PMID-sentid Pub_year Sent_text comp_official_name comp_offsetprotein_name organism prot_offset 32199204-3 2020 The results showed that the presence of 2-50 g L-1 microplastics could decrease the pesticide residues in water. Water 106-111 immunoglobulin kappa variable 1-16 Homo sapiens 47-50 2848782-2 1988 For example, ground water in the surficial aquifer of central Florida commonly has gross-alpha radioactivity in excess of 555 Bq m-3 (15 pCi L-1). Water 20-25 immunoglobulin kappa variable 1-16 Homo sapiens 141-144 32224384-5 2020 The total concentrations of the 11 target OPEs ( 11OPEs) in the water samples ranged 32.9-227 ng L-1. Water 64-69 immunoglobulin kappa variable 1-16 Homo sapiens 97-100 2575159-1 1989 Norethisterone and ethinyloestradiol concentrations in sewage effluent, reservoirs, rivers and potable water have been estimated at less than 20 ng L-1, a value unlikely to present a significant risk to human health. Water 103-108 immunoglobulin kappa variable 1-16 Homo sapiens 148-151 30628559-4 2020 The MF of the water previously adsorbed in the GAC fixed bed allowed the greater removal of 100% of the carbamates pesticides with an initial concentration of 25 mug L-1 during the first 48 h of operation. Water 14-19 immunoglobulin kappa variable 1-16 Homo sapiens 166-169 32069384-3 2020 The active principles were not found in the soil and sediment samples, only the propoxur principle was found in the water, reaching values of up to 0.025 mug L-1 . Water 116-121 immunoglobulin kappa variable 1-16 Homo sapiens 158-161 32113565-3 2020 This has led the European Union and other global organizations to reduce the maximum residue limit for the total arsenic up to 10 mug L-1 in water for human consumption. Water 141-146 immunoglobulin kappa variable 1-16 Homo sapiens 134-137 31520978-4 2020 About 35% of the drinking water samples showed radon concentrations above the European Union"s parametric value of 100 Bq l-1. Water 26-31 immunoglobulin kappa variable 1-16 Homo sapiens 122-125 31190125-8 2020 Paired drinking water samples contained a median iodine concentration of 3.2 microg L-1 (0.2-304.1 microg L-1). Water 16-21 immunoglobulin kappa variable 1-16 Homo sapiens 84-87 32152284-4 2020 Results from our investigation indicate that DC in saline (EC > 1000 muS cm-1) water bodies (mean +- S.D, 297.13 +- 356.14 mg L-1, n = 186) are much higher than those in fresh water bodies (79.55 +- 199.34 mg L-1, n = 669). Water 79-84 immunoglobulin kappa variable 1-16 Homo sapiens 126-129 31062242-4 2020 Water dissolved-phase SigmaPCB concentrations ranged from 150 to 170 pg L-1 with a median of 160 pg L-1, which is one-tenth of that measured in the 1990s. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 72-75 31062242-4 2020 Water dissolved-phase SigmaPCB concentrations ranged from 150 to 170 pg L-1 with a median of 160 pg L-1, which is one-tenth of that measured in the 1990s. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 100-103 31841921-7 2020 For the catchment as a whole, the average nitrate-N concentration (3.6 mg L-1) was slightly higher than the threshold of 2.5 mg L-1 nitrate-N in surface water. Water 153-158 immunoglobulin kappa variable 1-16 Homo sapiens 128-131 31524614-4 2020 The arsenic concentration of the water spring was 1481.9 mug L-1, and as the distance from the water spring increased, the arsenic concentration in the overlying water, pore-water and surface sediments decreased. Water 33-38 immunoglobulin kappa variable 1-16 Homo sapiens 61-64 31492466-6 2019 The method was validated using spiked recoveries (100 ng L-1) from PFAS contaminated surface-water samples with recoveries ranging from 86% to 111% and relative standard deviations below 18%. Water 93-98 immunoglobulin kappa variable 1-16 Homo sapiens 57-60 31369910-4 2019 The mean concentrations of six typical PFAS measured in indoor dust and drinking water are in the range of 15.13-491.07 ng g-1 and 0.31-4.14 ng L-1, respectively. Water 81-86 immunoglobulin