 Homo sapiens 209-212 31095520-7 2019 Increasing reliance on tap water likely requires measuring and addressing secondary contamination found in distributional systems and premise plumbing, and more aggressive public education campaigns. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 30979398-9 2019 CONCLUSIONS: Fluoridated tap water is a low-cost, ecologically friendly resource that provides health benefits seldom found in bottled water. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 30979398-9 2019 CONCLUSIONS: Fluoridated tap water is a low-cost, ecologically friendly resource that provides health benefits seldom found in bottled water. Water 135-140 nuclear RNA export factor 1 Homo sapiens 25-28 30979398-10 2019 However, mistrust about the quality and safety of tap water may make those in low-income communities more vulnerable to the effects of not receiving adequate fluoride and thus at higher risk of developing caries. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 30979398-11 2019 PRACTICAL IMPLICATIONS: Future interventions should encourage tap water use by dispelling misconceptions and educating low-income people in urban areas of LAC about the health benefits of fluoridated tap water and the safety of its sources. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 30979398-11 2019 PRACTICAL IMPLICATIONS: Future interventions should encourage tap water use by dispelling misconceptions and educating low-income people in urban areas of LAC about the health benefits of fluoridated tap water and the safety of its sources. Water 66-71 nuclear RNA export factor 1 Homo sapiens 200-203 30763841-12 2019 VPRs were quantified in 20% of the tap water samples. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 31151185-6 2019 However, for tap water, a high-surface-tension solvent, it has relatively low fragmentation degree, and good dispersion and exfoliation effects due to the hydrophilicity of GNPs. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 31459881-8 2019 Moreover, the analytical performance of the proposed probe was practically demonstrated to successfully monitor trace levels of TCS in samples of tap water and personal care products. Water 150-155 nuclear RNA export factor 1 Homo sapiens 146-149 30802796-7 2019 Furthermore, the sensor has been used for the detection of fluoride anion in tap water, ground water and human serum samples, the recovery can achieve 94.0%-103.3%, 94.7%-101.0% and 89.8-100.9%, respectively. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 30790554-12 2019 We found that containers with partial shade produce 4.6 times more pupae than without any shade, whereas in the excess zero group the expected number of observed zero pupae count is 86.5% lower in containers filled with rain water than those with tap water, tube-well water, ring well water and water from other sources. Water 251-256 nuclear RNA export factor 1 Homo sapiens 247-250 30790554-12 2019 We found that containers with partial shade produce 4.6 times more pupae than without any shade, whereas in the excess zero group the expected number of observed zero pupae count is 86.5% lower in containers filled with rain water than those with tap water, tube-well water, ring well water and water from other sources. Water 251-256 nuclear RNA export factor 1 Homo sapiens 247-250 30790554-12 2019 We found that containers with partial shade produce 4.6 times more pupae than without any shade, whereas in the excess zero group the expected number of observed zero pupae count is 86.5% lower in containers filled with rain water than those with tap water, tube-well water, ring well water and water from other sources. Water 251-256 nuclear RNA export factor 1 Homo sapiens 247-250 30790554-12 2019 We found that containers with partial shade produce 4.6 times more pupae than without any shade, whereas in the excess zero group the expected number of observed zero pupae count is 86.5% lower in containers filled with rain water than those with tap water, tube-well water, ring well water and water from other sources. Water 251-256 nuclear RNA export factor 1 Homo sapiens 247-250 30660975-2 2019 In this study, 64 tap water samples were collected from 8 counties (or county level cities) in Jinhua Region of Zhejiang Province, China. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 30571992-2 2019 AIM: To investigate the dispersal of CRE from sinks in which water delivered from the tap flows directly into the drain and from clinical handwash basins with the drain at the rear. Water 61-66 nuclear RNA export factor 1 Homo sapiens 86-89 30903353-0 2019 Selective, Sensitive and Label-Free Detection of Fe3+ Ion in Tap Water Using Highly Fluorescent Graphene Quantum Dots. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 30903353-7 2019 Importantly, the new sensor realizes the detection of Fe3+ ions in tap water because of its low detection limit, wide linear range, and high sensitivity. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 31133138-6 2019 When spiked concentration was 1.0 mug/L for pure water and tap water, the recoveries were 94.8% and 93.7%, respectively, and relative standard deviation was 2.9% and 3.4%, respectively. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 31133138-7 2019 When spiked concentration was 16.0 mug/L for pure water and tap water, the recoveries were both 101% and relative standard deviation was 1.0% and 1.3%, respectively. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 30660975-6 2019 Correlation analysis showed that DBPs occurrence in tap water was significantly related with physicochemical parameters. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 30660975-7 2019 Principle component analysis further suggested that organic matter (DOC and UVA254) are the major factors influencing the occurrence of THMs, HAAs, HANs and HKs in tap water, while for HNMs, both the organic (DOC and UVA254) and inorganic factors (e.g. Temp, NO2--N, pH, Br- and NH4+-N) played important role in its formation. Water 168-173 nuclear RNA export factor 1 Homo sapiens 164-167 30580164-7 2019 Overall, the quantitative findings suggested that the occurrence of non-nutritive artificial sweeteners is present in surface water, tap water, groundwater, seawater, lakes and atmosphere. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 30583431-4 2019 Green tea also generated H2O2; tea prepared on tap water generated significantly more H2O2 than tea prepared on deionized water. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 31003396-0 2019 Microplastics Detection in Streaming Tap Water with Raman Spectroscopy. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 31003396-3 2019 However, for drinking and tap water, with its comparatively low biological loads, direct observation may be possible and allows a point-of-entry monitoring for beverages and food to ensure uncontaminated drinking water is being used. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 31003396-4 2019 In a proof of concept, we apply Raman spectroscopy to observe individual microplastic particles in tap water with added particulate and fluorescent contaminants streaming with 1 L/h through a custom-made flow cell. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 31003396-6 2019 The experiment promises the monitoring of streaming tap water and even clear surface waters for microplastics smaller than 0.1 mm. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 30942779-4 2019 A wide-range of bacterial genera were found in bottled and tap water filtrates from 0.2 mum filters, including genera housing opportunistic pathogens (e.g. Methylobacterium) and endospore formers (Paenibacillus). Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 30771559-1 2019 INTRODUCTION: Improving children"s tap water intake and reducing sugar-sweetened beverage (SSB) consumption is beneficial for health and health equity, particularly in low-income communities and communities of color. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 30771559-2 2019 Existing community level interventions to improve the intake of tap water have predominantly occurred in schools and have focused on promoting water consumption in cafeterias during lunch or snack periods. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 30771559-3 2019 METHODS: The "Hydrate Philly" intervention was developed to target multiple environmental and social factors to improve tap water consumption in community recreation centers in low-income communities: replacing old and unappealing water fountains with appealing water-bottle-filling "hydration stations", conducting water safety testing and publicizing results, disseminating reusable water bottles, promoting tap water, and discouraging SSB consumption. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 30771559-7 2019 DISCUSSION: Multilevel approaches are needed to increase tap water intake and decrease SSB consumption among low-income and minority youth beyond school and meal settings. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 30535556-6 2019 Tap water will not supercool because it contains impurities that serve as nucleation sites for crystallization. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 31065474-10 2019 Our results suggest that it is better to store inhalers in places where there is easy access to tap water used for RMOG. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 31143736-1 2019 Purpose: The purpose of this study was to investigate parental knowledge and preference of tap water in a country where faucet water is fluoridated according to international standards and where the average percentage of dental caries in young children reaches up to approximately 73%. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 31143736-1 2019 Purpose: The purpose of this study was to investigate parental knowledge and preference of tap water in a country where faucet water is fluoridated according to international standards and where the average percentage of dental caries in young children reaches up to approximately 73%. Water 127-132 nuclear RNA export factor 1 Homo sapiens 91-94 31143736-9 2019 Amid revealing participants that our tap water is safe and that fluorine can prevent dental caries, 33% of parents would you use tap water due to its fluoride content. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 31143736-10 2019 The study also showed that 65% of parents would allow their children to drink tap water if it is free from any toxic ingredients. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 31143736-13 2019 These data will also allow us to propose the use of tap water safely in young children in the state of Qatar while simultaneously advocating awareness of oral health. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 30942779-5 2019 Two municipal tap water isolates were only distantly related to named species. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 30694266-8 2019 This proposed method was also successfully utilized for the determination of Hg2+ in drinking water, tap water and surface water with good recovery (>91%) and high intra-day and inter-day precision. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 30943671-5 2019 Patient revealed that he injected drugs intravenously with tap water. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 30694266-8 2019 This proposed method was also successfully utilized for the determination of Hg2+ in drinking water, tap water and surface water with good recovery (>91%) and high intra-day and inter-day precision. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 30764612-0 2019 Evolution of Cavitation Bubble in Tap Water by Continuous-Wave Laser Focused on a Metallic Surface. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 30884819-1 2019 Many people around the globe prefer bottled water especially in developing countries, where tap water is not drinkable. Water 44-49 nuclear RNA export factor 1 Homo sapiens 92-95 30884819-1 2019 Many people around the globe prefer bottled water especially in developing countries, where tap water is not drinkable. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 30508728-3 2019 Tap water and saline water with 32 g/L of sodium chloride were employed as the media to generate MBs. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 30597678-10 2019 The 87 Sr/86 Sr ratios of both hair and leachate were linearly correlated with tap water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 31384776-8 2019 The applicability of the developed method was investigated by analyzing tap water, bottled mineral water and waste water and demonstrated satisfactory recoveries in the ranges of 86.4-120%. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 30448547-8 2019 Additionally, both eARG and iARG concentrations in tap water presented a seasonal pattern with most abundant prevalence in summer. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 30764612-1 2019 As an example of photon-matter interaction, we experimentally investigate the temporal evolution of a millimeter-sized cavitation bubble, induced by focusing a continuous-wave laser on a metallic plate in tap water. Water 209-214 nuclear RNA export factor 1 Homo sapiens 205-208 30537651-0 2019 Impact of disinfectant on bacterial antibiotic resistance transfer between biofilm and tap water in a simulated distribution network. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 30537651-8 2019 The major prevalent genera in biofilms were also detected in tap water, suggesting that biofilm growth or biofilm detachment caused by external environmental factors will allow the movement of biofilm clusters with higher ARB concentration and percentage into bulk water, thereby increasing the antibiotic resistance of bacteria in tap water. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 30537651-8 2019 The major prevalent genera in biofilms were also detected in tap water, suggesting that biofilm growth or biofilm detachment caused by external environmental factors will allow the movement of biofilm clusters with higher ARB concentration and percentage into bulk water, thereby increasing the antibiotic resistance of bacteria in tap water. Water 65-70 nuclear RNA export factor 1 Homo sapiens 332-335 30832438-5 2019 Four categories of factors affecting the risk of threat to tap water consumers were assumed: the frequency or the probability of exposure-P, financial losses-C, damages to peoples" health-HL, the degree of the security-S. Based on this, a four-parametric risk matrix was developed. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 30469001-4 2019 Together, these factors may help explain varying CH photolysis in different types of waters: seawater > ultrapure water > tap water > lake water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 128-131 30537651-8 2019 The major prevalent genera in biofilms were also detected in tap water, suggesting that biofilm growth or biofilm detachment caused by external environmental factors will allow the movement of biofilm clusters with higher ARB concentration and percentage into bulk water, thereby increasing the antibiotic resistance of bacteria in tap water. Water 265-270 nuclear RNA export factor 1 Homo sapiens 61-64 30537651-3 2019 The results revealed that the disinfectants (>=2 mg/L) suppressed antibiotic resistant bacteria (ARB) in tap water and biofilms, while disinfected water and biofilms had a high relative abundance of ARB. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 30537651-8 2019 The major prevalent genera in biofilms were also detected in tap water, suggesting that biofilm growth or biofilm detachment caused by external environmental factors will allow the movement of biofilm clusters with higher ARB concentration and percentage into bulk water, thereby increasing the antibiotic resistance of bacteria in tap water. Water 265-270 nuclear RNA export factor 1 Homo sapiens 61-64 30469174-0 2019 Surface Characterizations of Railway Electrical Wires Coated with Anti-Icing Mixtures of Ethylene Glycol or Glycerol with Tap Water. Water 126-131 nuclear RNA export factor 1 Homo sapiens 122-125 30469174-4 2019 In the present study, the railway contact wires are coated with anti-icing mixtures of ethylene glycol/tap water and glycerol/tap water at various ratios (v/v %) as well as with tap water alone, at temperatures of -30 and -40 C in a deep freezer. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 30469174-4 2019 In the present study, the railway contact wires are coated with anti-icing mixtures of ethylene glycol/tap water and glycerol/tap water at various ratios (v/v %) as well as with tap water alone, at temperatures of -30 and -40 C in a deep freezer. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 30469174-4 2019 In the present study, the railway contact wires are coated with anti-icing mixtures of ethylene glycol/tap water and glycerol/tap water at various ratios (v/v %) as well as with tap water alone, at temperatures of -30 and -40 C in a deep freezer. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 30469174-4 2019 In the present study, the railway contact wires are coated with anti-icing mixtures of ethylene glycol/tap water and glycerol/tap water at various ratios (v/v %) as well as with tap water alone, at temperatures of -30 and -40 C in a deep freezer. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 30469174-7 2019 Conclusively, the fragments coated with 40/60 and 60/40 (v/v %) ratios of ethylene glycol or glycerol with tap water, as compared with the uncoated fragments, are shown to have been effectively de-iced. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 30469174-8 2019 The surface-characterizations data thus indicate that mixtures of glycerol or ethylene glycol with tap water can be practical de-icing agents for application to railway contact wires. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 30316091-1 2019 People are exposed to chlorinated by-products (CBPs) through the consumption of cold tap water (CTW) (ingestion, inhalation, dermal contact) but also through the use of hot tap water (HTW) in such activities as showering and bathing (inhalation, dermal contact). Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 30789878-3 2019 Untreated, unboiled city A tap water (i.e., well water) was the only exposure significantly associated with illness (odds ratio [OR] = 7.84; 95% confidence interval [CI] = 1.69-36.36). Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 30789878-3 2019 Untreated, unboiled city A tap water (i.e., well water) was the only exposure significantly associated with illness (odds ratio [OR] = 7.84; 95% confidence interval [CI] = 1.69-36.36). Water 49-54 nuclear RNA export factor 1 Homo sapiens 27-30 30316091-2 2019 This study focuses on the impact of residential water heating on CBP levels in tap water. Water 48-53 nuclear RNA export factor 1 Homo sapiens 79-82 31364530-5 2019 A 1:1 case-control study conducted and showed that tap water consumption significantly associated with developing symptoms of gastroenteritis (odds ratio = 36.9, P = 0.018). Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 30628337-5 2019 However, it dramatically decreased to 10.1 kPa after washing with tap water on day 13, indicating that the cake layer was the main fouling mechanism. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 30628337-9 2019 The corresponding TMP only increased to 19.5 kPa after running for 12 d, which decreased to 5.6 kPa after washing with tap water on day 13. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 30628337-12 2019 The TMP increased to 38.0 kPa on day 12, while it decreased to 3.8 kPa after washing with tap water on day 13. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 30628337-15 2019 After washing with tap water, the TMP decreased to 2.3 kPa on day 13, and the average pollutant removal efficiency was as high as 58.6%. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 30336414-1 2019 The reduction of tap water consumption in all activity sectors, including the building industry, is crucial to the sustainability of water resources. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 30336414-7 2019 Mortar properties such as setting time, workability, flexural strength, compressive strength and morphology were obtained for 100% effluent and tap water/effluent mixtures (50:50) with and without ED-T pre-treatment. Water 148-153 nuclear RNA export factor 1 Homo sapiens 144-147 30391910-7 2019 We test the use of this differential sensor for the selective detection of the water pollutant 17beta-estradiol in buffer and tap water. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 30391910-8 2019 Consistent detection results can be obtained with and without interferences of pH variations, and in tap water where unknown interferences are present. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 28422353-3 2019 The standard procedure of rinsing impressions under tap water immediately after removal from the mouth eliminates microorganisms along with saliva and blood. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 30474728-5 2019 To enrich for methanotrophs, we designed and operated four laboratory-scale, continuously methane-fed column reactors, inoculated with filter sand and one control column fed with tap water. Water 183-188 nuclear RNA export factor 1 Homo sapiens 179-182 31686572-5 2019 Although the sparse knowledge on the ecology and physiology of Betaproteobacteria thriving in tap or bottled natural mineral/spring drinking water (DW) is an evidence of this review, it is demonstrated that DW holds a high diversity of Betaproteobacteria, whose presence may not be innocuous. Water 141-146 nuclear RNA export factor 1 Homo sapiens 65-68 30717687-6 2019 Eyestrain, eye discharge, and dryness decreased with tap water (P = 0.020), Eye Shampoo (P = 0.036), and Eye Brush (P = 0.014), respectively. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 30388647-3 2019 The results showed that although the average concentration of total antibiotics in tap water was 10 ng/L, the concentrations reached hundreds or even thousands of ng/L in all the other sections, indicating antibiotics entering water system through human or pets discharge. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 30308921-7 2019 The results showed that the exposure patterns of phthalates varied among the population groups with different water intakes, and the health risk was higher for people ingesting the boiled tap water than that of the groups consuming bottled water (purified water) and filtered water with filter cartridge containing activated carbon. Water 192-197 nuclear RNA export factor 1 Homo sapiens 188-191 30308921-7 2019 The results showed that the exposure patterns of phthalates varied among the population groups with different water intakes, and the health risk was higher for people ingesting the boiled tap water than that of the groups consuming bottled water (purified water) and filtered water with filter cartridge containing activated carbon. Water 192-197 nuclear RNA export factor 1 Homo sapiens 188-191 30308921-7 2019 The results showed that the exposure patterns of phthalates varied among the population groups with different water intakes, and the health risk was higher for people ingesting the boiled tap water than that of the groups consuming bottled water (purified water) and filtered water with filter cartridge containing activated carbon. Water 192-197 nuclear RNA export factor 1 Homo sapiens 188-191 30308921-7 2019 The results showed that the exposure patterns of phthalates varied among the population groups with different water intakes, and the health risk was higher for people ingesting the boiled tap water than that of the groups consuming bottled water (purified water) and filtered water with filter cartridge containing activated carbon. Water 192-197 nuclear RNA export factor 1 Homo sapiens 188-191 30821496-5 2019 DNA LBL coatings reduced inorganic fouling from tap water by 90% when incubated statically or under flow conditions mimicking surfaces in heat exchangers. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 30899312-5 2018 Although Set Plus is disposable, the patient reused the product by cleansing with tap water. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 30273770-7 2018 The results of the analysis of popular posts identified innovative ways some water businesses are using Facebook posts to promote the health benefits of tap water consumption, water conservation behaviours and responsible wastewater practices. Water 77-82 nuclear RNA export factor 1 Homo sapiens 153-156 30522523-5 2018 In addition to hygiene and dietary habits, we found that the composition of tap water was related to important changes in the abundance of several bacterial genera. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 30563245-5 2018 Moreover, the extent application of this simple assay was successfully demonstrated in tap water samples with high reliability and applicability, indicating remarkable application in real samples. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 30189517-3 2018 Using a US pregnancy cohort, we assessed the impact of receiving well water arsenic test results on subsequent use of arsenic-contaminated tap water. Water 70-75 nuclear RNA export factor 1 Homo sapiens 139-142 29697009-0 2018 Factors associated with drinking and being satisfied with tap water in Indigenous communities in Saskatchewan, Canada. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 29697009-1 2018 Previous studies have described concerns regarding tap water in Indigenous communities, yet there is little information on participants who report drinking their tap water and being satisfied with its quality. Water 166-171 nuclear RNA export factor 1 Homo sapiens 162-165 29697009-4 2018 Less than one-quarter of participants (23.4%) drank tap water and were satisfied with its quality. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 30630284-3 2018 In this study, we isolated an Acanthamoeba CJW/W1 strain from tap water in Wuxi, Jiangsu Province, China. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 30630284-8 2018 This is the first report of an Acanthamoeba strain isolated from tap water in Wuxi, China. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 30195162-3 2018 The study was conducted at ambient temperature and LFL was fed to the bioreactor in gradually increasing concentration mixed with tap water (from 20% to 100%). Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 30336121-0 2018 Identification of free-living amoebae isolated from tap water in Istanbul, Turkey. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 30336121-10 2018 With this study, we established Acanthamoeba genotype T4 and Vermamoeba vermiformis as contaminants of tap water in Istanbul. Water 107-112 nuclear RNA export factor 1 Homo sapiens 103-106 30240071-7 2018 Very impressively, the PVA/PAANa hydrogel can easily distinguish tap water from deionized water, and its detection limit of metal cations can be as low as 10-4 mol L-1 . Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 30189517-3 2018 Using a US pregnancy cohort, we assessed the impact of receiving well water arsenic test results on subsequent use of arsenic-contaminated tap water. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 30189517-5 2018 Upon enrollment participants provided a tap water sample which was tested for arsenic using ICP-MS. During pregnancy and every four months after, participants were asked their extent of tap water use for drinking, cooking and mixing infant formula. Water 190-195 nuclear RNA export factor 1 Homo sapiens 186-189 30189517-6 2018 Logistic regression was used to estimate the odds of tap water use at one year post-partum in relation to baseline tap water use and arsenic concentration. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 30189517-6 2018 Logistic regression was used to estimate the odds of tap water use at one year post-partum in relation to baseline tap water use and arsenic concentration. Water 57-62 nuclear RNA export factor 1 Homo sapiens 115-118 30189517-6 2018 Logistic regression was used to estimate the odds of tap water use at one year post-partum in relation to baseline tap water use and arsenic concentration. Water 119-124 nuclear RNA export factor 1 Homo sapiens 53-56 30189517-6 2018 Logistic regression was used to estimate the odds of tap water use at one year post-partum in relation to baseline tap water use and arsenic concentration. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 30189517-7 2018 Compared to those who used tap water <50% of the time, mothers who reported using tap water for drinking and cooking >50% of time in their prenatal questionnaire had 8.54 times the odds of using their tap water at 1-year postpartum (95% CI: 5.37, 13.60). Water 31-36 nuclear RNA export factor 1 Homo sapiens 85-88 30189517-7 2018 Compared to those who used tap water <50% of the time, mothers who reported using tap water for drinking and cooking >50% of time in their prenatal questionnaire had 8.54 times the odds of using their tap water at 1-year postpartum (95% CI: 5.37, 13.60). Water 31-36 nuclear RNA export factor 1 Homo sapiens 85-88 30189517-7 2018 Compared to those who used tap water <50% of the time, mothers who reported using tap water for drinking and cooking >50% of time in their prenatal questionnaire had 8.54 times the odds of using their tap water at 1-year postpartum (95% CI: 5.37, 13.60). Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 30189517-7 2018 Compared to those who used tap water <50% of the time, mothers who reported using tap water for drinking and cooking >50% of time in their prenatal questionnaire had 8.54 times the odds of using their tap water at 1-year postpartum (95% CI: 5.37, 13.60). Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 30189517-7 2018 Compared to those who used tap water <50% of the time, mothers who reported using tap water for drinking and cooking >50% of time in their prenatal questionnaire had 8.54 times the odds of using their tap water at 1-year postpartum (95% CI: 5.37, 13.60). Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 30189517-7 2018 Compared to those who used tap water <50% of the time, mothers who reported using tap water for drinking and cooking >50% of time in their prenatal questionnaire had 8.54 times the odds of using their tap water at 1-year postpartum (95% CI: 5.37, 13.60). Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 30189517-8 2018 After adjusting for frequency of prenatal tap water use, mothers were less likely to use tap water for drinking and cooking (OR = 0.34, 95% CI: 0.19, 0.60) and for mixing formula (OR = 0.45, 95% CI: 0.24, 0.86) if the high arsenic concentration (>10 mug/L) was known to them. Water 46-51 nuclear RNA export factor 1 Homo sapiens 89-92 30189517-8 2018 After adjusting for frequency of prenatal tap water use, mothers were less likely to use tap water for drinking and cooking (OR = 0.34, 95% CI: 0.19, 0.60) and for mixing formula (OR = 0.45, 95% CI: 0.24, 0.86) if the high arsenic concentration (>10 mug/L) was known to them. Water 93-98 nuclear RNA export factor 1 Homo sapiens 42-45 30189517-8 2018 After adjusting for frequency of prenatal tap water use, mothers were less likely to use tap water for drinking and cooking (OR = 0.34, 95% CI: 0.19, 0.60) and for mixing formula (OR = 0.45, 95% CI: 0.24, 0.86) if the high arsenic concentration (>10 mug/L) was known to them. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 30189517-9 2018 Our findings suggest that providing well water test results during pregnancy may reduce subsequent maternal use of iAs contaminated tap water for drinking, cooking, and mixing infant formula. Water 41-46 nuclear RNA export factor 1 Homo sapiens 132-135 30189517-9 2018 Our findings suggest that providing well water test results during pregnancy may reduce subsequent maternal use of iAs contaminated tap water for drinking, cooking, and mixing infant formula. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 30189556-1 2018 BACKGROUND: Despite the rigorous control of tap water quality, substantial price differences, and environmental concerns, bottled water consumption has increased in recent decades. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 30189556-6 2018 RESULTS: The two consumer groups showed "polarized" ratings regarding perceived quality/hygiene, health risks and taste for bottled and tap water, indicating that the two consumer groups substantially diverged in their beliefs. Water 140-145 nuclear RNA export factor 1 Homo sapiens 136-139 30477133-3 2018 This work presents an aging of 11 pH electrodes within approximately 600 days in tap water. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 30290983-2 2018 Glucomannan powder, a dietary fiber supplement, can be mixed with tap water to form a gel that may be a field-expedient substitute for USTG. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 30477133-10 2018 As a result of this work, a model of the aging process of pH electrodes in tap water can be constructed and subsequently, the measurement accuracy in the periods between calibrations can be improved. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 30351033-10 2018 Furthermore, to our knowledge, it is the first study to compare biofilm in a tap water-fed, bench-scale simulated distribution system to biofilm on water mains from the full-scale system supplying the tap water. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 30103048-1 2018 Occurrence of residual endotoxin activity (ET) in dialysis water and also tap water as its source is a matter of great concern to medical professionals conducting dialysis therapy at healthcare facilities (HCFs). Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 29945113-4 2018 The fabricated label-free fluorescence aptasensor is not only conveniently but also effectively applicable used for analysis of Hg2+ ion in blood serum and tap water samples and the recovery range is of 96.0%-105.7%. Water 160-165 nuclear RNA export factor 1 Homo sapiens 156-159 30425313-8 2018 The main modifiable risk factor identified in this study was the consumption of tap or osmosis drinking water. Water 104-109 nuclear RNA export factor 1 Homo sapiens 80-83 30252454-5 2018 Therefore, enhanced stability of lead phosphate particles was observed, suggesting that although addition of excess phosphate can lower the dissolved lead concentrations in tap water, it may increase concentrations of particulate lead. Water 177-182 nuclear RNA export factor 1 Homo sapiens 173-176 30232522-5 2018 Additionally, the probe was successfully utilized to determine HClO in tap water, exogenous HClO in HeLa cells, and endogenous HClO in MCF-7 cells with a low detection limit and cytotoxicity. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 30031366-12 2018 Under the synergistic influence of water constituents (including acidity and alkalinity, ion species and dissolved organic substances), various water matrices greatly affected the degradation rate of TC-HCl, with the highest removal efficiency of 78.9% in natural seawater, followed by reservoir water (75.0%), tap water (62.3%), deionized water (49.8%), reverse osmosis concentrate (32.7%) and pharmaceutical wastewater (18.9%). Water 144-149 nuclear RNA export factor 1 Homo sapiens 311-314 28612312-5 2018 Tap water in households receiving trucked water contained less than the recommended 0.2 mg/L of free chlorine, while piped drinking water in Iqaluit complied with Health Canada guidelines for residual chlorine (i.e. >0.2 mg/L free chlorine). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 28612312-5 2018 Tap water in households receiving trucked water contained less than the recommended 0.2 mg/L of free chlorine, while piped drinking water in Iqaluit complied with Health Canada guidelines for residual chlorine (i.e. >0.2 mg/L free chlorine). Water 42-47 nuclear RNA export factor 1 Homo sapiens 0-3 28612312-5 2018 Tap water in households receiving trucked water contained less than the recommended 0.2 mg/L of free chlorine, while piped drinking water in Iqaluit complied with Health Canada guidelines for residual chlorine (i.e. >0.2 mg/L free chlorine). Water 42-47 nuclear RNA export factor 1 Homo sapiens 0-3 30515390-16 2018 Consumption of coconut water significantly increased urinary citrate (29%, p=0.02), urinary potassium (130%, p=0.01), and urinary chloride (37%, p=0.03), without affecting urine pH (p=0.16) or volume beyond that of tap water (p=1.00). Water 23-28 nuclear RNA export factor 1 Homo sapiens 215-218 29857026-9 2018 FINDINGS: A total of 139 clinical specimens of P. aeruginosa and 19 tap water samples were analysed. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 29857026-12 2018 Surprisingly, tap water was colonized with a single PA-OprD strain during both periods, but this single clone has never been isolated from clinical specimens. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 30056322-11 2018 Compared to ultrapure water, equal or higher removal efficiency was observed for HAAs spiked to tap water. Water 22-27 nuclear RNA export factor 1 Homo sapiens 96-99 30056322-11 2018 Compared to ultrapure water, equal or higher removal efficiency was observed for HAAs spiked to tap water. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 30031366-12 2018 Under the synergistic influence of water constituents (including acidity and alkalinity, ion species and dissolved organic substances), various water matrices greatly affected the degradation rate of TC-HCl, with the highest removal efficiency of 78.9% in natural seawater, followed by reservoir water (75.0%), tap water (62.3%), deionized water (49.8%), reverse osmosis concentrate (32.7%) and pharmaceutical wastewater (18.9%). Water 144-149 nuclear RNA export factor 1 Homo sapiens 311-314 30031366-12 2018 Under the synergistic influence of water constituents (including acidity and alkalinity, ion species and dissolved organic substances), various water matrices greatly affected the degradation rate of TC-HCl, with the highest removal efficiency of 78.9% in natural seawater, followed by reservoir water (75.0%), tap water (62.3%), deionized water (49.8%), reverse osmosis concentrate (32.7%) and pharmaceutical wastewater (18.9%). Water 144-149 nuclear RNA export factor 1 Homo sapiens 311-314 30031366-12 2018 Under the synergistic influence of water constituents (including acidity and alkalinity, ion species and dissolved organic substances), various water matrices greatly affected the degradation rate of TC-HCl, with the highest removal efficiency of 78.9% in natural seawater, followed by reservoir water (75.0%), tap water (62.3%), deionized water (49.8%), reverse osmosis concentrate (32.7%) and pharmaceutical wastewater (18.9%). Water 144-149 nuclear RNA export factor 1 Homo sapiens 311-314 30285963-0 2018 Drinking water in West Virginia (USA): tap water or bottled water - what is the right choice for college students? Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 29920408-7 2018 Consequently, a 50% lower methadone degradation rate was observed when deionized (DI) water was replaced with tap water. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 30207682-11 2018 The sensor was also found very efficient for MV determination in real water systems (well, spring, and tap water) despite the decrease of sensitivity due to the presence of interfering species. Water 107-112 nuclear RNA export factor 1 Homo sapiens 103-106 29894954-0 2018 A highly selective fluorescent probe for the detection of hypochlorous acid in tap water and living cells. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 29894954-5 2018 Moreover, the probe was used for the detection of HClO in tap water through the home-made test paper. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 30281598-9 2018 In the case control study, typhoid was found to be associated with ever using tap water from the municipal supply (OR = 4.29, 95% CI 2.20-8.38). Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 29978422-0 2018 DNA extraction from amoebal isolates and genotype determination of Acanthamoeba from tap water in Latvia. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 29978422-3 2018 This is the first study in Latvia describing Acanthamoeba detection by molecular techniques and genotyping using tap water from different sources. Water 117-122 nuclear RNA export factor 1 Homo sapiens 113-116 29978422-5 2018 The results indicate that tap water in Latvia may be a source of Acanthamoeba that is potentially pathogenic to humans. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 30285963-6 2018 Results indicated that a third of the student population primarily used bottled water for drinking purposes at home, while 39% used a filter at home and 26% drank water directly from the tap. Water 163-168 nuclear RNA export factor 1 Homo sapiens 187-190 30728998-10 2018 Conclusion: Based on the results of the tap-water quality application of POU-WT systems are not recommended in Tehran and Rasht, and regarding the outputs of these systems, side effects of softened water, lack of Fluoride and a remarkable increase of the number of bacteria should be considered. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 30283424-5 2018 Irrespective of differences in treatment plants, tap water bacterial communities in the distinct networks converged and highly resembled the flushed water communities. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 30283424-5 2018 Irrespective of differences in treatment plants, tap water bacterial communities in the distinct networks converged and highly resembled the flushed water communities. Water 149-154 nuclear RNA export factor 1 Homo sapiens 49-52 30345835-9 2018 In conclusion, a carbonated water mouthwash can significantly reduce oropharyngeal NO compared to a tap water mouthwash at expiratory flows of 30-300 mL/s without affecting the CANO and DawNO. Water 104-109 nuclear RNA export factor 1 Homo sapiens 100-103 29890477-8 2018 In a subset of study participants who did not use home water filters, consumption of at least some amount of non-boiled tap water reported in a monthly recall survey was associated with 11.1 (1.2; 100.0) and 0.6 (0.1; 2.5) aORs of immunoconversion to Cryptosporidium before and after the new water treatment plant construction, respectively. Water 55-60 nuclear RNA export factor 1 Homo sapiens 120-123 29890477-9 2018 Among individuals who used home water filters, associations between non-boiled tap water consumption and Cryptosporidium immunoconversion were not significant before and after new plant construction with aORs of 0.8 (0.2; 3.3) and 0.3 (0.1; 1.6), respectively. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 30283424-6 2018 Piping biofilm and sediment communities therefore largely determine the final tap water microbial quality, attenuating the impact of water source and treatment strategy and highlighting the fundamental role of local physicochemical conditions and microbial processes within infrastructure micro-niches. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 30200555-9 2018 Compared to traditional method, we obtained the conversion formula between the concentration of residual-chlorine in tap water and the concentration of hypochlorite detected by the proposed colorimetric assay, which is Cresidual-chlorine = 0.24 CNaClO. Water 121-126 nuclear RNA export factor 1 Homo sapiens 117-120 30319697-8 2018 Tap water distribution was poor in this slum area. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 30218202-5 2018 The matrix-matching calibration method was performed in order to improve the accuracy of cadmium quantification in tap water and the recovery results obtained were as follows: 88.56 +- 8.92 and 97.43 +- 9.76, for 6.0 and 8.0 ng/mL of cadmium-spiked tap water samples, respectively. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 30200555-10 2018 Finally, the real application of the colorimetric assay in tap water was successfully performed, and the accuracy of the colorimetric method can reach from -6.78% to +8.53%. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 30196635-0 2018 [The transformation of microcystin-LR during tap water treatment process and analysis of its degradation products]. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 29879534-6 2018 The radon concentrations in tap water samples were found to be in the range of 0.98 Bq/L-27.28 Bq/L. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 30189640-10 2018 A similar catalytic performance was also observed for three 4-nitrophenol spiked real water samples (e.g., surface water, tap water, and industrial dyeing wastewater). Water 86-91 nuclear RNA export factor 1 Homo sapiens 122-125 30409949-7 2018 Regular tap water was used for immersion in the control group. Water 12-17 nuclear RNA export factor 1 Homo sapiens 8-11 30045118-0 2018 Real-Time Monitoring of Gross Beta Radioactivity in Tap Water and Committed Effective Dose. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 30045118-3 2018 Finally, the annual committed effective doses to children and adults who drank the tap water for a long time were estimated. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 30045118-4 2018 The results showed that the gross beta radioactivity in tap water was 0.09 +- 0.03 Bq L using the scintillating fiber array system and 0.076 +- 0.009 Bq L using the evaporation concentration method. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 30221833-6 2018 In addition, the change in PA blood flow in response to immersion in carbonated water correlated with those of skin blood flow (P = 0.005) but not oxyhemoglobin concentration (P = 0.765) and tissue oxygenation index (P = 0.136) while no relations was found for tap water immersion. Water 80-85 nuclear RNA export factor 1 Homo sapiens 261-264 29710648-3 2018 The predominant compounds in tap water were perfluorohexane sulfonate (PFHxS), perfluoropentanoic acid (PFPeA), perfluorohexanoic acid (PFHxA), perfluorooctanoic acid (PFOA), tris(2-chloroethyl) phosphate (TCEP), tris(chloroisopropyl) phosphate (TCIPP), and tris(2-butoxyethyl) phosphate (TBOEP). Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 29710648-4 2018 Tap water originating from the Nakdong River within an industrial complex showed a notably higher PFHxS proportion to total PFASs. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 29660725-3 2018 However, people are exposed to tap water inside the house while water may stay in the plumbing premise for several hours prior to reaching the tap. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 29710648-5 2018 In addition, significantly higher PFAS levels were found in river-originating tap water than in lake/reservoir-originating tap water (Mann-Whitney U test, p<0.05). Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 29710648-5 2018 In addition, significantly higher PFAS levels were found in river-originating tap water than in lake/reservoir-originating tap water (Mann-Whitney U test, p<0.05). Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 29660725-3 2018 However, people are exposed to tap water inside the house while water may stay in the plumbing premise for several hours prior to reaching the tap. Water 35-40 nuclear RNA export factor 1 Homo sapiens 143-146 30078496-8 2018 In addition, a case study of Taipei City indicated that MSW disposal fees should reflect not only household population (P) but also tap water penetration (W). Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 29660725-3 2018 However, people are exposed to tap water inside the house while water may stay in the plumbing premise for several hours prior to reaching the tap. Water 64-69 nuclear RNA export factor 1 Homo sapiens 143-146 29660725-4 2018 Depending on stagnation period and plumbing premise, concentrations of Pb in tap water can be significantly higher than the WDS leading to higher intake of Pb than the values from WDS or WTP. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 29660725-13 2018 The models can be used for predicting Pb in tap water, which can assist to better protect the humans. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 29710648-7 2018 Finally, the average human exposure via tap water consumption was estimated for PFASs (46.8ng/person/day) and OPFRs (254ng/person/day). Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 30252663-1 2018 In this study, for the first time, the influence of the design of conventional membrane diffusers on the volumetric mass transfer coefficient (kLa) and bubble size in tap water (TW) and saline water (SW) was investigated (up to 15 g/L NaCl). Water 171-176 nuclear RNA export factor 1 Homo sapiens 167-170 30109505-6 2018 The temporal analysis revealed that the highest THM concentration occurred in April, both in tap water and in finished water, which was also shown by temporal cluster analysis. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 30111737-7 2018 In this work, we present a 19-month time series measuring nitrate, chloride, and sulfate in local precipitation, reservoir and household tap waters in order to better understand the relationship of the hydrologic residence time on the tap water chemistry, as well as to evaluate the anion concentrations. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 30111737-8 2018 The highest chloride tap water concentration, 6.9 mM, occurred in early February 2011, while increases in nitrate occurred in both early summer and the middle of winter. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 30111737-10 2018 Similarly, the tap water had concentrations of chloride and sulfate higher than reservoir water, while nitrate was similar to reservoir water. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 30111737-11 2018 Tap water had higher fluoride and sulfate concentrations, suggesting that they are added during the treatment of the reservoir water prior to residential distribution. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 30111737-11 2018 Tap water had higher fluoride and sulfate concentrations, suggesting that they are added during the treatment of the reservoir water prior to residential distribution. Water 127-132 nuclear RNA export factor 1 Homo sapiens 0-3 30111761-2 2018 In Finland, tap water is the main source of drinking water, and thus the nitrite in tap water increases nitrite exposure. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 30111761-2 2018 In Finland, tap water is the main source of drinking water, and thus the nitrite in tap water increases nitrite exposure. Water 16-21 nuclear RNA export factor 1 Homo sapiens 84-87 30111761-2 2018 In Finland, tap water is the main source of drinking water, and thus the nitrite in tap water increases nitrite exposure. Water 53-58 nuclear RNA export factor 1 Homo sapiens 12-15 30111761-2 2018 In Finland, tap water is the main source of drinking water, and thus the nitrite in tap water increases nitrite exposure. Water 53-58 nuclear RNA export factor 1 Homo sapiens 84-87 30111761-2 2018 In Finland, tap water is the main source of drinking water, and thus the nitrite in tap water increases nitrite exposure. Water 53-58 nuclear RNA export factor 1 Homo sapiens 12-15 30111761-2 2018 In Finland, tap water is the main source of drinking water, and thus the nitrite in tap water increases nitrite exposure. Water 53-58 nuclear RNA export factor 1 Homo sapiens 84-87 30081519-6 2018 The presence of fungi in different types of water has been thoroughly investigated during the past 30 years only in Europe, and more than 400 different species were reported from ground-, surface-, and tap-water. Water 206-211 nuclear RNA export factor 1 Homo sapiens 202-205 30082638-8 2018 After adjusting for confounders, the occurrence of diarrhoea was statistically significantly associated with sourcing water from an indoor tap (Adjusted Odds Ratio (AOR): 2.73, 95% CI: 2.73, 1.14-6.56) and storing cooked/perishable food in non-refrigerated conditions (AOR: 2.17, 95% CI: 2.17, 1.44-3.26). Water 118-123 nuclear RNA export factor 1 Homo sapiens 139-142 29948709-6 2018 The result shows that NWD made from tap water helps the engine to reduce nitrogen oxide (NOx) by 32%. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 29684495-7 2018 The ranking order of metals concentrations in the tap drinking water was Zn > Pb > As > Co > Hg. Water 63-68 nuclear RNA export factor 1 Homo sapiens 50-53 30082812-6 2018 However, after leaving drinking water treatment plants, corrosion by-products released from distribution pipes or in-home premise plumbing can release incidental nanoparticles into tap water. Water 32-37 nuclear RNA export factor 1 Homo sapiens 181-184 30067239-3 2018 This study aimed to reveal actual water intakes from tap water and other types of drinks, and to explore the relationships between these intakes. Water 34-39 nuclear RNA export factor 1 Homo sapiens 53-56 30067239-5 2018 Tap water intake negatively correlated with bottled water and soft drink intakes, suggesting a mutually complementary relationship. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 30067239-5 2018 Tap water intake negatively correlated with bottled water and soft drink intakes, suggesting a mutually complementary relationship. Water 52-57 nuclear RNA export factor 1 Homo sapiens 0-3 30067239-6 2018 We propose an index, potential Tap Water Intake (pTWI), calculated by adding soft drinks and bottled water to tap water intake. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 30067239-6 2018 We propose an index, potential Tap Water Intake (pTWI), calculated by adding soft drinks and bottled water to tap water intake. Water 35-40 nuclear RNA export factor 1 Homo sapiens 110-113 30067239-6 2018 We propose an index, potential Tap Water Intake (pTWI), calculated by adding soft drinks and bottled water to tap water intake. Water 101-106 nuclear RNA export factor 1 Homo sapiens 31-34 30067239-6 2018 We propose an index, potential Tap Water Intake (pTWI), calculated by adding soft drinks and bottled water to tap water intake. Water 114-119 nuclear RNA export factor 1 Homo sapiens 31-34 30067239-6 2018 We propose an index, potential Tap Water Intake (pTWI), calculated by adding soft drinks and bottled water to tap water intake. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 30067239-7 2018 Mean per-capita tap water intake across the entire Japanese population was estimated at 1.28 L/d, whereas mean pTWI was estimated at 1.65 L/d. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 33947175-0 2018 Oxygen and Hydrogen Isotopes in Human Hair and Tap Water: Modeling Relationships in a Modern Mexican Population. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 33947175-2 2018 The purpose of this study was twofold: to quantify the relationship between isotopes in Mexican hair and tap water, in order to understand the impact of water stress and differing socioeconomic status on accurate predictions of drinking water; and to determine whether currently existing semimechanistic models can accurately represent the relationship between hair and tap water. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 33947175-4 2018 Isotope values in tap water ranged from -11.4% to -4.3% and -79.1% to -22.5%, and in hair from +9.5% to +16.1% and -90.8% to -53.7%, for delta18O and delta2H, respectively. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 33947175-12 2018 They found that, although O and H isotopes in water and hair maintained similar geographic distributions, O and H isotopes in tap water explained only a small part of the variation observed in hair samples. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 30036962-0 2018 Effectiveness of Prevailing Flush Guidelines to Prevent Exposure to Lead in Tap Water. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 29752024-12 2018 Individuals using treated water for drinking or using own tap as the source of water were more likely to receive the OCV (aOR: 1.23; 95% CI = 1.17-1.29 and aOR: 1.14; 95% CI = 1.02-1.25 respectively) than their counterpart. Water 79-84 nuclear RNA export factor 1 Homo sapiens 58-61 30036962-1 2018 Flushing tap water is promoted as a low cost approach to reducing water lead exposures. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 29902377-9 2018 This investigation suggests water-main biofilms may serve as a source of Legionella for tap water and premise plumbing systems, and residual chloramine may aid in reducing their abundance. Water 28-33 nuclear RNA export factor 1 Homo sapiens 88-91 29902377-9 2018 This investigation suggests water-main biofilms may serve as a source of Legionella for tap water and premise plumbing systems, and residual chloramine may aid in reducing their abundance. Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 29875071-1 2018 The presence of water disinfection byproducts (DBPs) in tap water, resulting from disinfection processes involving chlorination or chloramination, increases the mutagenicity of the water and may pose adverse health effects. Water 16-21 nuclear RNA export factor 1 Homo sapiens 56-59 30533993-1 2018 Introduction and Objectives: Tap water iontophoresis is a promising therapy for palmoplantar hyperhidrosis. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 29875071-1 2018 The presence of water disinfection byproducts (DBPs) in tap water, resulting from disinfection processes involving chlorination or chloramination, increases the mutagenicity of the water and may pose adverse health effects. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 29875071-4 2018 Studies, primarily using the Salmonella mutagenicity assay, have continued to show that chlorination or chloramination of source waters results in finished, tap, or swimming pool/spa water that is more mutagenic than the original source water. Water 129-134 nuclear RNA export factor 1 Homo sapiens 157-160 29573632-1 2018 The general consensus is that the abundance of tap water bacteria is greatly influenced by water purification and distribution. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 29573632-1 2018 The general consensus is that the abundance of tap water bacteria is greatly influenced by water purification and distribution. Water 91-96 nuclear RNA export factor 1 Homo sapiens 47-50 29573632-3 2018 For the first time, this full-scale study has captured and identified the proportional contribution of the source water, treated water, and distribution system in shaping the tap water bacterial community based on their microbial community fingerprints using the Bayesian "SourceTracker" method. Water 114-119 nuclear RNA export factor 1 Homo sapiens 175-178 29573632-3 2018 For the first time, this full-scale study has captured and identified the proportional contribution of the source water, treated water, and distribution system in shaping the tap water bacterial community based on their microbial community fingerprints using the Bayesian "SourceTracker" method. Water 129-134 nuclear RNA export factor 1 Homo sapiens 175-178 29573632-3 2018 For the first time, this full-scale study has captured and identified the proportional contribution of the source water, treated water, and distribution system in shaping the tap water bacterial community based on their microbial community fingerprints using the Bayesian "SourceTracker" method. Water 129-134 nuclear RNA export factor 1 Homo sapiens 175-178 29573632-7 2018 The planktonic bacteria in the treated water was the major contributor to planktonic bacteria in the tap water (17.7-54.1%). Water 39-44 nuclear RNA export factor 1 Homo sapiens 101-104 29573632-9 2018 In return, the loose deposits and biofilm showed a significant influence on tap water planktonic and particle-associated bacteria, which were location dependent and influenced by hydraulic changes. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 29573632-10 2018 This was revealed by the increased contribution of loose deposits to tap water planktonic bacteria (from 2.5% to 38.0%) and an increased contribution of biofilm to tap water particle-associated bacteria (from 5.9% to 19.7%) caused by possible hydraulic disturbance from proximal to distal regions. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 29573632-11 2018 Therefore, our findings indicate that the tap water bacteria could possibly be managed by selecting and operating the purification process properly and cleaning the distribution system effectively. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 29934501-1 2018 This paper details an investigation into the characteristic "plink" sound produced by water droplets impacting a liquid surface, such as those falling from a dripping tap. Water 86-91 nuclear RNA export factor 1 Homo sapiens 167-170 29615322-8 2018 The low relative standard deviations from 1.6-3.1% for tap water and 2.5-5.4% for lake water was achieved. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 29588495-1 2018 What happens to tap water when you are away from home? Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 29588495-4 2018 Here, we track tap water microbiome assembly in situ, showing that bacterial community composition changes rapidly from the city supply following ~6-day stagnation, along with an increase in cell count from 103 cells/mL to upwards of 7.8 x 105 cells/mL. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 29567160-1 2018 In this work an electrochemical procedure for Cr(VI) flow based determination in tap water is presented. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 29567160-4 2018 Under optimal conditions, the electrochemical sensor offered an excellent response to Cr(VI) and the limit of detection estimated from 3sigma was 0.5 microg L-1 (n = 3) allowing the analysis of tap water samples. Water 198-203 nuclear RNA export factor 1 Homo sapiens 194-197 29992101-5 2018 For tap water, satisfying flocculation efficiencies (above 60 %) were only reached for autoclaved water samples. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 29992101-5 2018 For tap water, satisfying flocculation efficiencies (above 60 %) were only reached for autoclaved water samples. Water 98-103 nuclear RNA export factor 1 Homo sapiens 4-7 29602018-3 2018 For this purpose, 35 mg of caffeine were given to six healthy volunteers after a 10 h overnight together with 240 mL of tap water either on a fasted stomach or 30 min after the high-caloric, high-fat breakfast recommended for bioavailability/bioequivalence (BA/BE) studies. Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 29735091-1 2018 Tap water is used in France to reconstitute powder infant formula, although it is not sterile and possibly contaminated by microbiological and chemical hazards. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 29735091-2 2018 The present study aims to quantify risks of using tap water in France for the preparation of infant formula, during the first six months of life. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 29735091-8 2018 Consuming infant formula rehydrated with un-boiled tap water during the first six months of life led to a total of 2250 DALYs per 100,000 infants (90% uncertainty interval [960; 7650]) for Cryptosporidium due to diarrhea, and 1 DALY [0.4; 2] for arsenic due to expected lifetime risk of lung and bladder cancer as a result of early exposure in life. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 29735091-12 2018 This multi-risk assessment model could help public health authorities and managers in evaluating both microbiological and chemical safety issues associated with using infant formula prepared with tap water. Water 200-205 nuclear RNA export factor 1 Homo sapiens 196-199 29952326-4 2018 Most respondents reported that they believe their drinking water is of high quality, with 81.4% responding that they believe their tap water is safe to drink. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 29952326-5 2018 An even larger number, 92.1%, of those receiving their water from private sources believe their tap water is safe. Water 55-60 nuclear RNA export factor 1 Homo sapiens 96-99 29952326-5 2018 An even larger number, 92.1%, of those receiving their water from private sources believe their tap water is safe. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 29952326-6 2018 Conversely, only 57.0% of respondents who consume bottled water as their primary source of drinking water believe their tap water is safe to drink. Water 58-63 nuclear RNA export factor 1 Homo sapiens 120-123 29952326-6 2018 Conversely, only 57.0% of respondents who consume bottled water as their primary source of drinking water believe their tap water is safe to drink. Water 100-105 nuclear RNA export factor 1 Homo sapiens 120-123 29952326-6 2018 Conversely, only 57.0% of respondents who consume bottled water as their primary source of drinking water believe their tap water is safe to drink. Water 100-105 nuclear RNA export factor 1 Homo sapiens 120-123 29733189-8 2018 (iii) However, and in contrast to the behavior observed in GQD solutions, the fluorescence of the composite remains unaltered over a wide pH range and in the presence of different ions commonly found in tap water. Water 207-212 nuclear RNA export factor 1 Homo sapiens 203-206 29684671-4 2018 Our results also indicate the heterogeneities in the improving effects of clean water with respect to the coverage of tap water among citizens. Water 80-85 nuclear RNA export factor 1 Homo sapiens 118-121 29774656-5 2018 The accuracy and the applicability of the developed method was checked in tap water and two different wastewater samples by spiked recovery tests. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 29717354-8 2018 Long-term exposure to Cd and Cr through tap water consumption poses moderate carcinogenic health risks to the local residents. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 29684671-6 2018 However, the subsequent expansion of tap water could result in a continuous decline in the overall risk of deaths in the second phase. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 29519719-6 2018 He was given 0.4 mg nitroglycerin dissolved in 10 mL tap water orally, and obtained complete relief of symptoms within 2 min. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 29608983-7 2018 The rank order of drinking water resources based on the concentration of radon 222 was Spring > Spring and Well > Well > Spring and Qanat > Tap water. Water 27-32 nuclear RNA export factor 1 Homo sapiens 152-155 29633676-8 2018 The analysis of water samples revealed the presence of bacterial indicators of faecal contamination in the water used in the resort as well as in other areas of the municipal water network, linking the NoV gastroenteritis outbreak to tap water pollution from sewage leakage. Water 16-21 nuclear RNA export factor 1 Homo sapiens 234-237 28903806-7 2018 Matrix-matching was used to overcome any low recovery results obtained with tap water and municipal wastewater. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 29426545-7 2018 The method has been applied to the analysis of these isomers in spiked tap water with recoveries from 99.0 ~ 102.9% and relative standard deviations (RSDs) for 5 successive measurements less than 5% were also acceptable. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 29900322-0 2018 Human health risk assessment data of trace elements concentration in tap water-Abeokuta South, Nigeria. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 29900322-3 2018 In this study, the concentration of fluoride in tap water varied at different locations, ranging from 0.48 mg/L to 1.84 mg/L with an average value of 1.23 mg/L while that of iron ranged from 0.02 to 2.96 mg/L. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 29458034-7 2018 There were good correlation between the two methods from tap water, contaminated water and river water samples were 0.9994, 0.9935 and 0.9967, respectively. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 29641556-4 2018 Of the tap water samples analyzed, 81% were found to contain anthropogenic particles. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 29641556-10 2018 Based on consumer guidelines, our results indicate the average person ingests over 5,800 particles of synthetic debris from these three sources annually, with the largest contribution coming from tap water (88%). Water 200-205 nuclear RNA export factor 1 Homo sapiens 196-199 29519124-0 2018 Selective Membrane Complexation and Uranium Isotopes Analysis in Tap Water and Seawater Samples. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 29519124-1 2018 The complexation of 238U and 234U in tap water and seawater after the use of a selective membrane was examined. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 29289846-2 2018 We previously found that Tl(III), generally considered the less stable oxidation state of thallium, is present both in the stream and in tap water distributed in the area, whereas acid mine drainages only contain Tl(I). Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 29508034-0 2018 Evaluation of on-line concentration coupled to liquid chromatography tandem mass spectrometry for the quantification of neonicotinoids and fipronil in surface water and tap water. Water 173-178 nuclear RNA export factor 1 Homo sapiens 169-172 29618130-0 2018 131I DOSE ESTIMATION FROM INTAKE OF TAP WATER IN THE EARLY PHASE AFTER FUKUSHIMA DAIICHI NUCLEAR POWER PLANT ACCIDENT. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 29206474-0 2018 Trace lithium in Texas tap water is negatively associated with all-cause mortality and premature death. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 29206474-2 2018 Using a larger dataset with several Texas counties, our study shows that lithium concentrations in tap water are negatively associated with all-cause mortality (r = -0.18, p = 0.006, 232 counties) and years of potential life lost (r = -0.22, p = 0.001, 214 counties). Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 29332797-10 2018 The method was successively applied to determine the concentrations of trace amounts of chloroacetic acids in tap water. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 29618130-2 2018 To study its effect, we estimated the internal exposure due to intake of tap water in the early phase after the accident. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 29332797-12 2018 However, enrichment with the present method is effective for determination of tap water quality by improving the limits of detection of HPLC-UV. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 29332797-13 2018 The standard addition test with real tap water samples shows good recoveries (94.9-109.6%). Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 29618130-3 2018 As the number of measured values of tap water following the accident was limited, 131I concentration in tap water was estimated by 1-compartment model using the deposition amount of radionuclides calculated by an atmospheric transport, dispersion and deposition simulation. Water 108-113 nuclear RNA export factor 1 Homo sapiens 104-107 29132004-8 2018 Negative perceptions of tap water were associated with lower odds of consuming tap water (ORPCAcomponent1=0.73, 95% CI 0.56-0.94; ORPCAcomponent2=0.67, 95% CI 0.49-0.93); women had higher odds of drinking purchased water compared to men (OR=1.90, 95% CI 1.11-3.26). Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 29470061-5 2018 Tap water samples collected across Fort Collins, CO, were tested with this method and validated against ICP-MS. We demonstrate the ability to quantify the copper content of tap water within 30% of a reference technique at levels ranging from 20 to 500 000 ppb. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 29132004-8 2018 Negative perceptions of tap water were associated with lower odds of consuming tap water (ORPCAcomponent1=0.73, 95% CI 0.56-0.94; ORPCAcomponent2=0.67, 95% CI 0.49-0.93); women had higher odds of drinking purchased water compared to men (OR=1.90, 95% CI 1.11-3.26). Water 28-33 nuclear RNA export factor 1 Homo sapiens 79-82 29132004-8 2018 Negative perceptions of tap water were associated with lower odds of consuming tap water (ORPCAcomponent1=0.73, 95% CI 0.56-0.94; ORPCAcomponent2=0.67, 95% CI 0.49-0.93); women had higher odds of drinking purchased water compared to men (OR=1.90, 95% CI 1.11-3.26). Water 83-88 nuclear RNA export factor 1 Homo sapiens 24-27 29132004-8 2018 Negative perceptions of tap water were associated with lower odds of consuming tap water (ORPCAcomponent1=0.73, 95% CI 0.56-0.94; ORPCAcomponent2=0.67, 95% CI 0.49-0.93); women had higher odds of drinking purchased water compared to men (OR=1.90, 95% CI 1.11-3.26). Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 29132004-8 2018 Negative perceptions of tap water were associated with lower odds of consuming tap water (ORPCAcomponent1=0.73, 95% CI 0.56-0.94; ORPCAcomponent2=0.67, 95% CI 0.49-0.93); women had higher odds of drinking purchased water compared to men (OR=1.90, 95% CI 1.11-3.26). Water 83-88 nuclear RNA export factor 1 Homo sapiens 24-27 29132004-8 2018 Negative perceptions of tap water were associated with lower odds of consuming tap water (ORPCAcomponent1=0.73, 95% CI 0.56-0.94; ORPCAcomponent2=0.67, 95% CI 0.49-0.93); women had higher odds of drinking purchased water compared to men (OR=1.90, 95% CI 1.11-3.26). Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 29154205-3 2018 The source of tap water for Minami-Soma City is groundwater, which is treated by rapid filtration before distribution in two of the three treatment plants. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 29154205-8 2018 In tap water and groundwater, radiocesium was decreased to below the detection limit in 2016 except for four stations. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 29369621-9 2018 Tap water samples from residential area were tested using this sensor which showed good agreement with standard colorimetric measurement methods. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 29126642-1 2018 Antibiotic-resistant bacteria (ARB) are a potential threat to human health through drinking water with strong evidence of ARB presence in post treated tap water around the world. Water 92-97 nuclear RNA export factor 1 Homo sapiens 151-154 29126642-1 2018 Antibiotic-resistant bacteria (ARB) are a potential threat to human health through drinking water with strong evidence of ARB presence in post treated tap water around the world. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 29126642-4 2018 A literature search was carried out to collate data on the effect of environmental conditions on AR E. coli, the effect of different water treatments on AR E. coli and typical human consumption levels of tap water. Water 208-213 nuclear RNA export factor 1 Homo sapiens 204-207 29126642-6 2018 Overall results show the mean adult human exposure to AR E. coli from tap water consumption ranged between 3.44x10-7 and 2.95x10-1cfu/day for the scenarios tested and varied depending on the water treatments used. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 29127799-0 2018 Persistence of antibiotic resistance genes and bacterial community changes in drinking water treatment system: From drinking water source to tap water. Water 87-92 nuclear RNA export factor 1 Homo sapiens 141-144 29127799-6 2018 The total abundance of the detected ARGs in tap water was much lower than that in source water. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 29127799-9 2018 Bacteria and ARGs were still present in tap water after treatment, though they were significantly reduced. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 29991858-7 2018 Results: Tooth Mousse showed statistically significant difference (p-value 0.001) compared with sodium fluoride, artificial saliva, and tap water when stored in both 12 and 24 hours" duration. Water 140-145 nuclear RNA export factor 1 Homo sapiens 136-139 29991858-8 2018 Conclusion: Tooth Mousse was a better storage media when compared with sodium fluoride, artificial saliva, and tap water. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 29064483-2 2018 Water scarcity and desalination treatment provide the general population of countries from these regions (e.g., Kuwait and Cyprus) with unique tap water characteristics. Water 0-5 nuclear RNA export factor 1 Homo sapiens 143-146 29064483-8 2018 Median tap water TTHM in Kuwait (6.7 (5.4, 11.6) mug/l) did not correlate with urinary or air THM and they were lower than those in Cyprus (29.5 (20.1, 48.0) mug/l; P<0.01). Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 29595154-4 2018 The FO membrane fouling layer mainly consisted of organic substances like polysaccharides and proteins, and was very loose and could be effectively removed by rinsing the membrane surface with tap water. Water 197-202 nuclear RNA export factor 1 Homo sapiens 193-196 29393879-7 2018 Satisfactory recoveries were obtained for tap water (86.6-105.9%) and river water samples (82.9-107.1%), with relative standard deviations <10% under optimal conditions. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 29463835-0 2018 Strontium isotope ratios of human hair record intra-city variations in tap water source. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 29104107-9 2018 Findings suggest that (1) tap water treated by RO is equally preferable to some bottled water, (2) personality traits may affect water preferences, and (3) prior findings of gender differences in preferences for bottled water may reflect personality characteristics. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 29191396-1 2018 INTRODUCTION: This study"s purpose is to determine whether nonconsumption of tap water is associated with lower prevalence of elevated blood lead levels and higher prevalence of dental caries in children and adolescents. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 29191396-7 2018 Children and adolescents who did not drink water were less likely than tap water drinkers to have an elevated blood lead level (adjusted prevalence ratios=0.62, 95% confidence limits=0.42, 0.90). Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 29146458-5 2018 Convenience was the only contextual predictor - the inconvenience of transporting bottled water has a negative effect on its consumption, and a positive effect on tap water consumption. Water 167-172 nuclear RNA export factor 1 Homo sapiens 163-166 29304558-0 2018 Reduction of FENO by tap water and carbonated water mouthwashes: magnitude and time course. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 29169099-2 2018 Studies on exposure to arsenic (As) in tap water and the risk of GDM have not provided conclusive evidence, particularly when levels of exposure were low (from 10 to 50microg As/L). Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 28956169-14 2018 Our double-blind study provided evidence for the beneficial health effects of another Hungarian thermal mineral water masking the colour, odour and pH of the tap water and mineral water. Water 112-117 nuclear RNA export factor 1 Homo sapiens 158-161 28956169-14 2018 Our double-blind study provided evidence for the beneficial health effects of another Hungarian thermal mineral water masking the colour, odour and pH of the tap water and mineral water. Water 162-167 nuclear RNA export factor 1 Homo sapiens 158-161 28956169-14 2018 Our double-blind study provided evidence for the beneficial health effects of another Hungarian thermal mineral water masking the colour, odour and pH of the tap water and mineral water. Water 162-167 nuclear RNA export factor 1 Homo sapiens 158-161 28806668-0 2018 Combination of electrochemical biosensor and textile threads: A microfluidic device for phenol determination in tap water. Water 116-121 nuclear RNA export factor 1 Homo sapiens 112-115 29526907-3 2018 The developed on-line PIEC ion stacking-ion chromatography method was validated by recovery experiments for the determination of nitrate in tap water in terms of both accuracy and precision, and the results showed the reliability of the method. Water 144-149 nuclear RNA export factor 1 Homo sapiens 140-143 29111994-13 2018 CONCLUSIONS: Tap water distilled locally in surgical facilities may be a source of infection after ocular surgery and its use should be avoided. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 28826030-0 2018 Synthesis and characterization of triazole based supramolecule for interaction with cefuroxime in tap water and blood plasma. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 28826030-8 2018 Supramolecule 5 displayed fairly good spectrophotometric recognition of Cefuroxime in human blood plasma and tap water thus showing that the ingredients of tap water and plasma sample was inert in the recognition of cefuroxime. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 28826030-8 2018 Supramolecule 5 displayed fairly good spectrophotometric recognition of Cefuroxime in human blood plasma and tap water thus showing that the ingredients of tap water and plasma sample was inert in the recognition of cefuroxime. Water 113-118 nuclear RNA export factor 1 Homo sapiens 156-159 28826030-8 2018 Supramolecule 5 displayed fairly good spectrophotometric recognition of Cefuroxime in human blood plasma and tap water thus showing that the ingredients of tap water and plasma sample was inert in the recognition of cefuroxime. Water 160-165 nuclear RNA export factor 1 Homo sapiens 156-159 29865052-8 2018 Lithium concentrations in tap water was significantly lower in rural counties compared to urban (63.3+-8.2 and 33.4+-4.7mug/L, respectively). Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 29136518-4 2018 Several independent lines of evidence obtained from microcosm experiments with the methanotrophic enrichment culture, tap water and bentazone at concentrations below 2 mg/L showed methanotrophic co-metabolic bentazone transformation: The culture removed 53% of the bentazone in 21 days in presence of 5 mg/L of methane, while only 31% was removed in absence of methane. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 29304558-8 2018 The tap water mouthwash reduced FENO statistically significantly only for 2 min compared with the baseline. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 29186890-4 2017 In conclusion, urinary As III, As V, MMA, and hair arsenic concentrations were significantly higher in residents who consumed arsenic contaminated ground water than control participants who consumed tap water. Water 203-208 nuclear RNA export factor 1 Homo sapiens 199-202 33525852-2 2017 Both factors are equally to blame: a leaking bathtub may have plenty of water if the tap is left open; if not, it will soon be empty. Water 72-77 nuclear RNA export factor 1 Homo sapiens 85-88 29071784-5 2017 Recovery studies were also performed to show the applicability of the developed methods, and percentage recovery values were found to be 90-105% in tap water and 94-97% in wastewater for both analytes. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 29126634-15 2018 Before introducing the AED into the NGT, 93% of the nurses reported mixing with tap water. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 29270018-1 2017 Numerous contemporary incidents demonstrate that conventional control strategies for municipal tap water have limited ability to mitigate exposures to chemicals whose sources are within distribution systems, such as lead, and chemicals that are not removed by standard treatment technologies, such as perfluorooctanoic acid (PFOA)/perfluorooctanesulfonic acid (PFOS). Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 29270018-3 2017 As an initial effort to fill this information gap, we conducted a critical review and analysis of the existing literature and data on the effectiveness of POU drinking water treatment technologies for reducing chemical contaminants commonly found in tap water in the United States. Water 168-173 nuclear RNA export factor 1 Homo sapiens 250-253 29270018-3 2017 As an initial effort to fill this information gap, we conducted a critical review and analysis of the existing literature and data on the effectiveness of POU drinking water treatment technologies for reducing chemical contaminants commonly found in tap water in the United States. Water 254-259 nuclear RNA export factor 1 Homo sapiens 250-253 29270018-4 2017 We found that many types of water treatment devices available to consumers in the United States have undergone laboratory testing and often certification for removal of chemical contaminants in tap water, but in most cases their efficacy in actual use has yet to be well characterized. Water 28-33 nuclear RNA export factor 1 Homo sapiens 194-197 29251455-9 2017 Rosehip tea caused the most color changes, while tap water showed the least in all resin composites. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 29085343-8 2017 Both of these effects as well as the final wash-in of fresh tap water followed calculated predictions well. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 28732945-1 2017 The present work focuses on possible heat transfer enhancement from a heating plate towards tap water in forced convection by means of 2MHz ultrasound. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 28942244-1 2017 A massive spill of 4-methylcyclohexanemethanol (MCHM), a semi-volatile organic compound, contaminated the Elk river and forced the recent closure of tap water for nearly 300,000 residents. Water 153-158 nuclear RNA export factor 1 Homo sapiens 149-152 26923686-0 2017 Perineal tap water burns in the elderly: at what cost? Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 28800414-9 2017 Well water and tap water contained relatively higher PFC concentrations than other types of drinking water. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 28800414-9 2017 Well water and tap water contained relatively higher PFC concentrations than other types of drinking water. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 28915436-0 2017 Radiation hazards and lifetime risk assessment of tap water using liquid scintillation counting and high-resolution gamma spectrometry. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 28915436-2 2017 liquid scintillation counting and high-resolution gamma spectrometry are utilized to analyze radionuclides concentrations in tap water of Irbid governorate, Jordan, and study their correlation. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 28915436-6 2017 In addition, the results of both techniques show that storing tap water in drilled wells leads to higher levels of radioactivity concentrations beyond the international permissible limits. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 28915436-7 2017 Furthermore, the average lifetime risk and annual effective dose received by age-grouped inhabitants due to direct and indirect tap water consumption are evaluated, where most of the received dose is attributed to 226Ra. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 28738625-0 2017 The screening of organic matter in mineral and tap water by UHPLC-HRMS. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 28738625-6 2017 This UHPLC-HRMS method was developed and tested with tap water and mineral water. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 28612149-8 2017 Most wounds healed by secondary intention and were managed using simple tap water-moistened plain gauze dressings changed three times a day. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 28622555-7 2017 The constructed sensor was applied to determine diuron in enriched samples of orange juice, mineral and tap water which statistical t-test showed accuracy of method. Water 108-113 nuclear RNA export factor 1 Homo sapiens 104-107 28714172-0 2017 A study of DNA damage in buccal cells of consumers of well- and/or tap-water using the comet assay: Assessment of occupational exposure to genotoxicants. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 28651147-7 2017 The unpleasant sensorial problems associated with desalinated drinking tap water may constitute the driving force for most people in GCC countries to depend on bottled water. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 28714172-5 2017 Taking into account the professions of well- and/or tap-water consumers, agricultural workers exposed directly (those who fumigated) or indirectly (those not involved in fumigating) to agrochemicals showed greater genetic damage than controls. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 28651147-7 2017 The unpleasant sensorial problems associated with desalinated drinking tap water may constitute the driving force for most people in GCC countries to depend on bottled water. Water 168-173 nuclear RNA export factor 1 Homo sapiens 71-74 28651147-8 2017 To encourage people in the GCC countries to consume desalinated tap water, it is essential that water testing include measurements of physicochemical properties, biofilm presence and organoleptic parameters to improve overall water quality. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 28651147-9 2017 This review highlights the contribution of organoleptics for consumers of desalinated tap water. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 28651147-11 2017 Accordingly, consumer awareness and outreach campaigns should be implemented to encourage people to drink tap water in the GCC countries. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 28955704-1 2017 QUESTION: Can a multifaceted statewide communications campaign motivate behavior change in low-income Colorado families to limit children"s fruit juice consumption and increase children"s consumption of tap water to prevent tooth decay? Water 207-212 nuclear RNA export factor 1 Homo sapiens 203-206 28963642-8 2017 The percent recovery of naphthalene obtained from tap water was ranged between 93.8 and 102.2. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 28955704-4 2017 The purpose of this campaign, "Cavities Get Around," was to motivate families to limit children"s fruit juice consumption and increase consumption of tap water to protect baby teeth from caries, while also building public will for children"s oral health. Water 154-159 nuclear RNA export factor 1 Homo sapiens 150-153 28774174-4 2017 No false-positive response is generated when the sensors are placed in simulated and actual tap water contaminated by heavy metals. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 28864188-5 2017 This sensing system allowed the accurate classification of nine metal ions in pure water at 0.5 muM and tap water at 3.0 muM. Water 108-113 nuclear RNA export factor 1 Homo sapiens 104-107 28774628-8 2017 After adjusting by these personal determinants, a dose-response relationship was found between concentrations of all chemicals except aluminium in tap water and bottled water use. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 28727528-0 2017 Racial/Ethnic and Socioeconomic Disparities in Hydration Status Among US Adults and the Role of Tap Water and Other Beverage Intake. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 28857060-8 2017 More than a decade of water safety planning using the WSP approach has shown that supplying safe drinking water at the tap throughout the WHO South-East Asia Region is a realistic goal. Water 106-111 nuclear RNA export factor 1 Homo sapiens 119-122 28555336-0 2017 A Novel Liquid-Liquid Extraction for the Determination of Sertraline in Tap Water and Waste Water at Trace Levels by GC-MS. A simple, green and fast analytical method was developed for the determination of sertraline in tap and waste water samples at trace levels by using supportive liquid-liquid extraction with gas chromatography-mass spectrometry. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 28555336-7 2017 The spiking experiments yielded satisfactory recoveries of 91.19 +- 2.48%, 90.48 +- 5.19% and 95.46 +- 6.56% for 100, 250 and 500 ng/mL sertraline for tap water, and 85.80 +- 2.15% and 92.43 +- 4.02% for 250 and 500 ng/mL sertraline for waste water. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 29244884-1 2017 An innovative biological energy has been observed related to the eye sight and fusing with another energy over tap water through a small metallic chain. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 28801682-4 2017 We pooled data from two controlled studies where blood pressure (BP) and heart rate (HR) were continuously recorded before and after the ingestion of 355 mL of tap water. Water 164-169 nuclear RNA export factor 1 Homo sapiens 160-163 28774628-2 2017 We aim to describe personal and tap water quality determinants of bottled water use in the city of Barcelona. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 28774628-10 2017 CONCLUSION: More than half of Barcelona residents regularly drank bottled water, and the main determinant was the chemical composition of tap water, particularly THM level. Water 142-147 nuclear RNA export factor 1 Homo sapiens 138-141 28709509-6 2017 Controlling for age, sex, years of education, and whether respondents were African American and Hispanic/Latino/a, lower perceived tap water quality was associated with lower sleep quality and shorter sleep length. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 28771145-1 2017 Hundreds of waterborne disease outbreaks (WBDO) of acute gastroenteritis (AGI) due to contaminated tap water are reported in developed countries each year. Water 12-17 nuclear RNA export factor 1 Homo sapiens 99-102 28771145-4 2017 Data for the number of AGI cases are available at the municipality level while exposure to tap water depends on drinking water networks (DWN). Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 28771145-6 2017 This study proposed to develop an algorithm which would match the most relevant grouping of municipalities with a specific DWN, in order that tap water exposure can be taken into account when investigating future disease outbreaks. Water 146-151 nuclear RNA export factor 1 Homo sapiens 142-145 28463769-0 2017 Stable hydrogen and oxygen isotopes of tap water reveal structure of the San Francisco Bay Area"s water system and adjustments during a major drought. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 28463769-9 2017 We observed delta2H and delta18O values of tap water consistent with waters originating from snowmelt from the Sierra Nevada Mountains, local precipitation, ground water, and partially evaporated reservoir sources. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 28463769-9 2017 We observed delta2H and delta18O values of tap water consistent with waters originating from snowmelt from the Sierra Nevada Mountains, local precipitation, ground water, and partially evaporated reservoir sources. Water 69-74 nuclear RNA export factor 1 Homo sapiens 43-46 28432888-5 2017 In addition, the microgels were also shown moderate adsorption capacity for Cr (VI) and As (V) from other water sources; tap water with 115.18 mg/g and 82.86 mg/g, sea water with 64.24 mg/g and 46.88 mg/g and creek water with 73.52 mg/g and 59.33 mg/g, respectively. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 28720105-14 2017 Moreover, it is necessary to comprehensively promote the flush toilets and tap water in rural areas. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 28432888-5 2017 In addition, the microgels were also shown moderate adsorption capacity for Cr (VI) and As (V) from other water sources; tap water with 115.18 mg/g and 82.86 mg/g, sea water with 64.24 mg/g and 46.88 mg/g and creek water with 73.52 mg/g and 59.33 mg/g, respectively. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 28432888-5 2017 In addition, the microgels were also shown moderate adsorption capacity for Cr (VI) and As (V) from other water sources; tap water with 115.18 mg/g and 82.86 mg/g, sea water with 64.24 mg/g and 46.88 mg/g and creek water with 73.52 mg/g and 59.33 mg/g, respectively. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 30505209-2 2017 Pilot scale experiments were performed in a distribution system simulator by injecting arsenic and measuring both adsorption onto iron pipe material and the oxidation of arsenite by hypochlorite in tap water to form arsenate. Water 202-207 nuclear RNA export factor 1 Homo sapiens 198-201 28488787-0 2017 Nitrotoga is selected over Nitrospira in newly assembled biofilm communities from a tap water source community at increased nitrite loading. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 28725129-2 2017 METHODS: Five different samples of tap water collected from each of the four emirates of UAE: Ajman, Sharjah, Abu Dhabi and Dubai; twenty-two brands of bottled water and fifteen brands of popular cold beverages, purchased from different supermarkets in U.A.E were tested using ion selective electrode method and the fluoride concentration was determined. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 28516821-0 2017 Pseudomonas aeruginosa Outbreak in a Neonatal Intensive Care Unit Attributed to Hospital Tap Water. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 28529020-3 2017 The patient may have been exposed to waterborne pathogens despite terminal water filtration due to a technical device to release residual tap water from the hose after showering. Water 37-42 nuclear RNA export factor 1 Homo sapiens 138-141 28529020-3 2017 The patient may have been exposed to waterborne pathogens despite terminal water filtration due to a technical device to release residual tap water from the hose after showering. Water 75-80 nuclear RNA export factor 1 Homo sapiens 138-141 28725129-3 2017 RESULTS: The mean fluoride content of tap water samples was 0.14 mg F/L with a range of 0.04-0.3 mg F/L; with Ajman tap water samples showing the highest mean fluoride content of 0.3 mg F/L. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 28725129-6 2017 CONCLUSIONS: The tap water, bottled water and beverages available in U.A.E show varying concentrations of fluoride, however none showed the optimal level necessary to prevent dental caries. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 28725129-3 2017 RESULTS: The mean fluoride content of tap water samples was 0.14 mg F/L with a range of 0.04-0.3 mg F/L; with Ajman tap water samples showing the highest mean fluoride content of 0.3 mg F/L. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 27829559-9 2017 Furthermore, the biosensor excels in the practical application in water samples (e.g., lake, tap and drinking water) owing to its non-interference and on-site rapid determination. Water 66-71 nuclear RNA export factor 1 Homo sapiens 93-96 27836598-6 2017 Moreover, the application for detecting tap water samples further demonstrates that this AuNP-based assay can be an excellent method used for sensing mercury at very low content in the environment. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 28713508-0 2017 Presence and seasonal variation of trihalomethanes (THMs) levels in drinking tap water in Mostaganem Province in northwest Algeria. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 28598349-4 2017 Respondents with lower levels of environmental concern, education levels, and lower organoleptic perceptions were most likely to perceive health risks from tap water consumption, and were most likely to use bottled water. Water 160-165 nuclear RNA export factor 1 Homo sapiens 156-159 28659529-5 2017 Tap water with conductivity 248 muS/cm was fed to UF-EDI system. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 28391120-10 2017 Time-course profiles of ACE and the identified by-products in tap water and wastewater samples were followed in order to simulate the actual disinfection process. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 28391120-11 2017 Tap water did not significantly affect degradation, but wastewater did; it reacted with the ACE to produce several brominated-DBPs. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 28284958-2 2017 This study reports a complete survey of the fluoridated tap water taken from 100 water consumption points in Tunisia. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 28426322-10 2017 A promotional campaign to increase water consumption among these Latino youth should include bicultural messages to underscore the power of water to quench true thirst, highlight the health benefits of drinking water, and address the safety of tap water. Water 35-40 nuclear RNA export factor 1 Homo sapiens 244-247 28713508-9 2017 CONCLUSION: Our drinking tap water samples include a large quantity of THMs with different concentrations, where the dibromochloromethane and the bromoform constitute the major portion of THMs. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 28713508-4 2017 AIM: The aim of this study was to determine the presence of THMs in the drinking tap water of Mostaganem Province (Algeria) in order to assess the seasonal variation in trihalomethane levels in tap water and to identify the season of high risk to the consumer. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 28372730-5 2017 The quantitation of STR in honey, milk and tap water confirm the reliability and applicability of the reported method. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 28525992-8 2017 Plain drinking water provided 258 g/d (241 g/d for children aged 4-8 years; 274 g/d for 9-13 years), mostly (83.8%) from tap. Water 15-20 nuclear RNA export factor 1 Homo sapiens 121-124 28525992-10 2017 Tap water consumption increased with income and was highest in the South of England. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 28276891-2 2017 The tap water was used as scrubbing liquid. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 28483828-10 2017 Home tap water consumed as a beverage and dietary supplement and nonprescription antacids contributed minimally to sodium intake (<0.5% each). Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 27707640-1 2017 Tap water may not be readily available in numerous places as a first aid for burns and, therefore, tea tree oil products are recommended alternatives. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 27707640-9 2017 The reduction of skin surface temperature by tap water was significantly greater than that by the other two methods. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 28288350-3 2017 Benalaxyl decreased with half-life of 16.1 days in soil under tap water irrigation with preferential residue of S-benalaxyl. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 28288350-6 2017 Benalaxyl acid was also formed with similar enantioselectivity as in tap water irrigation. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 28442005-7 2017 To maintain soil chemistry similar to the field, rain water or tap water should be used in column studies. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 28497034-2 2017 Because of concern regarding local tap water quality, fluoride-free bottled water consumption is common in this region, raising concern that families are not receiving adequate fluoride to promote dental health. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 28497034-7 2017 RESULTS: Fluoride detection levels were significantly greater (p = 0.02, Fisher"s exact test) in tap water (average = 0.49 mg/dL) than in bottled water, yet, the majority (22/30) were below the range for optimal dental health (0.7-1.2 mg/L). Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 28441356-1 2017 This research has developed a simple to use, cost effective sensor system for the detection of lead ions in tap water. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 28441356-4 2017 Tap water from the Cleveland, OH, USA regional water district was the test medium. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 28441356-6 2017 The calibration curve for the DPV measurements of lead ions in tap water showed excellent reproducibility with R2 value of 0.970. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 28468698-8 2017 The proposed method was successfully applied to the determination of irinotecan in tap water, river water, and urine samples spiked with 10.20 mg/L for the water samples and 8.32 mg/L for the urine sample. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 29903263-9 2017 The tap water showed weaker mutagenicities than the raw water in samples with S9( P = 0. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 28453240-10 2017 The father as the main child caregiver and lack of access to tap water are risk factors for viral failure and justify a special caution to improve adherence in these easy-to-identify situations before ART initiation. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 28129907-5 2017 The accumulation of EOX in the soil appears to play a significant role in subsequent bioaccumulation in cultures irrigated with tap water (long term memory effect). Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 28086155-6 2017 In addition, HANs added to tap water exhibited higher removals than those added to ultrapure water, probably because of the presence of free chlorine in tap water. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 28086891-4 2017 This study is concerned with the initial development of a method to measure an electrocardiogram (ECG) through tap water without conscious awareness of the presence of electrodes that are placed outside the bathtub wall. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 27335016-6 2017 Sum of mean concentrations of eight PFAAs detected in drinking tap water from Leipzig was 11.5 ng L-1, dominated by perfluorooctanoic acid (PFOA, 6.2 ng L-1). Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 28452768-8 2017 Also, the adsorption efficiencies of 70.7, 73.5 and 67.3% were observed for river water, tap water and wastewater effluent, respectively. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 27870982-6 2017 And both two probes had the possibility of potentially applied in practical applications such as detecting the hypochlorite concentration of tap water and river water. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 27915157-11 2017 The method was also applied for the analysis of analytes in the blood serum, Vitamine C tablets, and tap water with satisfactory results. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 28394506-0 2017 Lithium Levels in Tap Water and the Mental Health Problems of Adolescents: An Individual-Level Cross-Sectional Survey. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 28394506-1 2017 OBJECTIVE: We investigated the association between lithium level in tap water and mental health problems, including depressive symptoms, anxiety, and aggressive and suicidal behaviors, in a general population of adolescents using a large individual-level dataset. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 28394506-9 2017 The mean lithium concentration in tap water was 0.48 mug/L (SD = 0.52; range, 0.01 to 2.10; skewness = 2.01; kurtosis = 4.04), and it was relatively low compared with previous studies. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 28394506-10 2017 In multivariable regression analysis, lithium level in tap water had an inverse association with depressive symptoms (P = .02) and interpersonal violence (P = .02) but not with suicidal behaviors (suicidal ideation, P = .82; self-harm, P = .46). Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 28394506-11 2017 CONCLUSIONS: Lithium level in tap water was inversely associated with depressive symptoms and interpersonal violence among a general population of adolescents and may have antidepressive and antiaggressive effects. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 27981479-0 2017 Chemical quality of tap water in Madrid: multicase control cancer study in Spain (MCC-Spain). Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 27981479-4 2017 In the context of the MCC study, our aims were to describe contaminant concentrations in tap water drawn from various sampling points distributed around the region, assess these concentrations by reference to guideline values and study possible differences between the two supply areas. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 27981479-5 2017 Tap water samples were collected from 34 sampling points in 7 towns in the Madrid region (19-29 April 2010), and 23 contaminants (metals, nitrates, disinfection by-product and Mutagen X levels) were quantified. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 27912978-0 2017 Tap water iontophoresis in the treatment of pediatric hyperhidrosis. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 27912978-2 2017 Tap water iontophoresis (TWI) involves immersing the affected area in tap water and passing a small electrical current through the area. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 27912978-2 2017 Tap water iontophoresis (TWI) involves immersing the affected area in tap water and passing a small electrical current through the area. Water 4-9 nuclear RNA export factor 1 Homo sapiens 70-73 27912978-2 2017 Tap water iontophoresis (TWI) involves immersing the affected area in tap water and passing a small electrical current through the area. Water 74-79 nuclear RNA export factor 1 Homo sapiens 0-3 27912978-2 2017 Tap water iontophoresis (TWI) involves immersing the affected area in tap water and passing a small electrical current through the area. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 28453591-0 2017 [The impact of tap water fluoridation on human health]. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 28453591-2 2017 Additional aims are to evaluate whether the Chilean tap water fluoridation program has had any impact on dental health, and analyze the basis for the Chilean elementary school milk fluoridation program, which is targeted at children living in places where tap water has a fluoride concentration less than 0.3 mg/L, without any artificial fluoridation process. Water 260-265 nuclear RNA export factor 1 Homo sapiens 256-259 28158004-2 2017 The micro-LED has a peak emission wavelength of ~440 nm and an underwater power attenuation of 1 dB/m in tap water. Water 68-73 nuclear RNA export factor 1 Homo sapiens 105-108 28271352-5 2017 In this study, soil moisture was controlled by using tap water and NaOH as electrolytes to enhance electromigration and electroosmosis flow. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 28271352-7 2017 Therefore, tap water was the most cost-effective electrolyte to remove As from fine-grained soil. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 28416871-2 2017 Pure, tap and spring water were tested, and water quality was found to have a distinct effect on the main compounds extracted. Water 44-49 nuclear RNA export factor 1 Homo sapiens 6-9 28161940-12 2017 If the copper in water is too high, a simple device can be put on the tap to remove copper. Water 17-22 nuclear RNA export factor 1 Homo sapiens 70-73 28252670-2 2017 Tap water can reflect integrated features of regional hydrological processes and human activities. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 28252670-6 2017 (1) Results yielded the Tap Water Line in China is delta2H = 7.72 delta18O + 6.57 (r2 = 0.95). Water 28-33 nuclear RNA export factor 1 Homo sapiens 24-27 27618271-4 2017 We determined that these episodes were caused by inadequate clearance of chloramine from the tap water used for portable dialysis. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 27618271-6 2017 CONCLUSIONS: Clinicians should be aware of municipal tap water as a potential cause of methemoglobinemia and monitor for excessive levels of oxidants in dialysis water sources. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 28302987-0 2017 Development of a Certified Reference Material (NMIJ CRM 7203-a) for Elemental Analysis of Tap Water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 28302987-1 2017 A certified reference material (CRM), NMIJ CRM 7203-a, was developed for the elemental analysis of tap water. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 28348920-6 2017 The absorbance-concentration plot corresponding to tap water spiked samples was rectilinear, over the range of 7.56 x 10-6-3.22 x 10-5 mol L-1, with detection and quantitation limits of 2.49 x 10-6 mol L-1 and 7.56 x 10-6 mol L-1, respectively. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 28770221-6 2017 Collectively, carbohydrate-electrolyte beverage intake may attenuate an increase in HR at a given AEE while mountaineering at ~3000 m compared with tap water intake. Water 152-157 nuclear RNA export factor 1 Homo sapiens 148-151 27507462-5 2017 Furthermore, Hg(II) from tap water samples was analyzed, and the results were confirmed by ICP-MS. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 27507462-7 2017 The approach provides a simple, sensitive, and practical tool for the detection of trace Hg(II) in tap water, showing great promise for in-situ applications. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 28613122-4 2017 Concerns regarding the taste, smell, and colour of tap water were associated with lower odds of consuming tap water. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 28613122-4 2017 Concerns regarding the taste, smell, and colour of tap water were associated with lower odds of consuming tap water. Water 55-60 nuclear RNA export factor 1 Homo sapiens 106-109 28613122-4 2017 Concerns regarding the taste, smell, and colour of tap water were associated with lower odds of consuming tap water. Water 110-115 nuclear RNA export factor 1 Homo sapiens 51-54 28613122-4 2017 Concerns regarding the taste, smell, and colour of tap water were associated with lower odds of consuming tap water. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 29181221-5 2017 Sensing of bromides was also explored in tap water after addition of bromides suggesting that herein prepared catalysts could be used for bromides detection in real samples. Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 27876141-3 2017 The allowed concentration in tap water is 2 10-7 mol L-1. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 27876141-4 2017 SMX could unintentionally be ingested by healthy people when drinking contaminated tap water, representing unnecessary drug intake. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 27876141-5 2017 To assess the quality of tap water, fast, specific and sensitive detection methods are required, in which consequence measures for improving the purification of water might be initiated in the short term. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 27876141-5 2017 To assess the quality of tap water, fast, specific and sensitive detection methods are required, in which consequence measures for improving the purification of water might be initiated in the short term. Water 161-166 nuclear RNA export factor 1 Homo sapiens 25-28 28260731-8 2017 The restriction orders of food supplies such as contaminated vegetables and milk, and tap water intake were implemented within several days after the major release of radionuclides on March 15, 2011. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 27837803-0 2017 Predicting consumer preferences for mineral composition of bottled and tap water. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 27837803-1 2017 The overall liking for taste of water was correlated with the mineral composition of selected bottled and tap waters. Water 32-37 nuclear RNA export factor 1 Homo sapiens 106-109 28513413-1 2017 - The "Traumatic wounds and bite wounds" treatment guideline by the NHG (Dutch College of General Practitioners) has recommendations for treating traumatic wounds, bite wounds and wound infection.- It is important to distinguish between traumatic wounds and bite wounds because treatment of lacerations and cuts differs from treatment of bites.- Clean a wound under a lukewarm water tap; avoid using disinfectants.- Preferably close traumatic wounds within 12 hours, provided that the wounds have been carefully cleaned and that there are no referral indications. Water 377-382 nuclear RNA export factor 1 Homo sapiens 383-386 27664766-8 2017 Cost analysis shows that the capital cost could be returned back in 1 to 4years depending on the choice of produced water (bottled or tap) and available market. Water 116-121 nuclear RNA export factor 1 Homo sapiens 134-137 28095290-13 2016 The authors consider that drinking tap water is perhaps a more appropriate way for newborns, infants, elderly, and people with compromised immunity to satisfy thirst than using bottled water. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 28118131-8 2016 The proposed method was successfully applied to the determination of irinotecan in tap water, river water, and urine samples spiked with 10.20 mg/L for the water samples and 8.32 mg/L for the urine sample. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 27451182-7 2016 Samples consisting of bottled water, conditioned in various materials (glass, PET) and subjected to different storage conditions, had no hormone-like activities whereas estrogenic activity was found in the filtered tap water. Water 219-224 nuclear RNA export factor 1 Homo sapiens 215-218 27655616-0 2016 Occurrence of cardiovascular drugs in the sewage-impacted Vistula River and in tap water in the Warsaw region (Poland). Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 26810082-1 2016 Tap water from 497 properties using private water supplies, in an area of metalliferous and arsenic mineralisation (Cornwall, UK), was measured to assess the extent of compliance with chemical drinking water quality standards, and how this is influenced by householder water treatment decisions. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 27655616-4 2016 The aim of our study was to determine the presence of 30 pharmaceutically active compounds and some of their metabolites, at specific points of the Vistula River and in tap water samples in the Warsaw region. Water 173-178 nuclear RNA export factor 1 Homo sapiens 169-172 26810082-7 2016 Significant reductions in concentrations of aluminium, cadmium, copper, lead and/or nickel were found in tap waters where households were successfully treating low-pH groundwaters, and similar adventitious results were found for arsenic and nickel where treatment was installed for iron and/or manganese removal, and successful treatment specifically to decrease tap water arsenic concentrations was observed at two properties where it was installed. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 27655616-8 2016 In tap water samples, trace amounts of pharmaceuticals were detected, for almost all target compounds. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 27876971-10 2016 were found in 25 (73.53 %) out of 34 environmental water samples and 17 (28.8 %) out of 59 tap water. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 27959882-3 2016 In this study, arsenic levels in 13/20 of well water samples and 1/7 of tap water samples exceeded World Health Organization (WHO) health-based guideline value for drinking water. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 27959882-3 2016 In this study, arsenic levels in 13/20 of well water samples and 1/7 of tap water samples exceeded World Health Organization (WHO) health-based guideline value for drinking water. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 27005824-4 2016 Furthermore, the Bodipy-based sensor has obvious advantages including simplicity, rapid response, high selectivity, sensitivity and a detection limit of 1.2 mumol/L, and has been demonstrated in real water samples including tap water, mineral water and water from Lake Tai. Water 200-205 nuclear RNA export factor 1 Homo sapiens 224-227 27546066-0 2016 Epidemiological investigation of a tap water-mediated hepatitis E virus genotype 4 outbreak in Zhejiang Province, China. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 27834889-9 2016 Consequently, the water program aiming at providing 80% of rural people with access to tap water from a centralized piped system will not be possible. Water 18-23 nuclear RNA export factor 1 Homo sapiens 87-90 28070256-10 2016 Dissatisfaction from production of foam, unsuitable taste, unacceptable appearance and other problems in tap water was 11.1, 95.6, 27.8 and 0.4% respectively. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 28070256-2 2016 The aim of this study was to assess the consumer perception of tap water quality and other drinking water sources in Gonabad as a small semiarid city. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 28070256-8 2016 Office employees, women and poor families had the most satisfaction from tap water quality. Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 27782220-0 2016 Improvement of Terahertz Wave Radiation for InAs Nanowires by Simple Dipping into Tap Water. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 27512893-1 2016 This study examines arsenic, copper, lead and manganese drinking water contamination at the domestic consumer"s kitchen tap in homes of New South Wales, Australia. Water 65-70 nuclear RNA export factor 1 Homo sapiens 120-123 27512893-7 2016 Analysis of kitchen tap fittings demonstrates these are a primary source of drinking water lead contamination (n=9, mean - 63.4microg/L, median - 59.0microg/L). Water 85-90 nuclear RNA export factor 1 Homo sapiens 20-23 28032063-12 2016 Moreover, sensitivity analysis indicated that tap water consumption (Pspearman >0.92) and washing activities (Pspearman>0.95) had the greatest correlation on the cancer risk. Water 50-55 nuclear RNA export factor 1 Homo sapiens 46-49 27276181-12 2016 Having indoor tap water was protective (aOR: 0.65, 95% CI: 0.54-0.78), whereas a primary care giver who smoked was a risk factor (aOR: 5.15, 95% CI: 2.94-9.03). Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 27595487-6 2016 The matrix effect was minimal, and tap water used for calibrators and controls. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 27782220-1 2016 We report improvement of terahertz (THz) wave radiation for Si-based catalyst-free InAs nanowires (NWs) by simple dipping into tap water (DTW). Water 131-136 nuclear RNA export factor 1 Homo sapiens 127-130 27344251-6 2016 The occurrence of phenylacetonitrile as an N-DBP in tap water was investigated for the first time; the results revealed that mug/L concentrations were present in nine different distributed drinking waters in China and the United States. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 25974044-0 2016 Reply to why use tap water by Nagoba et al. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 26399223-0 2016 Cleansing of wounds by tap water? Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 25605447-7 2016 Inorganic As from food alone was associated with serum MMP-9 in subjects exposed to tap water As<=3 mug/l. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 27465126-4 2016 In one trial, tap water (4 ml/kg/15 min) was consumed (Plac trial). Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 25605447-0 2016 Relation of dietary inorganic arsenic to serum matrix metalloproteinase-9 (MMP-9) at different threshold concentrations of tap water arsenic. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 27307033-4 2016 Median and 95th percentiles of concentrations in tap water were in mug/L: Al: <10, 48.3, As: 0.2, 2.1; B: <100, 100; Ba: 30.7, 149.4; Ca: 85,000, 121,700; Cd: <0.5, <0.5; Ce: <0.5, <0.5; Co: <0.5, 0.8; Cr: <5, <5; Cu: 70, 720; K: 2210, 6740; Fe: <20, 46; Mn: <5, <5; Mo: <0.5, 1.5; Na: 14,500, 66,800; Ni: <2, 10.2; Mg: 6500, 21,200; Pb: <1, 5.4; Sb: <0.5, <0.5; Se: <1, 6.7; Sr: 256.9, 1004; Tl: <0.5, <0.5; U: <0.5, 2.4; V: <1, 1; Zn: 53, 208. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 27307033-6 2016 Since it is representative, this tap water contamination data can be used for integrated exposure assessment, in conjunction with diet and environmental (dust and soil) exposure data. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 25605447-8 2016 Exposure to iAs from food and water combined, in areas where tap water As concentration is <=10 mug/l, may contribute to As-induced changes in a biomarker associated with toxicity. Water 30-35 nuclear RNA export factor 1 Homo sapiens 61-64 25605447-8 2016 Exposure to iAs from food and water combined, in areas where tap water As concentration is <=10 mug/l, may contribute to As-induced changes in a biomarker associated with toxicity. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 26531802-6 2016 Estimated maximum exposures reached 9 mug/kg/day among exclusively formula-fed infants in households with high tap water arsenic (80 mug/l). Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 27419322-0 2016 Choosing Tap Water vs. Sterile Saline for Wound Irrigation. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 27343607-6 2016 Finally, the sensor was successfully used to analyse the tap water, showing high potential for practical applications. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 27485513-10 2016 RESULTS: Both natural and tap water sources were contaminated with FLA, Cryptosporidium spp. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 27444184-0 2016 Preliminary human health risk assessment of arsenic and fluoride in tap water from Zacatecas, Mexico. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 26990369-2 2016 Despite bacterial contamination in rinse bottles and reports of infections from contaminated irrigation water, tap water is still used by ~50% of irrigation users, raising a potential public health concern. Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 26990369-9 2016 There was a trend toward tap having more bacteria than distilled water. Water 65-70 nuclear RNA export factor 1 Homo sapiens 25-28 26059709-1 2016 Irrigating wounds with tap water does not increase colonisation, but controlled studies are required for further evidence. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 26059709-9 2016 It is concluded that skin wound irrigation with tap water leads to further reduction of Gram-positive bacteria compared with 0 9% sodium chloride sterile solution, with no difference in colonisation of haemolytic bacteria, Gram-negative bacteria and fungi. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 28058090-1 2016 While the problem of unsafe tap water in Flint, Michigan fueled outrage and better awareness in regard to the hazards of lead in tap water, the problem has existed in city after city for years in the US and in other countries. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 27417861-2 2016 Since 2014, Flint citizens-among the poorest in America, mostly African American-had complained that their tap water was foul and discolored. Water 111-116 nuclear RNA export factor 1 Homo sapiens 107-110 27117780-17 2016 Using tap water to store RGP lenses and topping off solution in the lens case were modifiable risk behaviors identified in RGP wearers who wore lenses for both orthokeratology and nonorthokeratology indications. Water 10-15 nuclear RNA export factor 1 Homo sapiens 6-9 27344558-6 2016 The typical oestrogen, 17beta-estradiol (17beta-E2), was detected above the method limit of quantification (m-LOQ) in 5 of 14 analysed tap water samples at concentrations from 0.09 to 0.15 ng L(-1). Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 27359350-6 2016 On October 16, 2015, the Flint water source was switched back to DWA, and residents were instructed to use filtered tap water for cooking and drinking. Water 120-125 nuclear RNA export factor 1 Homo sapiens 116-119 27359350-12 2016 Although unrelated to lead in the water, the water advisory likely reduced tap water consumption and increased consumption of bottled water. Water 45-50 nuclear RNA export factor 1 Homo sapiens 75-78 27359350-12 2016 Although unrelated to lead in the water, the water advisory likely reduced tap water consumption and increased consumption of bottled water. Water 45-50 nuclear RNA export factor 1 Homo sapiens 75-78 27359350-12 2016 Although unrelated to lead in the water, the water advisory likely reduced tap water consumption and increased consumption of bottled water. Water 45-50 nuclear RNA export factor 1 Homo sapiens 75-78 27344558-0 2016 Determination of steroidal oestrogens in tap water samples using solid-phase extraction on a molecularly imprinted polymer sorbent and quantification with gas chromatography-mass spectrometry (GC-MS). Water 45-50 nuclear RNA export factor 1 Homo sapiens 41-44 27353625-0 2016 Handwashing With a Water-Efficient Tap and Low-Cost Foaming Soap: The Povu Poa "Cool Foam" System in Kenya. Water 19-24 nuclear RNA export factor 1 Homo sapiens 35-38 27107142-0 2016 The occurrence of haloanisoles as an emerging odorant in municipal tap water of typical cities in China. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 27107142-1 2016 In this study, occurrence of the haloanisoles odorous compounds in tap water of Chinese cities, were investigated by solid-phase microextraction (SPME)-GC/MS analysis. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 27107142-8 2016 Based on the survey of occurrence of halophenol and residual chlorine, the possible source for the formation of haloanisoles in tap water was discussed. Water 132-137 nuclear RNA export factor 1 Homo sapiens 128-131 27164108-5 2016 The proposed method was finally used to determine HZ in tap water to simulate the analysis of real samples. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 27267213-3 2016 Recently, there have been increased uses of bottled drinking water in an assumption that the bottled water is safer than the tap water and its use will help to protect from water-related diseases. Water 61-66 nuclear RNA export factor 1 Homo sapiens 125-128 27267213-8 2016 RESULTS: One hundred percent of the tap water samples and 87.5 % of the bottled water samples were found to be contaminated with heterotrophic bacteria. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 27267213-9 2016 Of the tap water samples, 55.3 % were positive for total coliforms, compared with 25 % of the bottled water. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 27267213-10 2016 No bottled water samples were positive for fecal coliforms and fecal streptococci, in contrast to 21.1 % and 14.5 % of the tap water samples being contaminated with fecal coliforms and fecal streptococci, respectively. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 27267213-11 2016 One hundred percent of the tap water samples and 54.2 % of the bottled water samples had pH in the acceptable range. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 27098934-6 2016 Tandem Oasis (MAX+MCX) was finally applied to extract the spiked analytes from tap water, surface water, and several wastewater samples. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 26399884-8 2016 Micronuclei formation tests show that well water and tap water in these regions have no mutagenicity. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 27230915-10 2016 Concentration of arsenic in home tap water and estimated water consumption were strongly predictive of levels of arsenicals in urine as were smoking, body mass index, and gender. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 26868560-4 2016 The residual levels decreased following washing with stagnant, running, and stagnant+running tap water (i.e., decline in levels increased from 65.08% to 85.02%, 69.99 to 86.79, and 74.75 to 88.96, respectively). Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 26868560-7 2016 Additionally, washing with stagnant and running tap water or even stagnant water for 5 min might reduce the residue levels substantially, making the prepared food safe for human consumption. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 26255726-1 2016 Residents of Vietnam living in areas with water shortages collect and store tap water, when it is available, in containers, such as jars, which is then used for their daily activities. Water 42-47 nuclear RNA export factor 1 Homo sapiens 76-79 27642318-0 2016 Simultaneous Determination of 13 Priority Polycyclic Aromatic Hydrocarbons in Tehran"s Tap Water and Water for Injection Samples Using Dispersive Liquid-Liquid Micro Extraction Method and Gas Chromatography-Mass Spectrometry. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 27061315-10 2016 The low LOD, LOQ, and rapid detection confirm the potential of applying this sensor for accurate and high-throughput detection of melamine in tap water and milk. Water 146-151 nuclear RNA export factor 1 Homo sapiens 142-145 26775247-7 2016 The control group was soaked in tap water. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 26564554-3 2016 A number of randomized controlled trials have been completed to estimate the influence of tap water from municipal drinking water plants on the burden of AGI. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 26564554-4 2016 In Canada, 83% of the population (28 521 761 people) consumes tap water from municipal drinking water plants serving >1000 people. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 26564554-10 2016 It is estimated that 334 966 cases (90% probability interval 183 006-501 026) of AGI per year are associated with the consumption of tap water from municipal systems that serve >1000 people in Canada. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 27061315-0 2016 Rapid Detection of Melamine in Tap Water and Milk Using Conjugated "One-Step" Molecularly Imprinted Polymers-Surface Enhanced Raman Spectroscopic Sensor. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 27061315-4 2016 Principal component analysis segregated SERS spectral features of tap water and milk samples with different melamine concentrations. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 27061315-5 2016 Partial least squares regression models correlated melamine concentrations in tap water and skim milk with SERS spectral features. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 27061315-6 2016 The limit of detection (LOD) and limit of quantification (LOQ) of melamine in tap water were determined as 0.0019 and 0.0064 mmol/L, while the LOD and LOQ were 0.0165 and 0.055 mmol/L for the determination of melamine in skim milk. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 27061315-9 2016 The time required to determine melamine in tap water and milk were 6 and 25 min, respectively. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 27147356-6 2016 The image of the tap-water phantom showed almost the same distribution as that of the pure-water phantom. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 27094433-0 2016 A Novel Liquid-Liquid Extraction for the Determination of Nicotine in Tap Water, Wastewater, and Saliva at Trace Levels by GC-MS. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 27094433-8 2016 The spiking experiments yielded satisfactory recoveries of 97.6 +- 3.5, 96.8 +- 1.1, and 85.1 +- 1.3% for tap water, wastewater, and saliva samples, respectively. Water 110-115 nuclear RNA export factor 1 Homo sapiens 106-109 27158679-4 2016 The patient admitted to taking the contacts out in the evening and cleaning them with tap water before reapplying them in the morning. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 26803211-4 2016 Soil and house dust were sieved, digested, and analyzed via ICP-MS. Tap water and urine were analyzed without digestion, while toenails were washed, digested and analyzed. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 26803211-12 2016 Mixed models showed that soil and tap water best predicted urinary arsenic. Water 38-43 nuclear RNA export factor 1 Homo sapiens 34-37 26593550-6 2016 The process of boiling tap water (containing HAAs) for the preparation of powdered infant formula did not remove them; therefore it would be advisable to prepare this type of milk with mineral water (free of HAAs). Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 27642318-8 2016 The concentration of PAHs in all tap water as well as water for injection samples were lower than the limit of quantification of PAHs. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 26547431-8 2016 The functionality of quinolone-specific aptamers in real water samples was demonstrated in local tap water and in effluents of sewage plants. Water 57-62 nuclear RNA export factor 1 Homo sapiens 97-100 26799805-0 2016 Human exposure to thallium through tap water: A study from Valdicastello Carducci and Pietrasanta (northern Tuscany, Italy). Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 26799805-4 2016 In September 2014 Tl contamination was also found in the tap water distributed in the same area (from 2 to 10mug/L). Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 26799805-9 2016 Thallium values found in biological samples were correlated with Tl concentrations found in tap water in the living area of each citizen, and with his/her habits. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 27105415-6 2016 We can infer that nationwide more than 1,000 clusters involving 30,000 cases of cAGE each year may be linked to tap water. Water 116-121 nuclear RNA export factor 1 Homo sapiens 112-115 26547431-8 2016 The functionality of quinolone-specific aptamers in real water samples was demonstrated in local tap water and in effluents of sewage plants. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 26829156-0 2016 Widespread Occurrence of Benzotriazoles and Benzothiazoles in Tap Water: Influencing Factors and Contribution to Human Exposure. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 26862992-0 2016 Evaluating a Tap Water Contamination Incident Attributed to Oil Contamination by Nontargeted Screening Strategies. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 26862992-1 2016 The present study applied nontargeted screening techniques as a novel approach to evaluate the tap water samples collected during the "4.11" tap water pollution incident occurred on April 11, 2014 in Lanzhou in west China. Water 99-104 nuclear RNA export factor 1 Homo sapiens 95-98 26862992-1 2016 The present study applied nontargeted screening techniques as a novel approach to evaluate the tap water samples collected during the "4.11" tap water pollution incident occurred on April 11, 2014 in Lanzhou in west China. Water 99-104 nuclear RNA export factor 1 Homo sapiens 141-144 26862992-1 2016 The present study applied nontargeted screening techniques as a novel approach to evaluate the tap water samples collected during the "4.11" tap water pollution incident occurred on April 11, 2014 in Lanzhou in west China. Water 145-150 nuclear RNA export factor 1 Homo sapiens 95-98 26862992-1 2016 The present study applied nontargeted screening techniques as a novel approach to evaluate the tap water samples collected during the "4.11" tap water pollution incident occurred on April 11, 2014 in Lanzhou in west China. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 26862992-2 2016 Multivariate analysis (PCA and OPLS-DA) of about 3000 chemical features obtained in extracts of tap water samples by ultrahigh-pressure liquid chromatography quadrupole time-of-flight mass spectrometry (UPLC-QTOF-MS) analysis showed significantly different chemical profiles in tap water from pollution regions versus reference regions during the event. Water 100-105 nuclear RNA export factor 1 Homo sapiens 96-99 26862992-5 2016 A consistent finding was further observed in the targeted analysis of NA mixtures, demonstrating that the Lanzhou "4.11" tap water pollution incident could be attributed to oil spill pollution, and NA mixtures would be a marker for oil contamination. Water 125-130 nuclear RNA export factor 1 Homo sapiens 121-124 27054094-10 2016 Low limits of quantification for tap water (4 ng/L) and river water (20 ng/L) using only 800 muL of sample; recoveries > 97%. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 26080391-0 2016 Use of a Cumulative Exposure Index to Estimate the Impact of Tap Water Lead Concentration on Blood Lead Levels in 1- to 5-Year-Old Children (Montreal, Canada). Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 26869048-0 2016 Perchlorate levels found in tap water collected from several cities in Turkey. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 26869048-4 2016 The aim of this study was to determine the perchlorate levels in tap water from five cities in Turkey. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 26829156-2 2016 This study demonstrates widespread occurrence of these compounds in tap water from 51 major cities in China, which have ranges of <LOQ-310 ng/L for SigmaBTRs (median: 15.6 ng/L) and 40.1-1310 ng/L for SigmaBTHs (median: 406 ng/L). Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 26829156-4 2016 Difference of concentration level and compound profile of BTRs and BTHs in tap water and their surface water source, as well as in wastewater treatment plant effluents, is described. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 26860258-10 2016 Poultry-associated campylobacteriosis was linked to poultry consumption in wintertime, and ruminant-associated campylobacteriosis to tap-water provider type. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 26938163-1 2016 PURPOSE: The use of tap water as a wound-cleansing agent is becoming more common in clinical practice, especially in community settings. Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 26938163-11 2016 CONCLUSIONS: Study findings indicate that tap water is a safe alternative to sterile normal saline for wound cleansing in a community setting. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 26917751-0 2016 How do you like your tap water? Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 33579146-0 2016 High occurrence of potentially-pathogenic free-living amoebae in tap water and recreational water sources in South-West Iran. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 33579146-4 2016 Thirty percent of tap water samples in Ahvaz city were also positive for potentially pathogenic Free Living Amoebae. Water 22-27 nuclear RNA export factor 1 Homo sapiens 18-21 26803001-7 2016 The elaborated microsensor showed fast responses towards catechol additions to tap water - a weakly supported medium - characterized by a linear range from 0.2 to 10 muM, a sensitivity of 1.35 +- 0.4 A M(-1) cm(-2) and a dynamic range up to 43 muM. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 26870010-9 2016 We discussed, how knowledge gained from novel techniques will improve design and monitoring of water treatment and distribution systems in order to maintain good drinking water microbial quality up to consumer"s tap. Water 95-100 nuclear RNA export factor 1 Homo sapiens 212-215 26839261-4 2016 It appears fundamentally impossible to accurately predict from statistical properties of the surfaces alone how strongly we have to tighten a water tap to make it stop dripping and also how it starts dripping once we loosen it again. Water 142-147 nuclear RNA export factor 1 Homo sapiens 148-151 26870010-1 2016 Biological stability of drinking water refers to the concept of providing consumers with drinking water of same microbial quality at the tap as produced at the water treatment facility. Water 33-38 nuclear RNA export factor 1 Homo sapiens 137-140 26599150-6 2016 The range of DCIM concentrations in Nicosia tap water samples was narrower (0.032 - 0.848 mug L(-1)). Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 26599150-7 2016 Mean total iodine concentration in tap water samples from the seaside city of Limassol was 15 mug L(-1) and approximately twice to those observed in samples from the mainland Nicosia city. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 27924798-10 2016 CONCLUSIONS: A 3-week treatment with 1 l/day of the sulfate-rich mineral water improved the frequency of bowel movements in subjects with FC compared with tap water; however, the difference was no longer significant after 6 weeks. Water 73-78 nuclear RNA export factor 1 Homo sapiens 155-158 26196932-5 2016 The sensor RBP was preliminarily applied to the determination of Al(3+) in water samples from the lake of Henan University and tap water with satisfying results. Water 131-136 nuclear RNA export factor 1 Homo sapiens 127-130 26571428-0 2016 Drugs of abuse, cytostatic drugs and iodinated contrast media in tap water from the Madrid region (central Spain):A case study to analyse their occurrence and human health risk characterization. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 26571428-1 2016 This work analyses the presence of forty-eight emerging pollutants, including twenty-five drugs of abuse and metabolites, seventeen cytostatic drugs and six iodinated contrast media, in tap water from the Madrid Region. Water 190-195 nuclear RNA export factor 1 Homo sapiens 186-189 26571428-2 2016 Analysis of the target compounds in the tap water was performed by means of (on-line or off-line) solid-phase extraction followed by analysis by liquid chromatography-tandem mass spectrometry. Water 44-49 nuclear RNA export factor 1 Homo sapiens 40-43 28955842-3 2016 First, we confirmed that ceramics could transform tap water into active tap water by increasing water permeability through aquaporin. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 28955842-3 2016 First, we confirmed that ceramics could transform tap water into active tap water by increasing water permeability through aquaporin. Water 54-59 nuclear RNA export factor 1 Homo sapiens 72-75 28955842-3 2016 First, we confirmed that ceramics could transform tap water into active tap water by increasing water permeability through aquaporin. Water 76-81 nuclear RNA export factor 1 Homo sapiens 50-53 28955842-3 2016 First, we confirmed that ceramics could transform tap water into active tap water by increasing water permeability through aquaporin. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 28955842-3 2016 First, we confirmed that ceramics could transform tap water into active tap water by increasing water permeability through aquaporin. Water 76-81 nuclear RNA export factor 1 Homo sapiens 50-53 28955842-3 2016 First, we confirmed that ceramics could transform tap water into active tap water by increasing water permeability through aquaporin. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 28955842-5 2016 The distilled water was determined to exhibit the same aquaporin permeability as the original tap water. Water 98-103 nuclear RNA export factor 1 Homo sapiens 94-97 26454333-7 2016 LIMITATIONS: The limitations of the present study include the lack of data relevant to lithium levels in food and the proportion of the population who drank tap water and their consumption habits. Water 161-166 nuclear RNA export factor 1 Homo sapiens 157-160 26787982-3 2016 It was found that blanching in distilled water had no effect on discolouration when blanching conditions were at 75, 85, and 95 C for 7 min but the violet-red discolouration occurred only when tap water was used for blanching at 95 C for 7 min. Water 198-203 nuclear RNA export factor 1 Homo sapiens 194-197 27081247-2 2016 Tap water iontophoresis is reliable and effective method for treatment of palmar and plantar hyperhydrosis when practiced with appropriate technique and timing. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 28025598-12 2016 The main water sources of the town were tap water within the yard, which was estimated to be 44.7%, and tap water in the community was 40.0% followed by private protected well which was 14.5%. Water 9-14 nuclear RNA export factor 1 Homo sapiens 40-43 26787982-4 2016 Moreover, the addition of bicarbonate (NaHCO3) in distilled water to imitate higher alkalinity of tap water during blanching could contribute to the violet-red discolouration. Water 60-65 nuclear RNA export factor 1 Homo sapiens 98-101 26787982-4 2016 Moreover, the addition of bicarbonate (NaHCO3) in distilled water to imitate higher alkalinity of tap water during blanching could contribute to the violet-red discolouration. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 26787982-6 2016 After sterilization, there was no violet-red discolouration from Palmyra palm flesh without any peel left on even though it had a preceding treatment of blanching in highly alkaline tap water. Water 186-191 nuclear RNA export factor 1 Homo sapiens 182-185 27244873-4 2016 Since untreated depression is the most powerful risk factor for suicidal behaviour, we postulated that the consumption of arsenic-contaminated tap drinking-water may also be related to suicide. Water 156-161 nuclear RNA export factor 1 Homo sapiens 143-146 26360456-7 2016 The results showed that the highest PFASs concentrations were found in tap water samples and the more frequently found compound was perfluorooctanesulfonic acid (PFOS), with mean concentrations of 7.73, 15.33 and 15.83ng/l in French, Spanish and Brazilian samples, respectively. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 26360456-8 2016 In addition, PFOS was detected in all tap water samples from Brazil. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 26360456-9 2016 The highest level of PFASs contamination in a single sample was 140.48ng/l in a sample of Spanish tap water. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 26519201-6 2016 The obtained results showed that this analytical method would be useful for the analysis of fenitrothion, diazinon, and ethion in tap water with high precision and accuracy. Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 27925711-6 2016 The testing was conducted according to the method based on conditions of dynamic flow of tap water. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 27852967-10 2016 CONCLUSIONS: Results indicate that lithium intake from tap water in doses far below those used in the clinical practice may have suicide-preventive effects. Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 27852967-11 2016 This raises the possibility that lithium supplementation of tap water may open a new avenue in suicide prevention. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 27852967-12 2016 In Hungary, where there is a stable in time spatial inhomogeneity of the suicide rate it would be especially interesting to test whether regional differences in lithium content of tap water contribute to this phenomenon. Water 184-189 nuclear RNA export factor 1 Homo sapiens 180-183 27097462-7 2015 Based on the above method, the target compounds in reservoir water, reservoir soil and tap water in a certain region of Liaoning Province were analyzed. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 26553436-10 2015 However, their concentration was very low and the maximum values for IBP, NPX, DIC, and IDM were 47, 39, 24, and 37 ng/L, respectively, in tap water samples. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 26363608-5 2015 Triethyl phosphate (TEP) was the most abundant OPE in the tap water and filtered drinking water with median concentrations of 50.2 and 30.2ng/L, respectively. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 26653310-10 2015 The number of residents, presence of pets, and local tap water also influenced the diversity and size of indoor air microbes. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 26653310-12 2015 Vacuum cleaning increased the signature of pet- and floor-derived bacteria in indoor air, while the frequency of natural ventilation decreased the relative abundance of tap water-derived microorganisms in air. Water 173-178 nuclear RNA export factor 1 Homo sapiens 169-172 26599790-10 2015 It was also significantly lower among peoples who used tap water as source of drinking water than from Wells/river (OR 9.67, P = 0.03). Water 59-64 nuclear RNA export factor 1 Homo sapiens 55-58 26599790-10 2015 It was also significantly lower among peoples who used tap water as source of drinking water than from Wells/river (OR 9.67, P = 0.03). Water 87-92 nuclear RNA export factor 1 Homo sapiens 55-58 26067701-6 2015 Among the studied compounds, pentachlorophenol was detected in tap water at a concentration level of 0.06 microg L(-1). Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 26520739-6 2015 Furthermore, the image of the pure-water phantom showed almost the same distribution as the tap-water phantom, indicating that the luminescence image was not related to impurities in the water. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 26094108-4 2015 With this conservative scenario, it can be seen that tap water makes a minor but potentially non-negligible contribution for a few micropollutants, by comparison with diet and air. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 25817821-7 2015 Probable cases were more likely than probable controls to drink tap water (adjusted odds ratio: 3.4; 95% CI: 1.2-9.2). Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 25817821-10 2015 Two tap water samples had detectable thermotolerant coliforms. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 26520739-6 2015 Furthermore, the image of the pure-water phantom showed almost the same distribution as the tap-water phantom, indicating that the luminescence image was not related to impurities in the water. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 26520739-9 2015 The luminescence images of the tap-water phantom during proton irradiation could be obtained in less than 2 s. CONCLUSIONS: Luminescence imaging during proton-beam irradiation is promising as an effective method for range estimation in proton therapy. Water 35-40 nuclear RNA export factor 1 Homo sapiens 31-34 26186865-10 2015 More than 200 measurements were recorded to define the map at each horizontal plane positioned at a different distance from the US transducer; tap water was heated at the same temperature used for dyeing tests (60 C). Water 147-152 nuclear RNA export factor 1 Homo sapiens 143-146 26411480-10 2015 Tap water, well water and wastewater samples were also analyzed to evaluate the method capability for real sample analysis. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 26506001-12 2015 Even though access to piped water supplies is low in Uvira, improving the reliability of tap water supply may substantially reduce the incidence of suspected cholera, in particular in neighbourhoods having a higher access to tap water. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 26506001-12 2015 Even though access to piped water supplies is low in Uvira, improving the reliability of tap water supply may substantially reduce the incidence of suspected cholera, in particular in neighbourhoods having a higher access to tap water. Water 93-98 nuclear RNA export factor 1 Homo sapiens 225-228 26506001-7 2015 Suspected cholera cases attributable to a suboptimal tap water supply reached 23.2% of total admissions (95% CI 11.4%-33.2%). Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 26437931-9 2015 RESULT: Only 18.1% (43/237) of the study population had access to tap water in the study area. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 26506001-8 2015 Although generally reporting less admissions to the CTC, neighbourhoods with a higher consumption of tap water were more affected by water supply interruptions, with a rate ratio of 3.71 (95% CI: 1.91-7.20) and an attributable fraction of cases of 31.4% (95% CI: 17.3%-42.5%). Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 26442138-1 2015 The tensile strength of ordinary water such as tap water or seawater is typically well below 1 bar. Water 33-38 nuclear RNA export factor 1 Homo sapiens 47-50 26516885-0 2015 Indoor Heating Drives Water Bacterial Growth and Community Metabolic Profile Changes in Building Tap Pipes during the Winter Season. Water 22-27 nuclear RNA export factor 1 Homo sapiens 97-100 26334055-3 2015 One of the most common antibacterial agents, oxytetracycline (OTC), was detected at concentrations as low as 1 nM in both buffer solution and tap water, which was 25-fold more sensitive, compared to the previous absorbance-based colorimetric aptasensors. Water 146-151 nuclear RNA export factor 1 Homo sapiens 142-145 26437931-13 2015 Accordingly, FC were detected in 80% of the total samples with counts ranging between 0.67 and 266.67 CFU/100 ml although 66.67% of tap water samples were negative for FC. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 26322121-8 2015 CONCLUSIONS: Due to acceptable recoveries (93.3-102.0 %) and RSD values (6-7.1) from spiked tap water, the developed method can be successfully applied for the determination of trace amounts of terbium ions in the presence of major components of water. Water 96-101 nuclear RNA export factor 1 Homo sapiens 92-95 26605175-3 2015 Artificial tap water was thickened to honey-like consistency (effective viscosity of 1,300+-100 mPa s at a shear rate of 50 per second at 20C) with a starch-based thickener (SB) or a gum-containing thickener (GC). Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 26985408-7 2015 Water was taken from two sources, tap water, and from the water filter. Water 0-5 nuclear RNA export factor 1 Homo sapiens 34-37 26985408-10 2015 RESULTS: The number of water samples found to be within desirable limits with respect to physicochemical parameters were significantly more with the filter water sample than the tap water samples. Water 23-28 nuclear RNA export factor 1 Homo sapiens 178-181 26985408-11 2015 Suspicious/unsatisfactory microbiological quality of water was observed in 28% and 4% of tap and filter water samples, respectively. Water 53-58 nuclear RNA export factor 1 Homo sapiens 89-92 26371025-1 2015 Municipal tap water is increasingly treated at the point of use (POU) to improve the acceptability and palatability of its taste. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 26573047-0 2015 Effective Dose Radon 222 of the Tap Water in Children and Adults People; Minab City, Iran. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 26573047-4 2015 Concentration of (222)Rn in tap water of Minab city in two temperatures 5 and 15 oC was measured by radon meter model RTM1668-2. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 26290299-4 2015 According to the 2008 European Food Safety Authority"s Concise Food Consumption Database, tap water consumption was highest in the northern European countries and in Austria. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 26290299-5 2015 While Germany had a particularly low intake of tap water, it led in consumption of fruit and vegetable juices, soft drinks, and especially bottled water. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 26308926-0 2015 Different senescent HDPE pipe-risk: brief field investigation from source water to tap water in China (Changsha City). Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 25592266-8 2015 Of participants aged <20 years, seropositivity was significantly associated with having a well as the source of home tap water (aOR 1 7, 95% CI 1 1-2 6) and living in a more crowded home (aOR 2 3, 95% CI 1 5-3 7). Water 124-129 nuclear RNA export factor 1 Homo sapiens 120-123 26320969-3 2015 The probe was used to detect bisulfite in tap water, sugar and dry white wine. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 26753282-1 2015 A hydrophilic interaction chromatographic (HILIC) method has been developed for the determination of the four carbapenems in human urine and tap water. Water 145-150 nuclear RNA export factor 1 Homo sapiens 141-144 25973582-7 2015 Rapid formation was observed between 10 C and 30 C, as well as between pH 3 and pH 11, in both ultrapure and tap water, even at trace quantities of reactants (ng/L-range for metformin, mg/L-range for free chlorine). Water 115-120 nuclear RNA export factor 1 Homo sapiens 111-114 25841997-9 2015 CONCLUSION: Education, home safety checks along with thermometers or thermostatic mixing valves should be promoted to reduce tap water scalds. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 23802652-0 2015 Cleansing of wounds by tap water? Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 26114840-7 2015 The practical utility of the method is well tested with tap water. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 25874436-1 2015 Activity concentration of (238)U, (234)U, (226)Ra, (228)Ra, (210)Pb and (210)Po in tap water from selected springs and private wells in the area of the former uranium mine at Zirovski Vrh were determined. Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 25973582-8 2015 While Y is degraded within a few hours to days in the presence of light, elevated temperature, organic solvents and matrix constituents within tap water, a secondary degradation product was discovered, which is stable and colorless (C; C4H6ClN3). Water 147-152 nuclear RNA export factor 1 Homo sapiens 143-146 26092033-22 2015 The decision to implement a water fluoridation programme relies upon an understanding of the population"s oral health behaviour (e.g. use of fluoride toothpaste), the availability and uptake of other caries prevention strategies, their diet and consumption of tap water and the movement/migration of the population. Water 28-33 nuclear RNA export factor 1 Homo sapiens 260-263 26030158-0 2015 Real-time detection of hypochlorite in tap water and biological samples by a colorimetric, ratiometric and near-infrared fluorescent turn-on probe. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 26030158-2 2015 In addition, experiments showed that this probe can be applied to detect hypochlorite in tap water, serum samples, and living cells with low cytotoxicity. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 25528218-6 2015 For typical dietary constituents, only tap water is probably locally derived and bottled water may not be. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 25139477-3 2015 Environmental recirculation can then occur when PFAAs from the environment enter the wastewater stream in, e.g., tap water. Water 90-95 nuclear RNA export factor 1 Homo sapiens 113-116 25139477-7 2015 With regard to environmental recirculation, tap water was an important source of PFAAs to the Bromma WWTP influent, contributing >40% for each quantified sulfonic acid and up to 30% for the carboxylic acids. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 25139477-9 2015 Our results show that in order to estimate current primary emissions from the technosphere, it may be necessary to correct the PFAA emission rates in WWTP effluents for PFAAs present in tap water, especially in the case of elevated levels in tap water. Water 190-195 nuclear RNA export factor 1 Homo sapiens 186-189 26014494-10 2015 To confirm the magnitude and temperature dependence, the experiment was repeated by two of the observers with a mixture of ice and water at 0 C and with thermalized tap water at 21 C room temperature. Water 170-175 nuclear RNA export factor 1 Homo sapiens 166-169 26028872-11 2015 CONCLUSION: Chlorhexidine, warm salt water and warm tap water averagely produced the same number of colony forming units of bacteria, which shows that the three different mouth washes are equally effective as post-operative mouth rinses after oral surgery. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 25430011-5 2015 Furthermore, in tap water from Osijek, levels of arsenic exceeded the WHO guidelines and EPA regulations. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 25728657-11 2015 The developed method was applied to water samples (tap and swimming pool water). Water 36-41 nuclear RNA export factor 1 Homo sapiens 51-54 25687671-2 2015 At the site, tap water and treated wastewater were intermittently infiltrated into a porous aquifer via a small pilot pond. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 25595746-0 2015 The first association of a primary amebic meningoencephalitis death with culturable Naegleria fowleri in tap water from a US treated public drinking water system. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 25595746-6 2015 His only reported water exposure was tap water; in particular, tap water that was used to supply water to a lawn water slide on which the child had played extensively prior to becoming ill. Water samples were collected from both the home and the water distribution system that supplied the home and tested; N. fowleri was identified in water samples from both the home and the water distribution system. Water 18-23 nuclear RNA export factor 1 Homo sapiens 37-40 25595746-6 2015 His only reported water exposure was tap water; in particular, tap water that was used to supply water to a lawn water slide on which the child had played extensively prior to becoming ill. Water samples were collected from both the home and the water distribution system that supplied the home and tested; N. fowleri was identified in water samples from both the home and the water distribution system. Water 18-23 nuclear RNA export factor 1 Homo sapiens 63-66 25595746-6 2015 His only reported water exposure was tap water; in particular, tap water that was used to supply water to a lawn water slide on which the child had played extensively prior to becoming ill. Water samples were collected from both the home and the water distribution system that supplied the home and tested; N. fowleri was identified in water samples from both the home and the water distribution system. Water 190-195 nuclear RNA export factor 1 Homo sapiens 63-66 25595746-6 2015 His only reported water exposure was tap water; in particular, tap water that was used to supply water to a lawn water slide on which the child had played extensively prior to becoming ill. Water samples were collected from both the home and the water distribution system that supplied the home and tested; N. fowleri was identified in water samples from both the home and the water distribution system. Water 41-46 nuclear RNA export factor 1 Homo sapiens 63-66 25595746-6 2015 His only reported water exposure was tap water; in particular, tap water that was used to supply water to a lawn water slide on which the child had played extensively prior to becoming ill. Water samples were collected from both the home and the water distribution system that supplied the home and tested; N. fowleri was identified in water samples from both the home and the water distribution system. Water 41-46 nuclear RNA export factor 1 Homo sapiens 63-66 25595746-6 2015 His only reported water exposure was tap water; in particular, tap water that was used to supply water to a lawn water slide on which the child had played extensively prior to becoming ill. Water samples were collected from both the home and the water distribution system that supplied the home and tested; N. fowleri was identified in water samples from both the home and the water distribution system. Water 41-46 nuclear RNA export factor 1 Homo sapiens 63-66 22199153-5 2015 The quality of the local environment, measured by access to tap water, was a significant factor for rural residents. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 25795972-0 2015 [Tap water as a dietary source of exposure to fluoride in Tenerife; risk assessment]. Water 5-10 nuclear RNA export factor 1 Homo sapiens 1-4 25795972-7 2015 METHOD: 44 samples of tap water collected in the 11 municipalities in the study were analyzed using the fluoride potentiometric determination with an ion selective electrode. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 25795972-8 2015 RESULTS: 9 of the 11 municipalities presented mean fluoride concentrations in their tap water that exceeded the parametric value set by the Spanish legislation (1.5 mg/L). Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 25486924-0 2015 Analysis of gadolinium-based contrast agents in tap water with a new hydrophilic interaction chromatography (ZIC-cHILIC) hyphenated with inductively coupled plasma mass spectrometry. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 25486924-5 2015 With the speciation method described, tap water samples from the area of Berlin were analysed and for the first time, three Gd species, Gd-BT-DO3A, Gd-DOTA and Gd-BOPTA, were found in tap water samples at concentrations of about 10-20 ng Gd per litre. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 25266775-3 2015 The results showed that 75% of the university community drinks only bottled water and that the consumption of tap water is low. Water 114-119 nuclear RNA export factor 1 Homo sapiens 110-113 25490042-5 2015 Application in 5 kinds of natural water source and accurate detection of cyanide in tap water solvent system also indicated the high practical significance of the probe. Water 34-39 nuclear RNA export factor 1 Homo sapiens 84-87 25490042-5 2015 Application in 5 kinds of natural water source and accurate detection of cyanide in tap water solvent system also indicated the high practical significance of the probe. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 25266775-5 2015 In general, the participants in this study do not trust the quality of the tap water, which could be caused by the facilities that distribute bottled water encouraging a general disinterest in learning about the origin and management of the tap water that is distributed on campus. Water 150-155 nuclear RNA export factor 1 Homo sapiens 241-244 25266775-5 2015 In general, the participants in this study do not trust the quality of the tap water, which could be caused by the facilities that distribute bottled water encouraging a general disinterest in learning about the origin and management of the tap water that is distributed on campus. Water 150-155 nuclear RNA export factor 1 Homo sapiens 241-244 25062494-7 2015 Drinking tap water was significantly associated with an increased risk for gastroenteritis (relative risk 3 67, 95% confidence interval 2 86-4 70) as was place of residence. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 24738825-10 2015 CONCLUSION: Total daily fluoride (F) intake increased as F concentration in tap water increased. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 25062494-10 2015 Tap water samples tested positive for faecal indicator bacteria and protozoa. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 25814730-0 2015 Aquagenic keratoderma treated with tap water iontophoresis. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 25814730-4 2015 We report a case of AK unresponsive to topical 20% of aluminum chloride successfully treated with tap water iontophoresis. Water 102-107 nuclear RNA export factor 1 Homo sapiens 98-101 25236939-6 2015 RESULTS: Statistical analysis demonstrated that tap water, saline, and saliva decreased cell viability as the storage temperature increased. Water 52-57 nuclear RNA export factor 1 Homo sapiens 48-51 25555117-4 2015 Tap water was infused via a metal trocar for approximately 60 minutes. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 25879490-4 2015 In a case-control study among kindergarten children, we compared cases and controls regarding environmental exposure, use of swimming pools, zoo visits and tap water consumption 14 days pre-onset or a corresponding 14-days-period (controls) and adjusted for residence. Water 160-165 nuclear RNA export factor 1 Homo sapiens 156-159 25546315-7 2015 The method was also evaluated for the analysis of tap water and cooling water samples treated with the biocide. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 25531406-2 2015 This study investigated temporal variations in the levels of regulated and non-regulated disinfection byproducts (DBPs) in cold and hot tap water in a home on a medium-sized municipal water system. Water 140-145 nuclear RNA export factor 1 Homo sapiens 136-139 25531406-13 2015 The ratio of unknown total organic halide (UTOX) to TOX was substantially lower in the hot tap water as the THM to TOX ratio became correspondingly larger. Water 95-100 nuclear RNA export factor 1 Homo sapiens 91-94 25253043-9 2015 Moreover, Pearson"s correlation analysis indicated that Actinobacteria was positively correlated with the levels of total alkalinity and dissolved organic carbon in tap water, while Firmicutes had a significant positive correlation with nitrite nitrogen. Water 169-174 nuclear RNA export factor 1 Homo sapiens 165-168 25513829-0 2015 Residential tap water contamination following the Freedom Industries chemical spill: perceptions, water quality, and health impacts. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 24967824-4 2015 The patients were instructed to dilute 1 ampulla of TXA in 300 ml of tap water (concentration 0.2%) from postoperative day 5-10 and to gargle or spray the tonsillar fossae 5-6 times daily. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 25428514-8 2015 Therefore, the iodide content of tap water, urine and blood serum is monitored using this sensor and it is found that the sensor can detect a range of iodide in tap water, urine and blood serum. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 25428514-8 2015 Therefore, the iodide content of tap water, urine and blood serum is monitored using this sensor and it is found that the sensor can detect a range of iodide in tap water, urine and blood serum. Water 37-42 nuclear RNA export factor 1 Homo sapiens 161-164 25428514-8 2015 Therefore, the iodide content of tap water, urine and blood serum is monitored using this sensor and it is found that the sensor can detect a range of iodide in tap water, urine and blood serum. Water 165-170 nuclear RNA export factor 1 Homo sapiens 33-36 25428514-8 2015 Therefore, the iodide content of tap water, urine and blood serum is monitored using this sensor and it is found that the sensor can detect a range of iodide in tap water, urine and blood serum. Water 165-170 nuclear RNA export factor 1 Homo sapiens 161-164 25196960-5 2015 Of the 14 pharmaceutical compounds selected, nine were identified in tap water of Beijing downtown with the concentration up to 38.24 ng/L (carbamazepine), and the concentration levels of detected pharmaceuticals in tap water (<5 ng/L for most pharmaceuticals) were lower than previous studies in other countries. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 25196960-5 2015 Of the 14 pharmaceutical compounds selected, nine were identified in tap water of Beijing downtown with the concentration up to 38.24 ng/L (carbamazepine), and the concentration levels of detected pharmaceuticals in tap water (<5 ng/L for most pharmaceuticals) were lower than previous studies in other countries. Water 220-225 nuclear RNA export factor 1 Homo sapiens 216-219 25574772-9 2015 Source water bacteriology was found to have the greatest effect on tank water and biofilm bacteriology, an effect confirmed by a controlled study comparing ultrasonic and boiler humidifiers fed with tap vs. treated (deionized, reverse osmosis, 0.2 mum filtered) water over a period of two months. Water 7-12 nuclear RNA export factor 1 Homo sapiens 199-202 25513829-6 2015 Flushing reduced tap water 4-methylcyclohexanemethanol (4-MCHM) concentrations within some but not all homes. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 25085618-3 2015 Results indicate that although violations of the current chromium regulation limit in tap water are very rare, 25% of cases showed Cr(VI) concentrations above 10 mug/L, whereas Cr(VI) was detectable in 70% of the samples (>2 mug/L). Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 25454232-12 2015 Lead concentrations in tap water above 5mug/L were also positively correlated with the GM, 75th and 90th quantiles of BLLs in children drinking tap water. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 25921118-1 2015 OBJECTIVE: This study aimed to evaluate the prevalence of skin lesions, which is a health effect of chronic arsenic (As) exposure, and determine the hair/blood arsenic concentrations of people living in Kutahya villages who are using and drinking tap water with a high concentration of arsenic. Water 251-256 nuclear RNA export factor 1 Homo sapiens 247-250 25898079-6 2015 The removal rate of Na(+) in ADE was above 95% and the citric acid production was even higher than that with tap water. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 25180822-0 2015 Pentafluorobenzyl esterification of haloacetic acids in tap water for simple and sensitive analysis by gas chromatography/mass spectrometry with negative chemical ionization. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 25180822-9 2015 The method was applied to 30 tap water samples from 15 cities in the Kansai region of Japan. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 25180822-11 2015 Dichloroacetic acid, trichloroacetic acid, and bromochloroacetic acid were the major HAAs detected in most of the tap water, and accounted for 29%, 20% and 19% of the total HAAs, respectively. Water 118-123 nuclear RNA export factor 1 Homo sapiens 114-117 25514858-3 2015 Remarkable temporal and spatial variations were observed among most of the trace elements in the tap water collected from two tap water treatment plants. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 25454232-12 2015 Lead concentrations in tap water above 5mug/L were also positively correlated with the GM, 75th and 90th quantiles of BLLs in children drinking tap water. Water 27-32 nuclear RNA export factor 1 Homo sapiens 144-147 25454232-12 2015 Lead concentrations in tap water above 5mug/L were also positively correlated with the GM, 75th and 90th quantiles of BLLs in children drinking tap water. Water 148-153 nuclear RNA export factor 1 Homo sapiens 23-26 25454232-12 2015 Lead concentrations in tap water above 5mug/L were also positively correlated with the GM, 75th and 90th quantiles of BLLs in children drinking tap water. Water 148-153 nuclear RNA export factor 1 Homo sapiens 144-147 26856179-3 2015 The population health risk assessment was performed according to public health regulatory methods P 2.1.10.1920-04 in relation to the ionic composition of tap water consumed by children"s population of the city of Kazan. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 26856179-4 2015 The use of a risk assessment in consumption of tap water by the most susceptible population group with localized residence allows to identify zones in the boundaries of the urban area in which water is needed post-treatment of tap waters flowing to consumers. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 26856179-4 2015 The use of a risk assessment in consumption of tap water by the most susceptible population group with localized residence allows to identify zones in the boundaries of the urban area in which water is needed post-treatment of tap waters flowing to consumers. Water 51-56 nuclear RNA export factor 1 Homo sapiens 227-230 26856179-4 2015 The use of a risk assessment in consumption of tap water by the most susceptible population group with localized residence allows to identify zones in the boundaries of the urban area in which water is needed post-treatment of tap waters flowing to consumers. Water 193-198 nuclear RNA export factor 1 Homo sapiens 47-50 26856179-4 2015 The use of a risk assessment in consumption of tap water by the most susceptible population group with localized residence allows to identify zones in the boundaries of the urban area in which water is needed post-treatment of tap waters flowing to consumers. Water 193-198 nuclear RNA export factor 1 Homo sapiens 227-230 25985122-0 2015 An on-line spectrophotometric determination of trace amounts of thiourea in tap water, orange juice, and orange peel samples using multi-channel flow injection analysis. Water 80-85 nuclear RNA export factor 1 Homo sapiens 76-79 25542943-6 2015 RESULTS: All 10 sonographically guided PSTJ tap water injections were accurate, distending both the posterior and lateral PSTJ recesses. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 25714644-5 2015 The proposed CE method was successfully applied for the analysis of samples of tap water and cooling water spiked with DBNPA. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 26074054-0 2015 [Hygienic maintenance of water mist-generating equipment that couples directly to the tap]. Water 25-30 nuclear RNA export factor 1 Homo sapiens 86-89 26074054-1 2015 OBJECTIVES: Water mist is usually generated using equipment directly connected to the water tap, as its installation is relatively easy. Water 12-17 nuclear RNA export factor 1 Homo sapiens 92-95 26074054-1 2015 OBJECTIVES: Water mist is usually generated using equipment directly connected to the water tap, as its installation is relatively easy. Water 86-91 nuclear RNA export factor 1 Homo sapiens 92-95 25958631-9 2015 When compared with drinking tap water, OR for drinking well water was 1.770 (95% CI 1.001 - 2.444), 2.442 for drinking river water (95% CI 0.956 - 3.950), 2.554 for drinking house and field ditch water (95% CI 1.961 - 6.584), and 3.121 for drinking pond water (95% CI 1.872 - 6.566). Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 25958631-9 2015 When compared with drinking tap water, OR for drinking well water was 1.770 (95% CI 1.001 - 2.444), 2.442 for drinking river water (95% CI 0.956 - 3.950), 2.554 for drinking house and field ditch water (95% CI 1.961 - 6.584), and 3.121 for drinking pond water (95% CI 1.872 - 6.566). Water 60-65 nuclear RNA export factor 1 Homo sapiens 28-31 25958631-9 2015 When compared with drinking tap water, OR for drinking well water was 1.770 (95% CI 1.001 - 2.444), 2.442 for drinking river water (95% CI 0.956 - 3.950), 2.554 for drinking house and field ditch water (95% CI 1.961 - 6.584), and 3.121 for drinking pond water (95% CI 1.872 - 6.566). Water 60-65 nuclear RNA export factor 1 Homo sapiens 28-31 25958631-9 2015 When compared with drinking tap water, OR for drinking well water was 1.770 (95% CI 1.001 - 2.444), 2.442 for drinking river water (95% CI 0.956 - 3.950), 2.554 for drinking house and field ditch water (95% CI 1.961 - 6.584), and 3.121 for drinking pond water (95% CI 1.872 - 6.566). Water 60-65 nuclear RNA export factor 1 Homo sapiens 28-31 25958631-9 2015 When compared with drinking tap water, OR for drinking well water was 1.770 (95% CI 1.001 - 2.444), 2.442 for drinking river water (95% CI 0.956 - 3.950), 2.554 for drinking house and field ditch water (95% CI 1.961 - 6.584), and 3.121 for drinking pond water (95% CI 1.872 - 6.566). Water 60-65 nuclear RNA export factor 1 Homo sapiens 28-31 27646620-3 2015 METHODS: In two retrospective case-control studies, the association between gastroenteritis of etiologically unspecified origin or Salmonellosis and food from a restaurant or drinking tap water were tested by univariate and multivariate analysis. Water 188-193 nuclear RNA export factor 1 Homo sapiens 184-187 27646620-7 2015 A resident exposed to tap water from specific water source had a 3.4 times higher odds ratio (univariate analysis of OR 3.4, 95% CI 2.2 to 5.1 is p <0.05, multivariate analysis of RO 2.9, 95% CI 1, 7 to 5.3, p <0.05), for gastroenteritis of unspecific etiology than non-exposed. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 27646620-7 2015 A resident exposed to tap water from specific water source had a 3.4 times higher odds ratio (univariate analysis of OR 3.4, 95% CI 2.2 to 5.1 is p <0.05, multivariate analysis of RO 2.9, 95% CI 1, 7 to 5.3, p <0.05), for gastroenteritis of unspecific etiology than non-exposed. Water 46-51 nuclear RNA export factor 1 Homo sapiens 22-25 27646620-9 2015 CONCLUSION: Analytical cases - controls studies confirmed a causal relationship between salmonellosis and food from the specific restaurant and the causal relationship between gastroenteritis of etiologically unspecified origin and drinking tap water from specific water source. Water 245-250 nuclear RNA export factor 1 Homo sapiens 241-244 25985122-1 2015 In this work, a flow injection analysis (FIA) method was introduced for the determination of trace amounts of thiourea in tap water. Water 126-131 nuclear RNA export factor 1 Homo sapiens 122-125 25710978-0 2014 [Report on tap water quality in France ]. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 25259680-2 2014 Tap water quality was investigated at a six month old plumbing system and chemical and odor quality impacts of six PEX pipe brands were examined. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 25440663-8 2014 The nanographene-based sensor was also demonstrated to be a promising and reliable tool for the rapid detection of cadmium existing in tap water and for the rapid on-site analysis of critical pollution levels of cadmium. Water 139-144 nuclear RNA export factor 1 Homo sapiens 135-138 24405389-4 2014 We aimed to investigate the efficacy and reliability of tap water iontophoresis in children with primary hyperhidrosis. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 24405389-6 2014 In our clinic, tap water iontophoresis was administered at regular intervals, starting with five times per week and decreased to once a week on fifth week. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 24405389-16 2014 CONCLUSION: Tap water iontophoresis is an effective method of treatment for primary palmoplantar and axillary hyperhidrosis in paediatric patients. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 25498933-7 2014 One test group washed their hands with standing water, and the other with running tap water. Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 25056753-4 2014 In Pakistan, water at the source, in the distribution network, and at the consumer tap is heavily polluted with coliforms and fecal coliforms all over the country. Water 13-18 nuclear RNA export factor 1 Homo sapiens 83-86 25823213-1 2014 London tap water experiment. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 25217752-0 2014 Phthalate occurrence in rivers and tap water from central Spain. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 25217752-5 2014 The DBP was found to make the highest average contribution to pollution in both river and tap water. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 25217752-9 2014 A preliminary risk assessment suggested that the risk of exposure to phthalates from tap water in this study is acceptable, although continuous monitoring of the presence of these substances in both drinking and river water should be undertaken to detect possible increases in their concentrations. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88 25856896-6 2014 The coverage rates of tap water and harmless toilets were 10.14% and 10.21% in 1997, and 100.0% and 90.38% in 2012, respectively. Water 26-31 nuclear RNA export factor 1 Homo sapiens 22-25 25412499-11 2014 However, analyses of spiked tap water samples revealed a high correlation (R(2) = 0.863) between results from EMA-qPCR and the reference method. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 25759346-8 2014 RESULTS: Air contamination by Legionella was found in three healthcare facilities (one with active and two with passive sampling), showing a concomitant tap water contamination (median=40,000; range 1,100-43,000 cfu/l). Water 157-162 nuclear RNA export factor 1 Homo sapiens 153-156 25462676-5 2014 We measured urine TCAA and creatinine, and 9 haloacetic acids and 4 trihalomethanes (THM) in tap water. Water 97-102 nuclear RNA export factor 1 Homo sapiens 93-96 25462676-9 2014 Mean total tap water consumption was 2.2l/48h (standard error, 0.1l/48h). Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 25462676-10 2014 Geometric mean urine TCAA excretion rate was 17.3pmol/min [95%CI: 14.0-21.3], which increased 2% for a 10% increase in TCAA ingestion and decreased with total tap water consumption (-17%/l), water intake outside home (-32%), plasmatic volume (-64%/l), in smokers (-79%), and in users of non-steroidal anti-inflammatory drugs (-50%). Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 25764804-3 2014 However, the maximum concentration of viable bacteria in the tap water was 700CFU/mL, which exceeds the legal standard for purity of tap water (100CFU/mL). Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 25514075-4 2014 RESULTS: Nonfiltered tap water accounted for the primary drinking water source in only 10 percent of the respondents. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 25514075-4 2014 RESULTS: Nonfiltered tap water accounted for the primary drinking water source in only 10 percent of the respondents. Water 66-71 nuclear RNA export factor 1 Homo sapiens 21-24 25514075-6 2014 Nonfiltered tap water was much more likely to be utilized in cooking (58 percent). Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 25764804-3 2014 However, the maximum concentration of viable bacteria in the tap water was 700CFU/mL, which exceeds the legal standard for purity of tap water (100CFU/mL). Water 137-142 nuclear RNA export factor 1 Homo sapiens 61-64 25764804-3 2014 However, the maximum concentration of viable bacteria in the tap water was 700CFU/mL, which exceeds the legal standard for purity of tap water (100CFU/mL). Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 25764804-4 2014 Furthermore, Y. enterocolitica O8 was isolated from the tap water with the use of immunomagnetic beads prepared with anti-Y. Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 25764804-7 2014 An epidemiological investigation revealed improper management of the residual chlorine concentration in the tap water. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 25764804-8 2014 This is the first report of an outbreak of Y. enterocolitica due to tap water from a small-scale water system in Japan. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 25672190-13 2014 Logistic regression was done and uncovered water containers (p-value <0.05) to (adjusted OR=1.8; p-=0.008), surrounding marshy land (p=0.03) to (adjusted OR=1.75; p=0.02) & tap water (p=0.001) to (adjusted OR=3.2964; p=0.0012) were found to be associated with the fever. Water 43-48 nuclear RNA export factor 1 Homo sapiens 180-183 25279561-1 2014 Tap water (unfiltered), filtered tap water and processed bottled water (purified water, artificial mineralized water, or natural water) are now the five most widely consumed types of drinking water in China. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 25279561-4 2014 The results showed that the unfiltered tap water group had the lowest values for the maternal gestation index (MGI) and offspring"s learning and memory abilities (OLMA); the lowest offspring survival rate was found in the purified water group; and the highest OLMA were found in the filtered tap water group. Water 43-48 nuclear RNA export factor 1 Homo sapiens 39-42 25279561-4 2014 The results showed that the unfiltered tap water group had the lowest values for the maternal gestation index (MGI) and offspring"s learning and memory abilities (OLMA); the lowest offspring survival rate was found in the purified water group; and the highest OLMA were found in the filtered tap water group. Water 43-48 nuclear RNA export factor 1 Homo sapiens 292-295 25279561-4 2014 The results showed that the unfiltered tap water group had the lowest values for the maternal gestation index (MGI) and offspring"s learning and memory abilities (OLMA); the lowest offspring survival rate was found in the purified water group; and the highest OLMA were found in the filtered tap water group. Water 231-236 nuclear RNA export factor 1 Homo sapiens 39-42 25279561-4 2014 The results showed that the unfiltered tap water group had the lowest values for the maternal gestation index (MGI) and offspring"s learning and memory abilities (OLMA); the lowest offspring survival rate was found in the purified water group; and the highest OLMA were found in the filtered tap water group. Water 231-236 nuclear RNA export factor 1 Homo sapiens 39-42 25279561-5 2014 Thus, the best reproductive and offspring early developmental outcomes were found in the group that drank filtered tap water, which had the lowest levels of pollutants and the richest minerals. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 25012143-7 2014 Tap water samples collected from three towns (North Wales, the English Midlands, and South East England) supplied uniquely by upland reservoir water, river water, and Chalk groundwater, respectively, also showed a remarkable uniformity in Mo concentrations at each location. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 25012143-8 2014 Within each, the variability was very small between houses (old and new), between pre-flush and post-flush samples, and between the tap water and respective source water samples. Water 136-141 nuclear RNA export factor 1 Homo sapiens 132-135 25012143-10 2014 The findings contrast with those for Cu, Zn, Ni, Pb, and Cd, which showed significant differences (p < 0.05) in concentrations between pre-flush and post-flush tap water samples. Water 167-172 nuclear RNA export factor 1 Homo sapiens 163-166 25247736-5 2014 We have determined that these symptoms were caused by the tap water used for irrigation. Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 25102910-10 2014 Nursing staff should pay special attention to children and immunosuppressed patients in terms of tap-water exposure and also their personal hygiene, and should regularly use sterile water for rinsing/cleaning devices. Water 101-106 nuclear RNA export factor 1 Homo sapiens 97-100 25308589-0 2014 Comparison of individuals consuming natural spring water and tap water in terms of urinary tract stone disease. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 25059148-1 2014 This article investigates the flow injection analysis of mercury (II) ions in tap water samples via surface Plasmon resonance detection. Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 25059148-6 2014 The accurate determination of mercury (II) ions in samples of unknown composition is demonstrated with a fortified tap water sample. Water 119-124 nuclear RNA export factor 1 Homo sapiens 115-118 25308589-1 2014 OBJECTIVES: To compare individuals consuming natural spring water and tap water in terms of presence of urinary tract stone disease. Water 74-79 nuclear RNA export factor 1 Homo sapiens 70-73 24911889-0 2014 Concentration of enteric viruses from tap water using an anion exchange resin-based method. Water 42-47 nuclear RNA export factor 1 Homo sapiens 38-41 24690560-6 2014 The selectivity relative to other potentially interfering ions and the applicability in real samples, human serum and tap water, have also been evaluated. Water 122-127 nuclear RNA export factor 1 Homo sapiens 118-121 25127652-7 2014 The practical applications of 1-AgNPs for selective sensing of NO(2-) in different water samples such as ground, river, pond and tap water have also been demonstrated. Water 133-138 nuclear RNA export factor 1 Homo sapiens 129-132 24908641-2 2014 The occurrence of these compounds in tap water in this region is also investigated and a preliminary human health risk characterization performed for those substances found in tap water. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 24908641-2 2014 The occurrence of these compounds in tap water in this region is also investigated and a preliminary human health risk characterization performed for those substances found in tap water. Water 180-185 nuclear RNA export factor 1 Homo sapiens 176-179 24908641-10 2014 Two out of the nineteen compounds studied, namely cocaine (CO) and EPH, were detected in tap water from one sampling point at concentrations of 1.61 and 0.29ngL(-1), respectively. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 24908641-11 2014 The preliminary human health risk characterization showed that no toxic effects could be expected at the detected concentration level in tap water. Water 141-146 nuclear RNA export factor 1 Homo sapiens 137-140 24155180-7 2014 Moreover, the method was applied successfully to the determination of chromium(III) in synthetic samples and tap water. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 25341358-4 2014 In healthy animals drinking tap water, oral citrate administration increased aluminum absorption and, over a 4-week period, increased aluminum deposition in brain and bone by about 2- and 20-fold, respectively. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 25179107-2 2014 The limiting factor for microbial re-growth in a tap water produced by a conventional drinking water treatment plant in China was identified by determining the microbial re-growth potential (MRP) by adding different nutrients to stimulate growth of a natural microbial consortium as inoculum and flow-cytometric enumeration. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 25179107-4 2014 This clearly demonstrated that microbial re-growth in this tap water was limited by P. Most of the re-grown microbial flora (>85%) consisted of high nucleic acid content cells. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 25000576-6 2014 Tap water consumption was significantly associated with creatinine-adjusted urinary TCAA concentration (beta = 0.23 mug/g creatinine per log10 unit; 95% CI: 0.12, 0.35). Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 25000576-11 2014 Our results suggest that tap water consumption, water source, smoking, age, and household income as the primary determinants of exposure to drinking water DBPs should be considered in exposure assessment. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 25518681-1 2014 This research used batch soil column experiment to study the effects of irrigating with reclaimed water and tap water on the soil chemical properties and culturable microorganisms. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 25518681-4 2014 The dominant bacteria in tap water irrigation area was the genus Bacillus whereas that of reclaimed water irrigation area was the genus Acinetobacter. Water 29-34 nuclear RNA export factor 1 Homo sapiens 25-28 24911889-4 2014 Ten liter samples of tap water spiked with different concentrations (10-10,000 TCID50/10 L) of human adenovirus 40 (HAdV-40), hepatitis A virus (HAV) or rotavirus (RV) were concentrated and detected by real time PCR or real time RT-PCR. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 24617572-4 2014 METHODS: In skin soak tests, 5% detergent solutions were applied to the forearms of 10 Japanese healthy volunteers for 30 min followed by washing with tap water once a day for 4 days. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 25093550-7 2014 However, tap water was a major contributor to PFOA intake when it was the main source of drinking water (rather than bottled water). Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 25093550-7 2014 However, tap water was a major contributor to PFOA intake when it was the main source of drinking water (rather than bottled water). Water 98-103 nuclear RNA export factor 1 Homo sapiens 9-12 25093550-7 2014 However, tap water was a major contributor to PFOA intake when it was the main source of drinking water (rather than bottled water). Water 98-103 nuclear RNA export factor 1 Homo sapiens 9-12 25147923-8 2014 Drinking untreated tap water from the defined outbreak area was significantly associated with illness (RR 5.6, 95% CI 1.9-16.4) increasing in a dose response manner. Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 25147923-11 2014 Microbial community sequencing of contaminated tap water revealed abundance of Arcobacter species. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 24907161-7 2014 One subgroup was stored for 3 days in 37 C tap water and the other subgroup was stored for 150 days in 37 C tap water interrupted by 37,500 thermal cycles between 5 C and 55 C. After the storage, the bond strength was measured using a material testing machine. Water 112-117 nuclear RNA export factor 1 Homo sapiens 108-111 25162736-1 2014 BACKGROUND: Many people use bottled water instead of tap water for many reasons such as taste, ease of carrying, and thinking that it is safer than tap water. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 25162736-1 2014 BACKGROUND: Many people use bottled water instead of tap water for many reasons such as taste, ease of carrying, and thinking that it is safer than tap water. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 25029447-6 2014 However, the removability of radionuclides from contaminated tap water has not been tested to date. Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 25202204-1 2014 [Purpose] The purpose of this study was to evaluate the efficacy of tap water (drinking water) and normal saline (sodium chloride solution 0.9%) iontophoresis treatment for a patient with idiopathic hyperhidrosis [Subjects and Methods] In this study, tap water and normal saline iontophoresis were used to treat a 21 year-old female who was suffering from severe palmoplantar idiopathic hyperhidrosis. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 25202204-3 2014 [Results] The subject showed 24.72% and 42.01% decreases in sweat intensity following tap water and normal saline iontophoresis, respectively. Water 90-95 nuclear RNA export factor 1 Homo sapiens 86-89 25202204-4 2014 [Conclusion] Tap water and normal saline iontophoresis are effective in the treatment of idiopathic hyperhidrosis. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 25029447-7 2014 Thus, the current research was undertaken to assess the capability of the apparatus to remove radionuclides from artificially contaminated tap water. Water 143-148 nuclear RNA export factor 1 Homo sapiens 139-142 24583689-8 2014 The SPR biosensor is characterized for 5 different heavy metal ions, Cu(2+), Fe(3+), Mn(2+), Pb(2+), and Hg(2+), most common heavy metal ions found in tap water. Water 155-160 nuclear RNA export factor 1 Homo sapiens 151-154 25029447-8 2014 The results presented here demonstrate that the apparatus can reduce radioactivity levels to below the detection limit in applied tap water containing either 300 Bq/kg of 137Cs or 150 Bq/kg of 125I. Water 134-139 nuclear RNA export factor 1 Homo sapiens 130-133 24659576-5 2014 RESULTS: In settings with network malfunction, consumers of tap water versus POU-treated water had increased GII [incidence density ratio (IDR) = 1.34; 95% CI: 1.00, 1.79]. Water 64-69 nuclear RNA export factor 1 Homo sapiens 60-63 24659576-6 2014 The subset of nonblinded studies showed a significant association between GII and tap water versus POU-treated water consumption (IDR = 1.52; 95% CI: 1.05, 2.20), but there was no association based on studies that blinded participants to their POU water treatment status (IDR = 0.98; 95% CI: 0.90, 1.08). Water 86-91 nuclear RNA export factor 1 Homo sapiens 82-85 24659576-8 2014 CONCLUSIONS: Tap water consumption is associated with GII in malfunctioning distribution networks. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 24726966-10 2014 The tap water production is identified as the most influential process due to its high embodied energy demand in a local context. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 24047516-8 2014 Age <5 years and consumption of tap water were risk factors for norovirus infection. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 24684853-3 2014 METHODS: We determined, in a randomized crossover study, the acute cardiovascular and metabolic responses to 500 mL of tap water at 3 C (cold), 22 C (room) and 37 C (body) in 12 young humans to ascertain an effect of water temperature. Water 123-128 nuclear RNA export factor 1 Homo sapiens 119-122 24632126-0 2014 Evaluation of exposure to trihalomethanes in tap water and semen quality: a prospective study in Wuhan, China. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 24943941-0 2014 The parched planet: water on tap. Water 20-25 nuclear RNA export factor 1 Homo sapiens 29-32 24684853-0 2014 Cardiovascular and metabolic responses to tap water ingestion in young humans: does the water temperature matter? Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 24164509-8 2014 Fluoride concentration in tap water was low (0.04+-SD 0.02 ppm), but was higher in bottled water (0.28+-SD 0.40 ppm). Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 24917858-5 2014 As proof-of-concept we demonstrate examples of microbial dynamics in (i) flowing tap water from a municipal drinking water supply network and (ii) river water from a small creek subject to two rainfall events. Water 85-90 nuclear RNA export factor 1 Homo sapiens 81-84 24091560-3 2014 Tap water has the same washing effects as saline. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 24636953-10 2014 In tap water only trace amounts of antidepressants including citalopram (up to 1.5ng/l), mianserin (up to 0.9ng/l), sertraline (<3.1ng/l), moclobemid (up to 0.3ng/l) and venlafaxine (up to 1.9ng/l) were detected. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 24091560-9 2014 There were statistically significant differences in QoL scores between tap water nasal irrigation group and non-tap water nasal irrigation group. Water 75-80 nuclear RNA export factor 1 Homo sapiens 71-74 24091560-10 2014 The tap water nasal irrigation group had better QoL scores than the non-tap water nasal irrigation group. Water 8-13 nuclear RNA export factor 1 Homo sapiens 4-7 24360431-7 2014 This epimerisation may take place more readily in tap water than in distilled water owing to the complexity of the ions present in tap water. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 24138387-10 2014 Distilled water, 1% NaOCl, ethanol and EDTA were associated with significantly more remaining TAP. Water 10-15 nuclear RNA export factor 1 Homo sapiens 94-97 24875554-0 2014 Levels of haloacetic acids in tap water in an urban Australian city and its relevance to autosomal dominant polycystic kidney disease. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 25141315-3 2014 Warm tap water was administered via a rectal tube to the patients in prone position. Water 9-14 nuclear RNA export factor 1 Homo sapiens 5-8 24730513-5 2014 On the other hand, the multiplicative method outperformed the Bayesian method if actual tap water consumption rates were systematically overestimated. Water 92-97 nuclear RNA export factor 1 Homo sapiens 88-91 24730513-6 2014 If tap water consumption rates gradually decreased over time because of substitution with bottled water or other liquids, neither method clearly outperformed another. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 24597927-0 2014 A new approach for evaluating the water resistance of sunscreens on consumers: tap water vs. salt water vs. chlorine water. Water 34-39 nuclear RNA export factor 1 Homo sapiens 79-82 24597927-0 2014 A new approach for evaluating the water resistance of sunscreens on consumers: tap water vs. salt water vs. chlorine water. Water 83-88 nuclear RNA export factor 1 Homo sapiens 79-82 24597927-9 2014 The method proved capable of discriminating not only sunscreen performances with different water proofing ingredients but also water specific sunscreens such as a beach dedicated product showing a 20% higher resistance to salt water vs. tap and chlorine waters. Water 127-132 nuclear RNA export factor 1 Homo sapiens 237-240 24597927-9 2014 The method proved capable of discriminating not only sunscreen performances with different water proofing ingredients but also water specific sunscreens such as a beach dedicated product showing a 20% higher resistance to salt water vs. tap and chlorine waters. Water 127-132 nuclear RNA export factor 1 Homo sapiens 237-240 24886757-2 2014 This study reports the perspectives on health risks from tap water and corresponding use of, and spending on, bottled water in a number of different communities in Canada. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 24360431-7 2014 This epimerisation may take place more readily in tap water than in distilled water owing to the complexity of the ions present in tap water. Water 54-59 nuclear RNA export factor 1 Homo sapiens 131-134 24360431-7 2014 This epimerisation may take place more readily in tap water than in distilled water owing to the complexity of the ions present in tap water. Water 78-83 nuclear RNA export factor 1 Homo sapiens 131-134 24360431-7 2014 This epimerisation may take place more readily in tap water than in distilled water owing to the complexity of the ions present in tap water. Water 78-83 nuclear RNA export factor 1 Homo sapiens 131-134 25194123-5 2014 In 2012, tap water provided to almost one million Italians in 112 municipalities of three regions (Latium, Tuscany and Campania), did not comply with the legal limits for the following parameters: arsenic, boron and fluorides. Water 13-18 nuclear RNA export factor 1 Homo sapiens 9-12 24636435-0 2014 Compliance with tap water iontophoresis in patients with palmoplantar hyperhidrosis. Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 24633562-7 2014 Tap water and bottled water were also analyzed by the column, and nitrate was detected as 20.1 and 13.8 mg L(-1), respectively. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 24170038-2 2014 We compared changes in pharyngeal swallowing and sensory aspects induced by a carbonated beverage preferred by Japanese with those induced by carbonated water, a sports drink, and tap water in healthy young subjects and elderly inpatients with no swallowing problems. Water 184-189 nuclear RNA export factor 1 Homo sapiens 180-183 24581998-9 2014 Post hoc tests showed that the CCT in the sodium chloride (NaCl) 10.0% and tap-water groups increased significantly less than with 4 other preservation methods. Water 79-84 nuclear RNA export factor 1 Homo sapiens 75-78 24581998-12 2014 Lens epithelial cells from eyes preserved in tap water for 48 hours appeared to be intact but lost cell organization. Water 49-54 nuclear RNA export factor 1 Homo sapiens 45-48 24581998-13 2014 CONCLUSIONS: Of the 15 tested methods to preserve porcine eyes, tap water (mineral content 1.79 mmol/L) resulted in the least corneal swelling. Water 68-73 nuclear RNA export factor 1 Homo sapiens 64-67 24512498-7 2014 The mixing and gradient formation units were incorporated into a device for analysis of nitrate in tap water with standard addition as a single run and multiple depth detection cells to provide an extended linear range. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 24783149-2 2014 The main objective of introduction of bottled water in the society was its better safety, taste and convenience over tap water. Water 46-51 nuclear RNA export factor 1 Homo sapiens 117-120 23361441-3 2014 Three hundred and six children aged 1 to 5 years and currently drinking tap water participated in the study. Water 76-81 nuclear RNA export factor 1 Homo sapiens 72-75 23443240-0 2014 A time series study of gastroenteritis and tap water quality in the Nantes area, France, 2002-2007. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 23838883-6 2014 Household tap-water arsenic, toenail arsenic and urinary inorganic arsenic and metabolites were significantly higher in Ajo (20.6+-3.5 mug/l, 0.54+-0.77 mug/g and 27.7+-21.2 mug/l, respectively) than in Tucson (3.9+-2.5 mug/l, 0.16+-0.20 mug/g and 13.0+-13.8 mug/l, respectively). Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 24387938-0 2014 [Fluoride content in tap water in Spain and prevention of dental caries]. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 24532542-0 2014 Determination of endosulfan isomers and their metabolites in tap water and commercial samples using microextraction by packed sorbent and GC-MS. A simple, rapid, accurate and sensitive method using microextraction by packed sorbent (MEPS) followed by GC-MS has been pursued for the determination of organochlorine insecticide endosulfan isomers (alpha and beta) and their metabolites (ether, lactone and sulfate). Water 65-70 nuclear RNA export factor 1 Homo sapiens 61-64 24532542-8 2014 The developed method is applicable for the quantification of these compounds in tap water and commercial samples. Water 84-89 nuclear RNA export factor 1 Homo sapiens 80-83 24534568-1 2014 A pipette tip-based molecularly imprinted polymer monolith microextraction (PT-MIPMME) method was developed for the selective extraction of difenoconazole in tap water and grape juice. Water 162-167 nuclear RNA export factor 1 Homo sapiens 158-161 24534568-8 2014 The results showed that difenoconazole was selectively enriched from tap water and grape juice samples. Water 73-78 nuclear RNA export factor 1 Homo sapiens 69-72 23860400-6 2014 Among subjects exposed to tap water As >10 p.p.b., aggregate inorganic exposure was 24.5-26.1 mug/day, with approximately 30% of intake from food. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 24636435-1 2014 BACKGROUND: Patients tend to be noncompliant with tap water iontophoresis (TWI), which is an effective treatment option for palmoplantar hyperhidrosis. Water 54-59 nuclear RNA export factor 1 Homo sapiens 50-53 24443781-0 2014 Perceptions of tap water and school water fountains and association with intake of plain water and sugar-sweetened beverages. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 24443781-1 2014 BACKGROUND: Little is known regarding youth perceptions of tap water and school water fountains and how these relate to water and sugar-sweetened beverage (SSB) intake. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 24443781-4 2014 Perceived tap water risk was more prevalent among non-Hispanic (NH) Blacks (26.4%) and Hispanics (28.3%) compared with NH Whites (14.7%, p < .001) and more prevalent among lower-income youth. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 24443781-6 2014 Perceived tap water risk was not associated with SSB intake (odds ratio [OR] = 1.0, 95% confidence interval [CI]: 0.6, 1.5) or water intake (OR = 1.4, 95% CI: 0.9, 2.1). Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 24443781-8 2014 CONCLUSION: Negative perceptions of tap water and water fountains among youth are common and should be considered in efforts to provide water in schools. Water 40-45 nuclear RNA export factor 1 Homo sapiens 36-39 23166116-0 2014 Pseudofungal tap water contaminants in sputum cytology. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 24413272-9 2014 Use of tap water to rinse contact lens cases was associated with significantly more cases contaminated with Gram-negative bacteria (GNB) (30% vs. 10%, p < 0.001), a greater risk of GNB case contamination (OR: 2.91, p < 0.001. Water 11-16 nuclear RNA export factor 1 Homo sapiens 7-10 24586302-1 2014 Identifying which factors influence household water management can help policy makers target interventions to improve drinking water quality for communities that may not receive adequate water quality at the tap. Water 46-51 nuclear RNA export factor 1 Homo sapiens 208-211 24586302-5 2014 Specifically, households in PRASA communities are more likely to boil and filter their tap water due to perceptions of low water quality. Water 91-96 nuclear RNA export factor 1 Homo sapiens 87-90 24586302-7 2014 Based on informal discussions with community members, we suggest that water quality may be improved if PRASA systems improve the taste and odor of tap water, possibly by allowing for dechlorination prior to distribution, and if non-PRASA systems reduce the turbidity of water at the tap, possibly by increasing the degree of chlorination and filtering prior to distribution. Water 70-75 nuclear RNA export factor 1 Homo sapiens 147-150 24586302-7 2014 Based on informal discussions with community members, we suggest that water quality may be improved if PRASA systems improve the taste and odor of tap water, possibly by allowing for dechlorination prior to distribution, and if non-PRASA systems reduce the turbidity of water at the tap, possibly by increasing the degree of chlorination and filtering prior to distribution. Water 70-75 nuclear RNA export factor 1 Homo sapiens 283-286 24586302-7 2014 Based on informal discussions with community members, we suggest that water quality may be improved if PRASA systems improve the taste and odor of tap water, possibly by allowing for dechlorination prior to distribution, and if non-PRASA systems reduce the turbidity of water at the tap, possibly by increasing the degree of chlorination and filtering prior to distribution. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 24586302-7 2014 Based on informal discussions with community members, we suggest that water quality may be improved if PRASA systems improve the taste and odor of tap water, possibly by allowing for dechlorination prior to distribution, and if non-PRASA systems reduce the turbidity of water at the tap, possibly by increasing the degree of chlorination and filtering prior to distribution. Water 151-156 nuclear RNA export factor 1 Homo sapiens 147-150 24246238-10 2014 Urinary metabolites of both atrazine and dealkylated triazine were correlated with tap water consumption (OR=2.94, 1.09-7.90, and OR=1.82, 1.10-3.03, respectively); hydroxylated triazine metabolites were correlated with fish intake (OR=1.48, 1.09-1.99). Water 87-92 nuclear RNA export factor 1 Homo sapiens 83-86 24055670-4 2014 We assess three types of entities engaged in water management along the source-to-tap spectrum (watershed agencies, water utilities, and public health authorities). Water 45-50 nuclear RNA export factor 1 Homo sapiens 82-85 24127653-8 2014 In addition, the highest infection risk was 1 caused by HAdV in surface water at the slum outlet, while the lowest infection risk was 2.71 x 10(-6) caused by E. coli O157:H7 in tap water. Water 181-186 nuclear RNA export factor 1 Homo sapiens 177-180 24442359-11 2014 These findings suggest that Aspergillus is found in the hospital environment including the air, surface, and tap water. Water 113-118 nuclear RNA export factor 1 Homo sapiens 109-112 24333849-1 2014 Little is known about the nature of the microbiology in tap waters delivered to consumers via public drinking water distribution systems (DWDSs). Water 60-65 nuclear RNA export factor 1 Homo sapiens 56-59 24487453-0 2014 Risk factors associated with the choice to drink bottled water and tap water in rural Saskatchewan. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 24487453-1 2014 A cross-sectional study investigated risk factors associated with choices to drink bottled water and tap water in rural Saskatchewan. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 24487453-4 2014 Those who reported tap water was not safe to drink were more likely to choose bottled water, an effect greater for those who had no aesthetic complaints (p <= 0.001), while those with aesthetic complaints were more likely to choose bottled water if they believed the water was safe (p < 0.001). Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 24487453-4 2014 Those who reported tap water was not safe to drink were more likely to choose bottled water, an effect greater for those who had no aesthetic complaints (p <= 0.001), while those with aesthetic complaints were more likely to choose bottled water if they believed the water was safe (p < 0.001). Water 86-91 nuclear RNA export factor 1 Homo sapiens 19-22 24487453-4 2014 Those who reported tap water was not safe to drink were more likely to choose bottled water, an effect greater for those who had no aesthetic complaints (p <= 0.001), while those with aesthetic complaints were more likely to choose bottled water if they believed the water was safe (p < 0.001). Water 86-91 nuclear RNA export factor 1 Homo sapiens 19-22 24487453-4 2014 Those who reported tap water was not safe to drink were more likely to choose bottled water, an effect greater for those who had no aesthetic complaints (p <= 0.001), while those with aesthetic complaints were more likely to choose bottled water if they believed the water was safe (p < 0.001). Water 86-91 nuclear RNA export factor 1 Homo sapiens 19-22 24487453-6 2014 A similar pattern of risk factors was associated with a decreased likelihood of consuming tap water daily; however, the use of a community water supply was not significant. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 24121662-12 2014 As the recycled water has similar effects like tap water on cloth and washing machine, it is safe to use for laundry. Water 16-21 nuclear RNA export factor 1 Homo sapiens 47-50 24332350-8 2014 The fiber was successfully applied in the analysis of tap water and effluent samples from a waste water treatment plant with spike recoveries ranging from 68.5 to 105.1%. Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 24332350-8 2014 The fiber was successfully applied in the analysis of tap water and effluent samples from a waste water treatment plant with spike recoveries ranging from 68.5 to 105.1%. Water 98-103 nuclear RNA export factor 1 Homo sapiens 54-57 25281816-8 2014 The conducted tests demonstrated that microfungi were found in tap water originating from the cities and in bottled water. Water 67-72 nuclear RNA export factor 1 Homo sapiens 63-66 25281816-10 2014 Eighteen species of microfungi were identified in tap water from Olsztyn and 9 species in tap water from Ostroleka. Water 94-99 nuclear RNA export factor 1 Homo sapiens 90-93 23900955-7 2014 Furthermore, tap water from Lisbon and three small neighbor cities was analyzed. Water 17-22 nuclear RNA export factor 1 Homo sapiens 13-16 24308807-0 2014 Boiling of simulated tap water: effect on polar brominated disinfection byproducts, halogen speciation, and cytotoxicity. Water 25-30 nuclear RNA export factor 1 Homo sapiens 21-24 24728544-1 2014 The aims of this study are to investigate the presence of 30 substances known or thought to act as endocrine disrupting compounds in tap water from the main water supply areas for region of Madrid, to determine the total estrogenic activity of the samples analysed and to estimate the health risk for the population resulting from those compounds found at detectable concentrations. Water 137-142 nuclear RNA export factor 1 Homo sapiens 133-136 24728544-5 2014 Tap water in the region of Madrid is contaminated with traces (ng/L) of compounds with endocrine disrupting properties. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 24756667-1 2014 The electrochemical degradation of the nonsteroidal anti-inflammatory drug ketoprofen in tap water has been studied using electro-Fenton (EF) and anodic oxidation (AO) processes with platinium (Pt) and boron-doped diamond (BDD) anodes and carbon felt cathode. Water 93-98 nuclear RNA export factor 1 Homo sapiens 89-92 23632123-3 2014 A 1:1 case-control study showed that consumption of tap water was a risk factor for acquiring infection [odds ratio (OR) 2.18, 95% confidence interval (CI) 1.11-4.28]. Water 56-61 nuclear RNA export factor 1 Homo sapiens 52-55 24308807-1 2014 Tap water typically contains numerous halogenated disinfection byproducts (DBPs) as a result of disinfection, especially of chlorination. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 24308807-9 2014 Thus, boiling of tap water can be regarded as a "detoxification" process and may reduce human exposure to halogenated DBPs through tap water ingestion. Water 135-140 nuclear RNA export factor 1 Homo sapiens 131-134 24308807-5 2014 A novel adsorption unit for volatile total organic halogen was designed, which enabled the evaluation of halogen speciation and mass balances in the simulated tap water samples during boiling. Water 163-168 nuclear RNA export factor 1 Homo sapiens 159-162 24308807-7 2014 The simulated tap water sample without boiling was cytotoxic in a chronic (72 h) exposure to mammalian cells; this cytotoxicity was reduced by 76.9% after boiling for 5 min. Water 18-23 nuclear RNA export factor 1 Homo sapiens 14-17 24308807-9 2014 Thus, boiling of tap water can be regarded as a "detoxification" process and may reduce human exposure to halogenated DBPs through tap water ingestion. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 24308807-9 2014 Thus, boiling of tap water can be regarded as a "detoxification" process and may reduce human exposure to halogenated DBPs through tap water ingestion. Water 21-26 nuclear RNA export factor 1 Homo sapiens 131-134 24308807-9 2014 Thus, boiling of tap water can be regarded as a "detoxification" process and may reduce human exposure to halogenated DBPs through tap water ingestion. Water 135-140 nuclear RNA export factor 1 Homo sapiens 17-20 23098620-0 2014 The relationship of perceptions of tap water safety with intake of sugar-sweetened beverages and plain water among US adults. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 24343032-7 2014 If tap water is used, then the use of sterile filters is strongly recommended. Water 7-12 nuclear RNA export factor 1 Homo sapiens 3-6 25005864-3 2014 The response ratios for washing by tap water, boiling and sun drying were 0.59, 0.71 and 0.65, respectively, indicating that they could reduce the pesticide residues effectively. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 25030724-0 2014 Radioactive substances in tap water. Water 30-35 nuclear RNA export factor 1 Homo sapiens 26-29 25030724-4 2014 On March 16(th), 2011, radioiodine and radioactive cesium were detected at levels of 177 Bq/kg and 58 Bq/kg, respectively, in tap water in Fukushima city (about 62km northwest of TEPCO F-1 NPP). Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 25030724-5 2014 On March 20th, radioiodine was detected in tap water at a level of 965 Bq/kg, which is over the value-index of restrictions on food and drink intake (radioiodine 300 Bq/kg (infant intake 100 Bq/kg)) designated by the Nuclear Safety Commission. Water 47-52 nuclear RNA export factor 1 Homo sapiens 43-46 24382119-4 2014 Compared to the total number of tap water samples analyzed (122), the values higher than limits of Directive 98/83/EC were 17% for lead, 11% for nickel, 14% for zinc, and 7% for iron. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 23098620-1 2014 OBJECTIVE: Research is limited on whether mistrust of tap water discourages plain water intake and leads to a greater intake of sugar-sweetened beverages (SSB). Water 58-63 nuclear RNA export factor 1 Homo sapiens 54-57 23098620-1 2014 OBJECTIVE: Research is limited on whether mistrust of tap water discourages plain water intake and leads to a greater intake of sugar-sweetened beverages (SSB). Water 82-87 nuclear RNA export factor 1 Homo sapiens 54-57 23098620-3 2014 DESIGN: The study examined perceptions of tap water safety and their cross-sectional association with intake of SSB and plain water. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 23098620-8 2014 Both mistrust of tap water safety and favouring bottled water differed by region, age, race/ethnicity, income and education. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 23098620-9 2014 The associations of tap water mistrust with intake of SSB and plain water were modified by race/ethnicity (P < 0 05). Water 24-29 nuclear RNA export factor 1 Homo sapiens 20-23 23098620-9 2014 The associations of tap water mistrust with intake of SSB and plain water were modified by race/ethnicity (P < 0 05). Water 68-73 nuclear RNA export factor 1 Homo sapiens 20-23 23098620-10 2014 Non-white racial/ethnic groups who disagreed that their local tap water was safe to drink were more likely to report low intake of plain water. Water 66-71 nuclear RNA export factor 1 Homo sapiens 62-65 23098620-10 2014 Non-white racial/ethnic groups who disagreed that their local tap water was safe to drink were more likely to report low intake of plain water. Water 137-142 nuclear RNA export factor 1 Homo sapiens 62-65 23098620-11 2014 The odds of consuming >=1 SSB/d among Hispanics who mistrusted their local tap water was twice that of Hispanics who did not (OR = 2 0; 95 % CI 1 2, 3 3). Water 82-87 nuclear RNA export factor 1 Homo sapiens 78-81 25295305-0 2014 Determination of haloacetic acids in bottled and tap water sources by dispersive liquid-liquid microextraction and GC-MS analysis. Water 53-58 nuclear RNA export factor 1 Homo sapiens 49-52 23098620-12 2014 CONCLUSIONS: Public health efforts to promote healthy beverages should recognize the potential impact of tap water perceptions on water and SSB intake among minority populations. Water 109-114 nuclear RNA export factor 1 Homo sapiens 105-108 23098620-12 2014 CONCLUSIONS: Public health efforts to promote healthy beverages should recognize the potential impact of tap water perceptions on water and SSB intake among minority populations. Water 130-135 nuclear RNA export factor 1 Homo sapiens 105-108 24185489-0 2013 Rapid and ratiometric detection of hypochlorite with real application in tap water: molecules to low cost devices (TLC sticks). Water 77-82 nuclear RNA export factor 1 Homo sapiens 73-76 23673346-6 2014 The feasibility of this method was demonstrated in tap-water and a tap-water filled cavity in the tissue-mimicking gelatin-agar phantom as capable of observing temporal evolutions of cavitation bubble cloud with temporal resolution of several microseconds, lateral and axial resolution of 0.50 mm and 0.29 mm respectively. Water 55-60 nuclear RNA export factor 1 Homo sapiens 51-54 23673346-6 2014 The feasibility of this method was demonstrated in tap-water and a tap-water filled cavity in the tissue-mimicking gelatin-agar phantom as capable of observing temporal evolutions of cavitation bubble cloud with temporal resolution of several microseconds, lateral and axial resolution of 0.50 mm and 0.29 mm respectively. Water 71-76 nuclear RNA export factor 1 Homo sapiens 67-70 23892027-1 2014 The aim of this study was to infer about the modes and extent of dispersion of Sphingomonadaceae via tap water. Water 105-110 nuclear RNA export factor 1 Homo sapiens 101-104 23892027-4 2014 Sphingomonadaceae from hospital tap water comprised members of the genera Sphingomonas, Sphingobium, Novosphingobium and Blastomonas. Water 36-41 nuclear RNA export factor 1 Homo sapiens 32-35 23892027-8 2014 Although the potential of Sphingomonadaceae as opportunistic pathogens may be low, the capacity of these bacteria to thrive in water supply systems, combined with the intrinsic or acquired antibiotic resistance, may raise the risk associated with their occurrence in hospital tap water. Water 127-132 nuclear RNA export factor 1 Homo sapiens 276-279 23892027-8 2014 Although the potential of Sphingomonadaceae as opportunistic pathogens may be low, the capacity of these bacteria to thrive in water supply systems, combined with the intrinsic or acquired antibiotic resistance, may raise the risk associated with their occurrence in hospital tap water. Water 280-285 nuclear RNA export factor 1 Homo sapiens 276-279 25293563-4 2014 Two of three studies showed that tap water significantly lowered pH as well, but only if it was administered within 60 seconds after exposure. Water 37-42 nuclear RNA export factor 1 Homo sapiens 33-36 24185489-2 2013 The sensor could be useful for the detection of hypochlorites in tap water. Water 69-74 nuclear RNA export factor 1 Homo sapiens 65-68 24379894-9 2013 When available, the English children drank municipal tap water more often than did the Spanish children. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 23796954-6 2013 The recovery of adenovirus was highest for samples in unconditioned tap water (pH 8) using the 1MDS filter and celite for secondary concentration. Water 72-77 nuclear RNA export factor 1 Homo sapiens 68-71 24125471-6 2013 Detection of Au(3+) ions in complex and environmentally and biologically relevant solvents such as tap water and phosphate buffer solution (PBS) was also successfully carried out in order to demonstrate the real-life application of these sensors. Water 103-108 nuclear RNA export factor 1 Homo sapiens 99-102 24148493-7 2013 When applied to spiked samples of real water, the method provided recoveries of 88.6-106.3% for tap water, 87.8-108.5% for Mi River water, 82.7-113.5% for chemical wastewater, 45.5-115.3% for urine, and 46.4-126.2% for fruit juice, with RSDs (n=5) less than 4%, 6%, 8%, 10%, and 9% respectively. Water 39-44 nuclear RNA export factor 1 Homo sapiens 96-99 24649672-2 2013 Sodium sulfide dissolved in tap water was pumped into the bioreactor as sulfide for biological desulfurization. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 24597042-1 2013 The objective of drinking water treatment plants (DWTP) is to supply the population with tap water that is in optimal condition and in compliance with water quality regulations. Water 26-31 nuclear RNA export factor 1 Homo sapiens 89-92 24144041-7 2013 However, the particle concentration of the filtered water from the AWM was still four times higher than that found in regular tap water. Water 52-57 nuclear RNA export factor 1 Homo sapiens 126-129 24144041-7 2013 However, the particle concentration of the filtered water from the AWM was still four times higher than that found in regular tap water. Water 130-135 nuclear RNA export factor 1 Homo sapiens 126-129 24219567-8 2013 Plain water, from tap or bottled sources, contributed 30-37% of total dietary water. Water 6-11 nuclear RNA export factor 1 Homo sapiens 18-21 24219567-9 2013 Overall, 56% of drinking water volume was from tap water while bottled water provided 44%. Water 25-30 nuclear RNA export factor 1 Homo sapiens 47-50 24219567-12 2013 Plain water consumption (bottled and tap) tended to be associated with higher incomes. Water 6-11 nuclear RNA export factor 1 Homo sapiens 37-40 24019225-0 2013 A convenient and sensitive method for haloacetic acid analysis in tap water by on-line field-amplified sample-stacking CE-ESI-MS. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 24019225-1 2013 In this study, we propose a simple strategy based on flow injection and field-amplified sample-stacking CE-ESI-MS/MS to analyze haloacetic acids (HAAs) in tap water. Water 159-164 nuclear RNA export factor 1 Homo sapiens 155-158 24019225-2 2013 Tap water was passed through a desalination cartridge before field-amplified sample-stacking CE-ESI-MS/MS analysis to reduce sample salinity. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23759536-0 2013 Chlorination by-products in tap water and semen quality in England and Wales. Water 32-37 nuclear RNA export factor 1 Homo sapiens 28-31 23796954-9 2013 By optimizing secondary elution steps, AdV recovery from tap water could be improved at least two-fold compared to the currently used methodology. Water 61-66 nuclear RNA export factor 1 Homo sapiens 57-60 23992844-1 2013 An analytical method based on on-line solid-phase extraction coupled to liquid chromatography with fluorescence detection has been developed to determine quinolones in tap water and human urine. Water 172-177 nuclear RNA export factor 1 Homo sapiens 168-171 24044418-5 2013 Heating of the tap water with low pH led to a more significant increase of chloroform and a more significant short-term increase of DCAN. Water 19-24 nuclear RNA export factor 1 Homo sapiens 15-18 23992844-5 2013 The method allowed the determination of 11 quinolones directly in tap water samples in less than 20 min and with limits of detection ranging between 7 and 110 ng/L. Water 70-75 nuclear RNA export factor 1 Homo sapiens 66-69 23895327-5 2013 Two patients reacted also to tap water or to normal saline, but less intensely. Water 33-38 nuclear RNA export factor 1 Homo sapiens 29-32 23769186-5 2013 TCAA level in home tap water supply was not correlated with urinary TCAA (0.18, P=0.29). Water 23-28 nuclear RNA export factor 1 Homo sapiens 19-22 23769186-6 2013 Cold unfiltered tap water intake at home measured by questionnaire was correlated with urinary TCAA (0.44, P=0.007), but correlation was stronger still for cold unfiltered tap water intake reported over the 3 days prior to urine sampling (0.60, P<0.001). Water 20-25 nuclear RNA export factor 1 Homo sapiens 16-19 23769186-6 2013 Cold unfiltered tap water intake at home measured by questionnaire was correlated with urinary TCAA (0.44, P=0.007), but correlation was stronger still for cold unfiltered tap water intake reported over the 3 days prior to urine sampling (0.60, P<0.001). Water 176-181 nuclear RNA export factor 1 Homo sapiens 172-175 23769186-7 2013 For unemployed women TCAA ingestion at home, derived from tap water sampling and self-reported water-use, correlated strongly with urinary TCAA (0.78, P<0.001), but for employed women the correlation was weak (0.31, P=0.20). Water 62-67 nuclear RNA export factor 1 Homo sapiens 58-61 24266111-4 2013 Tap water with KMnO4 was the best cathodic electrolyte as the highest values for all the measured MFC parameters were reported with it. Water 4-9 nuclear RNA export factor 1 Homo sapiens 0-3 23769186-8 2013 Results suggest individual tap water intake is most influential in determining TCAA exposure variability in this cohort, and that TCAA ingestion at home is a valid proxy for TCAA exposure for unemployed women but less satisfactory for employed women. Water 31-36 nuclear RNA export factor 1 Homo sapiens 27-30 23777639-3 2013 Study participants were 904 adult residents of Churchill County, Nevada, whose home tap water supplies contained <3 to about 1200 microg of arsenic per liter. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 23777639-5 2013 Increased tap water arsenic concentration and consumption were associated with significant upward trends for urinary speciated and total and toenail total arsenical concentrations. Water 14-19 nuclear RNA export factor 1 Homo sapiens 10-13 23807022-5 2013 486) mug/day for samples cooked with tap water. Water 41-46 nuclear RNA export factor 1 Homo sapiens 37-40 23889610-9 2013 In the final multiple variable model, significant interactions were found between tooth brushing frequency and initial D1 status, and also between family income and home tap water fluoride level. Water 174-179 nuclear RNA export factor 1 Homo sapiens 170-173 23889610-11 2013 More frequent tooth brushing was protective of sound surfaces, and fluoride in home tap water was also protective, but significantly more so for adolescents in low-income families. Water 88-93 nuclear RNA export factor 1 Homo sapiens 84-87 23872186-8 2013 Eleven of the 12 tap water samples and all of the filtered tap water samples had a total bacterial load that exceeded the Thai water quality standards. Water 21-26 nuclear RNA export factor 1 Homo sapiens 17-20 23872186-8 2013 Eleven of the 12 tap water samples and all of the filtered tap water samples had a total bacterial load that exceeded the Thai water quality standards. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 23872186-8 2013 Eleven of the 12 tap water samples and all of the filtered tap water samples had a total bacterial load that exceeded the Thai water quality standards. Water 63-68 nuclear RNA export factor 1 Homo sapiens 59-62 23866131-8 2013 Dilution of urine with tap water decreased the phosphate loading on HAIX resin. Water 27-32 nuclear RNA export factor 1 Homo sapiens 23-26 23872186-9 2013 One of the tap water samples and one of the filtered tap water samples were found to be positive for Shigella sp., although none of the floodwater samples showed detectable levels of this pathogen as determined by PCR analysis. Water 15-20 nuclear RNA export factor 1 Homo sapiens 11-14 23872186-9 2013 One of the tap water samples and one of the filtered tap water samples were found to be positive for Shigella sp., although none of the floodwater samples showed detectable levels of this pathogen as determined by PCR analysis. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 23872186-11 2013 Most of the tap water samples and all filtered tap water samples were found to be contaminated with Vibrio cholerae. Water 16-21 nuclear RNA export factor 1 Homo sapiens 12-15 23872186-11 2013 Most of the tap water samples and all filtered tap water samples were found to be contaminated with Vibrio cholerae. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 23608541-0 2013 Ultrasensitive and selective gold film-based detection of mercury (II) in tap water using a laser scanning confocal imaging-surface plasmon resonance system in real time. Water 78-83 nuclear RNA export factor 1 Homo sapiens 74-77 23608541-2 2013 The detection limit was as low as 0.01ng/ml for Hg(2+) ions in ultrapure and tap water based on a T-rich, single-stranded DNA (ssDNA)-modified gold film, which can be individually manipulated using specific T-Hg(2+)-T complex formation. Water 81-86 nuclear RNA export factor 1 Homo sapiens 77-80 23608541-5 2013 The coefficients obtained for ultrapure and tap water were 0.99902 and 0.99512, respectively, for the linear part over a range of 0.01-100ng/ml. Water 48-53 nuclear RNA export factor 1 Homo sapiens 44-47 23608541-6 2013 The results show that the double-effect sensor has potential for practical applications with ultra sensitivity and selectivity, especially in online or real-time monitoring of Hg(2+) ions pollution in tap water with the further improvement of portable LSCI-SPR instrument. Water 205-210 nuclear RNA export factor 1 Homo sapiens 201-204 24386522-3 2013 An analytical electrolyte for tap water was used instead of an expensive acid or base ionic solution. Water 34-39 nuclear RNA export factor 1 Homo sapiens 30-33 24040477-13 2013 According to our results, consuming 16 C water, cool tap water, could be suggested in dehydration. Water 57-62 nuclear RNA export factor 1 Homo sapiens 53-56 23494953-6 2013 The reductions due to washing with tap water (for 10 min) and the emulsion with only egg yolk lecithin (at high concentration for 10 min) were 25.18 %, 37.83%, 21.84%, 20.87%, 13.86% and < LOQ, 59.70%, 54.09%, 54.76%, 54.47%, respectively. Water 39-44 nuclear RNA export factor 1 Homo sapiens 35-38 23446885-0 2013 Occurrence of disinfection by-products in tap water distribution systems and their associated health risk. Water 46-51 nuclear RNA export factor 1 Homo sapiens 42-45 23997676-3 2013 The results indicate that green tea prepared with distilled water exhibits higher antioxidant activity than that made with tap water. Water 127-132 nuclear RNA export factor 1 Homo sapiens 123-126 23937937-7 2013 Different water samples were examined, including deionized, tap, and river waters, and sensitive detection was achieved. Water 10-15 nuclear RNA export factor 1 Homo sapiens 60-63 23743873-5 2013 The motion of the microjets is also reduced in tap water, which contains large quantities of inorganic ions that have been purposely introduced into tap water via processing in water treatment plants. Water 51-56 nuclear RNA export factor 1 Homo sapiens 47-50 23743873-5 2013 The motion of the microjets is also reduced in tap water, which contains large quantities of inorganic ions that have been purposely introduced into tap water via processing in water treatment plants. Water 51-56 nuclear RNA export factor 1 Homo sapiens 149-152 23997676-4 2013 The high performance liquid chromatography showed that major constituents of green tea were found in higher concentrations in tea made with distilled water than in that made with tap water. Water 183-188 nuclear RNA export factor 1 Homo sapiens 179-182 23822900-3 2013 Of the liquid media, sweat and urine yielded the highest amount of silver release, up to 38% of the silver mass in products; tap water yielded the lowest amount, <=1.5%. Water 129-134 nuclear RNA export factor 1 Homo sapiens 125-128 23806897-7 2013 Exposure of patients who have central venous catheters and other invasive devices to tap water poses a risk for infection with waterborne pathogens. Water 89-94 nuclear RNA export factor 1 Homo sapiens 85-88