kappa variable 1-16 Homo sapiens 144-147 31377929-3 2019 Twenty-six out of thirty-four PPCPs were detected, and the total concentrations of antibiotics ranged from 0.15 to 214.75 ng L-1 in surface water. Water 140-145 immunoglobulin kappa variable 1-16 Homo sapiens 125-128 31352502-9 2019 Method quantification limits were in the range from 1.0 to 33 ng L-1 in wastewater and from 0.5 to 28 ng L-1 in tap water. Water 77-82 immunoglobulin kappa variable 1-16 Homo sapiens 65-68 30968014-4 2019 Results indicate that nitrate can be removed from source waters using FCDI to concentrations <1 mg NO3-N L-1 though a lower quality target such as 10 mg L-1 would be more cost-effective, particularly where the influent nitrate concentration is high (50 mg NO3-N L-1). Water 57-63 immunoglobulin kappa variable 1-16 Homo sapiens 108-111 31390846-7 2019 Experimental results proved that elevated NOM (6.14 mg L-1 as Total Organic Carbon, TOC) in raw water was the root cause for the failure of the plant while the low temperature played a minor but significant role. Water 96-101 immunoglobulin kappa variable 1-16 Homo sapiens 55-58 31185163-5 2019 Moreover, maximum concentrations that leached from enameled glass fragments according to a standard test that simulates water and other liquids percolating through a landfill were about 1200 and 3200 mug L-1 for Pb and Cd, respectively, with several fragments exceeding the U.S. Model Toxins in Packaging Legislation and, therefore, defined as "hazardous". Water 120-125 immunoglobulin kappa variable 1-16 Homo sapiens 204-207 30896927-5 2019 The overall method performance was satisfactory with limits of quantification under 50 ng L-1 for most of analytes in both surface and drinking water. Water 144-149 immunoglobulin kappa variable 1-16 Homo sapiens 90-93 31226391-5 2019 The results indicated that fluoride concentration in drinking water ranged from 0.0 to 5.5 mg L-1 of the study area. Water 62-67 immunoglobulin kappa variable 1-16 Homo sapiens 94-97 31320731-3 2019 We found that the global median Ca concentration was 4.0 mg L-1 with 20.7% of the water samples showing Ca concentrations <= 1.5 mg L-1, a threshold considered critical for the survival of many Ca-demanding organisms. Water 82-87 immunoglobulin kappa variable 1-16 Homo sapiens 60-63 31117244-6 2019 The naked eye detection limit was 10 mug L-1 where the World Health Organization (WHO) have regulated the maximum level of cyanide in drinking water as 70 mug L-1. Water 143-148 immunoglobulin kappa variable 1-16 Homo sapiens 41-44 31117244-6 2019 The naked eye detection limit was 10 mug L-1 where the World Health Organization (WHO) have regulated the maximum level of cyanide in drinking water as 70 mug L-1. Water 143-148 immunoglobulin kappa variable 1-16 Homo sapiens 159-162 30547581-6 2019 The treatment of a 6.7 nM NDMA-spiked surface water sample, under similar operating conditions (liquid residence time of 22 s), achieved 92 to 97% removal with permeate concentrations between 16 and 40 ng L-1. Water 46-51 immunoglobulin kappa variable 1-16 Homo sapiens 205-208 30609490-5 2019 The mean Sb concentration in the wetlands water is 7.03 mug L-1, which consist of pentavalent, trivalent, organic Sb dissolved in water and a great part that attached to suspend solids (SS). Water 42-47 immunoglobulin kappa variable 1-16 Homo sapiens 60-63 30609490-5 2019 The mean Sb concentration in the wetlands water is 7.03 mug L-1, which consist of pentavalent, trivalent, organic Sb dissolved in water and a great part that attached to suspend solids (SS). Water 130-135 immunoglobulin kappa variable 1-16 Homo sapiens 60-63 30366240-4 2019 From August through October, concentrations of dissolved Zn in overlying water (338 ~ 1023 mug L-1) exceeded the water quality limit for fisheries in China (100 mug L-1). Water 73-78 immunoglobulin kappa variable 1-16 Homo sapiens 95-98 30617890-3 2019 Concentrations of the seven target steroid hormones ranged from below the detection limit (ND) to 69.5 ng L-1 in the water of Chaohu Lake and the upstream rivers. Water 117-122 immunoglobulin kappa variable 1-16 Homo sapiens 106-109 31087971-4 2019 Total OPEs (Sigma7OPEs) ranged from 689.09 to 10623.94 ng L-1, with the mean of 3747.58 ng L-1 in the surface water. Water 110-115 immunoglobulin kappa variable 1-16 Homo sapiens 91-94 30248879-6 2018 An initial target of 0.5 mg L-1 free chlorine ensured sufficient suppression of intact cells for up to 14 days (setting the time intervals for system flushes at times of low water usage). Water 174-179 immunoglobulin kappa variable 1-16 Homo sapiens 28-31 30628283-5 2019 When the raw water contained BSA molecules and the coagulant dosage was 0.16 mmol L-1, the flocs formed by PACl with Ca2+ were larger (~50 mum) than the flocs generated by PACl and the settleability also improved. Water 13-18 immunoglobulin kappa variable 1-16 Homo sapiens 82-85 30327111-7 2018 It offers good accuracy when applied to analyze water samples, with relative recoveries ranging from 72 to 130%, for 4-octylphenol and 4-nonylphenol, respectively, and precision varying from 1 to 14.3%, for 4-nonylphenol at 1.0 mug L-1 and bisphenol A at 8.0 mug L-1, respectively. Water 48-53 immunoglobulin kappa variable 1-16 Homo sapiens 232-235 30327111-7 2018 It offers good accuracy when applied to analyze water samples, with relative recoveries ranging from 72 to 130%, for 4-octylphenol and 4-nonylphenol, respectively, and precision varying from 1 to 14.3%, for 4-nonylphenol at 1.0 mug L-1 and bisphenol A at 8.0 mug L-1, respectively. Water 48-53 immunoglobulin kappa variable 1-16 Homo sapiens 263-266 30433769-4 2018 Surface water and atmospheric concentrations were dominated by alpha-HCH (average 250 pg L-1 and 4.2 pg m-3, respectively), followed by HCB (average 17 pg L-1 and 89 pg m-3, respectively). Water 8-13 immunoglobulin kappa variable 1-16 Homo sapiens 89-98 30245272-1 2018 In this work, the capability of the ionic liquid, 1-ethyl-3-methylimidazolium bis(fluorosulfonyl)imide, [C2mim]FSI, to extract o-cresol, 2-chlorophenol, resorcinol and phenol from water, reaching the legal limit of 1 mg L-1 was analyzed. Water 180-185 immunoglobulin kappa variable 1-16 Homo sapiens 220-223 30223332-2 2018 In this paper, the performance of UV/chlorine was compared with that of chlorine and UV to degrade GSM (100 ng L-1) and 2-MIB (100 ng L-1) in water. Water 142-147 immunoglobulin kappa variable 1-16 Homo sapiens 111-114 30317029-7 2018 24-753 mBq L-1 uranium activity concentrations were found in groundwater and surface water showing great areal variability. Water 67-72 immunoglobulin kappa variable 1-16 Homo sapiens 11-14 30172535-4 2018 The use of modified paper filters for fast extraction and enrichment of the target substance from water samples results in a lower limit of detection of 0.19 microg L-1. Water 98-103 immunoglobulin kappa variable 1-16 Homo sapiens 165-168 30628223-11 2018 According to the criteria of the National Standard of Surface Water Quality of China, DEHP and DBP have limiting values of 8 mug L-1 and 3 mug L-1, respectively. Water 62-67 immunoglobulin kappa variable 1-16 Homo sapiens 129-138 30628223-11 2018 According to the criteria of the National Standard of Surface Water Quality of China, DEHP and DBP have limiting values of 8 mug L-1 and 3 mug L-1, respectively. Water 62-67 immunoglobulin kappa variable 1-16 Homo sapiens 129-132 30223332-2 2018 In this paper, the performance of UV/chlorine was compared with that of chlorine and UV to degrade GSM (100 ng L-1) and 2-MIB (100 ng L-1) in water. Water 142-147 immunoglobulin kappa variable 1-16 Homo sapiens 134-137 30119972-12 2018 Under optimum extraction conditions, the method shows low limits of detection in the ranges of 5-10, 8-15 and 32-60 ng L-1 in deionized water, urine, and plasma, respectively. Water 136-141 immunoglobulin kappa variable 1-16 Homo sapiens 119-122 30062348-2 2018 Due to its mobility in the environment it is frequently found in river catchments, often at concentrations exceeding the EU Drinking Water Directive limit of 100 ng L-1 for a single pesticide. Water 133-138 immunoglobulin kappa variable 1-16 Homo sapiens 165-168 29934829-6 2018 Dissolution of calcite from limestone bedrock and a high concentration of bicarbonate ions in natural river water (about 250 mg L-1) enhanced the neutralization of acidic river water and subsequent chemical precipitation of metals and arsenic. Water 108-113 immunoglobulin kappa variable 1-16 Homo sapiens 128-131 29934829-6 2018 Dissolution of calcite from limestone bedrock and a high concentration of bicarbonate ions in natural river water (about 250 mg L-1) enhanced the neutralization of acidic river water and subsequent chemical precipitation of metals and arsenic. Water 177-182 immunoglobulin kappa variable 1-16 Homo sapiens 128-131 30510981-4 2018 Data indicated that average fluoride concentration in drinking water was 0.731 mg L-1. Water 63-68 immunoglobulin kappa variable 1-16 Homo sapiens 82-85 29736649-2 2018 The nitrite and nitrate in drinking water had a concentration range of 0.030-0.113 and 2.41-8.70 mg L-1, with mean values of 0.059 +- 0.014 and 5.25 +- 1.61 mg L-1, respectively. Water 36-41 immunoglobulin kappa variable 1-16 Homo sapiens 100-103 30067237-5 2018 The levels in soil and rock influences the levels in surface and underground water which were between 0.087 and 1.097 mg L-1 for surface water and <0.01-0.46 mg L-1 for underground water, respectively. Water 77-82 immunoglobulin kappa variable 1-16 Homo sapiens 121-124 30067237-5 2018 The levels in soil and rock influences the levels in surface and underground water which were between 0.087 and 1.097 mg L-1 for surface water and <0.01-0.46 mg L-1 for underground water, respectively. Water 77-82 immunoglobulin kappa variable 1-16 Homo sapiens 164-167 30067237-5 2018 The levels in soil and rock influences the levels in surface and underground water which were between 0.087 and 1.097 mg L-1 for surface water and <0.01-0.46 mg L-1 for underground water, respectively. Water 137-142 immunoglobulin kappa variable 1-16 Homo sapiens 121-124 30067237-5 2018 The levels in soil and rock influences the levels in surface and underground water which were between 0.087 and 1.097 mg L-1 for surface water and <0.01-0.46 mg L-1 for underground water, respectively. Water 137-142 immunoglobulin kappa variable 1-16 Homo sapiens 121-124 29554623-3 2018 Standards for drinking water range from 2 to 18 microg L-1 in United States and Europe. Water 23-28 immunoglobulin kappa variable 1-16 Homo sapiens 55-58 29554623-6 2018 As a result of this presence, and the use of Chile saltpeter as a nitrogen fertilizer, perchlorate in Chile has been found at concentrations as high as 1480 microg L-1 in drinking water, 140 microg/kg-1 in fruits, and 30 microg L-1 in wine. Water 180-185 immunoglobulin kappa variable 1-16 Homo sapiens 164-167 29587231-6 2018 Thiamethoxam was detected in one grab sample of raw drinking water at a mean concentration of 0.28 mug L-1, which is above the guidelines for drinking water recommended in some jurisdictions, including the European Union directive on pesticide levels <0.1 mug L-1 in water intended for human consumption. Water 61-66 immunoglobulin kappa variable 1-16 Homo sapiens 103-106 29705649-11 2018 An average recovery of 97.7% and limit of detection of 1-2 mug L-1 were obtained in analyses of surface water. Water 104-109 immunoglobulin kappa variable 1-16 Homo sapiens 63-66 30857104-7 2018 The total concentration in treated drinking water (56-57 ng L-1) was at a similar level as upstream from the WWTP (79-90 ng L-1). Water 44-49 immunoglobulin kappa variable 1-16 Homo sapiens 60-63 29717354-2 2018 The results showed that 10% of the water samples exceeded the limit level of Cd established by World Health Organization (WHO) of 0.003 mg L-1. Water 35-40 immunoglobulin kappa variable 1-16 Homo sapiens 139-142 29529572-5 2018 The 95th percentile concentrations in freshwater were the same in North America and Europe at 0.30 mug L-1 and were 0.024 mug L-1 and 0.15 mug L-1 in marine water, respectively. Water 43-48 immunoglobulin kappa variable 1-16 Homo sapiens 103-106 29529572-5 2018 The 95th percentile concentrations in freshwater were the same in North America and Europe at 0.30 mug L-1 and were 0.024 mug L-1 and 0.15 mug L-1 in marine water, respectively. Water 43-48 immunoglobulin kappa variable 1-16 Homo sapiens 126-129 29529572-5 2018 The 95th percentile concentrations in freshwater were the same in North America and Europe at 0.30 mug L-1 and were 0.024 mug L-1 and 0.15 mug L-1 in marine water, respectively. Water 43-48 immunoglobulin kappa variable 1-16 Homo sapiens 126-129 30966601-6 2018 These hydrogels were proved to absorb water with low salinity from brine solution of 2 g L - 1 NaCl and release the absorbed water at relatively low temperature conditions of 50 C. The fraction of the grafted polyacrylic acid and the comb-chain length were varied to understand their influence on the swelling/deswelling behaviour for these hydrogels. Water 38-43 immunoglobulin kappa variable 1-16 Homo sapiens 89-94 29544216-7 2018 From an ecological point of view, PAHs posed a potential risk to drinking water sources as the concentrations exceeded the guideline value of 0.05 mug L-1. Water 74-79 immunoglobulin kappa variable 1-16 Homo sapiens 151-154 29615320-6 2018 The recoveries of the method for two water samples with spiking levels of 1 and 10 mug L-1 ranged from 83 to 121%. Water 37-42 immunoglobulin kappa variable 1-16 Homo sapiens 87-90 29965512-2 2018 In the natural river areas, the mean value of total nitrogen (TN) concentrations in the sediment pore water was about 15.254 mg L-1, and the total phosphorus (TP) was only 0.654 mg L-1; while in the reservoirs, the mean value of TN and TP were 6.577 mg L-1 and 1.432 mg L-1, respectively. Water 102-107 immunoglobulin kappa variable 1-16 Homo sapiens 129-132 29417482-7 2018 However, addition of 50 mg L-1 fullerene C60 to the wastewater decreased the values for water uptake and nitrogen recovery. Water 57-62 immunoglobulin kappa variable 1-16 Homo sapiens 27-30 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 203-208 immunoglobulin kappa variable 1-16 Homo sapiens 47-50 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 203-208 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 203-208 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 203-208 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 203-208 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 300-305 immunoglobulin kappa variable 1-16 Homo sapiens 47-50 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 300-305 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 300-305 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 300-305 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29557460-6 2018 When the dosage of Mg7Zn1Fe4-Asp-LDH was 0.8 g L-1, the concentration of As(iii) in the aqueous solution could be reduced from 2 mg L-1 to below 10 mug L-1.When Mg-Zn-Fe-Asp-LDH was applied in practical water samples with a dosage of 0.2 g L-1, the residual concentrations of arsenic in three actual water samples were all lower than 10 mug L-1 after adsorption. Water 300-305 immunoglobulin kappa variable 1-16 Homo sapiens 132-135 29527894-5 2018 In inland surface water, the annual average (AA)-EQS of the EU Water Framework Directive of 0.65 ng L-1 for PFOS (linear and branched isomers) was exceeded in 46% of the samples. Water 63-68 immunoglobulin kappa variable 1-16 Homo sapiens 100-103 29527894-6 2018 The drinking water guideline value of 90 ng L-1 for 11PFASs recommended by the Swedish EPA was exceeded in 3% of the water samples from drinking water sources ( n = 169). Water 13-18 immunoglobulin kappa variable 1-16 Homo sapiens 44-47 29527894-6 2018 The drinking water guideline value of 90 ng L-1 for 11PFASs recommended by the Swedish EPA was exceeded in 3% of the water samples from drinking water sources ( n = 169). Water 118-123 immunoglobulin kappa variable 1-16 Homo sapiens 44-47 29615767-6 2018 Such the water soluble graphene can be stored in the form of dispersion (~0.55 g L-1) or filter cake for more than 6 months without the risk of re-stacking. Water 9-14 immunoglobulin kappa variable 1-16 Homo sapiens 81-84 29150771-3 2018 The total concentrations of PFCs (Sigma PFCs) ranged from 0.143 to 1.41 ng L-1 in water samples. Water 82-87 immunoglobulin kappa variable 1-16 Homo sapiens 75-78 29039044-2 2018 The variation of radon concentration in water ranged from 1.44 +- 0.31 to 63.64 +- 2.88 Bq L-1, with a mean value of 28.73 Bq L-1 using RAD7 and 0.64 +- 0.28 to 52.65 +- 2.50 Bq L-1, with a mean value of 20.30 Bq L-1 using Smart RnDuo monitor, respectively. Water 40-45 immunoglobulin kappa variable 1-16 Homo sapiens 91-94 29039044-2 2018 The variation of radon concentration in water ranged from 1.44 +- 0.31 to 63.64 +- 2.88 Bq L-1, with a mean value of 28.73 Bq L-1 using RAD7 and 0.64 +- 0.28 to 52.65 +- 2.50 Bq L-1, with a mean value of 20.30 Bq L-1 using Smart RnDuo monitor, respectively. Water 40-45 immunoglobulin kappa variable 1-16 Homo sapiens 126-129 29039044-2 2018 The variation of radon concentration in water ranged from 1.44 +- 0.31 to 63.64 +- 2.88 Bq L-1, with a mean value of 28.73 Bq L-1 using RAD7 and 0.64 +- 0.28 to 52.65 +- 2.50 Bq L-1, with a mean value of 20.30 Bq L-1 using Smart RnDuo monitor, respectively. Water 40-45 immunoglobulin kappa variable 1-16 Homo sapiens 126-129 29039044-2 2018 The variation of radon concentration in water ranged from 1.44 +- 0.31 to 63.64 +- 2.88 Bq L-1, with a mean value of 28.73 Bq L-1 using RAD7 and 0.64 +- 0.28 to 52.65 +- 2.50 Bq L-1, with a mean value of 20.30 Bq L-1 using Smart RnDuo monitor, respectively. Water 40-45 immunoglobulin kappa variable 1-16 Homo sapiens 126-129 29280103-3 2018 The results indicate that the total PFC concentration in raw water is 261.51 ng L-1 and that perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) are the predominant pollutants. Water 61-66 immunoglobulin kappa variable 1-16 Homo sapiens 80-83 29965455-3 2018 The results show that overlying water and sediment interstitial water rho(TN) ranges from 1.10 to 6.90 mg L-1 and 6.19 to 32.57 mg L-1 respectively; indicating the nitrogen concentrations in the overlying and interstitial water of sediments have a certain variation along the process and vertically. Water 32-37 immunoglobulin kappa variable 1-16 Homo sapiens 106-115 29965455-3 2018 The results show that overlying water and sediment interstitial water rho(TN) ranges from 1.10 to 6.90 mg L-1 and 6.19 to 32.57 mg L-1 respectively; indicating the nitrogen concentrations in the overlying and interstitial water of sediments have a certain variation along the process and vertically. Water 64-69 immunoglobulin kappa variable 1-16 Homo sapiens 106-115 29965455-3 2018 The results show that overlying water and sediment interstitial water rho(TN) ranges from 1.10 to 6.90 mg L-1 and 6.19 to 32.57 mg L-1 respectively; indicating the nitrogen concentrations in the overlying and interstitial water of sediments have a certain variation along the process and vertically. Water 64-69 immunoglobulin kappa variable 1-16 Homo sapiens 106-115 29594488-8 2018 Under optimal conditions, the limits of detection range from 70 to 800 ng L-1, with linear responses from 0.1-500 mug L-1 (water samples), 0.6-500 mug L-1 (spiked urine), and 0.9-500 mug L-1 (spiked plasma). Water 123-128 immunoglobulin kappa variable 1-16 Homo sapiens 74-77 29964827-3 2018 The results showed that 17 VOCs and SVOCs in the surface water samples of 4 monitoring sections were detected, in a concentration range of 0.01-1.21 mug L-1, which is a low pollution level. Water 57-62 immunoglobulin kappa variable 1-16 Homo sapiens 153-156 29239453-5 2018 The experimental results also showed that with the addition of aluminium chloride at 100 mg L-1, the water separation was about 70% after 20 min. Water 101-106 immunoglobulin kappa variable 1-16 Homo sapiens 92-95 29218575-3 2018 The water with NaCl concentration of 66.7 mg L-1 had the highest leaching ability, the hazardous materials were leached after only approximately 50 days (average time, with a standard deviation of 4.1), while less than 100 days were needed in the others. Water 4-9 immunoglobulin kappa variable 1-16 Homo sapiens 45-48 29965675-4 2018 Fortunately, it can meet the water standards by increasing the amount of dosed phosphate to 30 mug L-1 or increasing the height of the filter layer. Water 29-34 immunoglobulin kappa variable 1-16 Homo sapiens 99-102 29145135-6 2018 When the exposition of river water to sunlight was partially limited and kept under the natural day-night cycle, as occurs inside a body of water, tenoxicam, piroxicam and meloxicam (at 2 mug L-1) were detected during a period of 15, 27 and 45 days, respectively. Water 29-34 immunoglobulin kappa variable 1-16 Homo sapiens 192-195 29964561-2 2017 It was found that the levels of THg, dissolved mercury, and particulate mercury in the water ranged from 1.65-9.65, 0.80-3.16, and 0.70-7.81 ng L-1, respectively. Water 87-92 immunoglobulin kappa variable 1-16 Homo sapiens 144-147 29137704-4 2017 The limit of detection ranged from 0.5 ng L-1 to 2 ng L-1 on the basis of 50 mL water sample; the recovery 79.9-119.1%; and the relative standard deviation 0.23%-9.82% (>=5 replicates). Water 80-85 immunoglobulin kappa variable 1-16 Homo sapiens 54-57 29964561-4 2017 The amounts of MeHg, dissolved MeHg, and particulate MeHg in the water samples were 0.05-0.36, 0.02-0.14, and ND-0.26 ng L-1, respectively. Water 65-70 immunoglobulin kappa variable 1-16 Homo sapiens 121-124 29078957-6 2017 The detection limits obtained on xylitol resulted 180 mg L-1 (CV% = 6.9) and 44 mg L-1 (CV% = 6.5) in water and oral fluid, respectively. Water 102-107 immunoglobulin kappa variable 1-16 Homo sapiens 83-86 28929288-6 2017 The concentrations of paper manufacturing chemicals in river water-for example, of the endocrine-disrupting compound bisphenol A (50-8000 ng L-1)-were as high as in pure untreated paper industry wastewaters. Water 61-66 immunoglobulin kappa variable 1-16 Homo sapiens 141-144 28901245-7 2017 Surface water concentrations for PFOS ranged from 16 to 122 ng L-1 and input water concentrations were 132 ng L-1 and 206 ng L-1. Water 8-13 immunoglobulin kappa variable 1-16 Homo sapiens 63-66 28901245-7 2017 Surface water concentrations for PFOS ranged from 16 to 122 ng L-1 and input water concentrations were 132 ng L-1 and 206 ng L-1. Water 77-82 immunoglobulin kappa variable 1-16 Homo sapiens 110-113 28901245-7 2017 Surface water concentrations for PFOS ranged from 16 to 122 ng L-1 and input water concentrations were 132 ng L-1 and 206 ng L-1. Water 77-82 immunoglobulin kappa variable 1-16 Homo sapiens 110-113 28901245-8 2017 Of the eight water samples, seven had water concentrations that exceeded the EPA health advisory level for PFOS of 70 ng L-1. Water 13-18 immunoglobulin kappa variable 1-16 Homo sapiens 121-124 28901245-8 2017 Of the eight water samples, seven had water concentrations that exceeded the EPA health advisory level for PFOS of 70 ng L-1. Water 38-43 immunoglobulin kappa variable 1-16 Homo sapiens 121-124 29036389-4 2017 High radon activity (180 Bq l-1) was also found in thermal potable water in fountains used by the patients and the public. Water 67-72 immunoglobulin kappa variable 1-16 Homo sapiens 28-31 28500355-5 2017 The recoveries are between 84.5%-98.6% with the spiked level of 10 mug L-1 for the real water samples. Water 88-93 immunoglobulin kappa variable 1-16 Homo sapiens 71-74 28734214-4 2017 Mean concentrations of total Hg (THg) and methylmercury (MeHg) in river water in WRB were 3.41 +- 1.98 ng L-1 and 0.15 +- 0.06 ng L-1, respectively. Water 72-77 immunoglobulin kappa variable 1-16 Homo sapiens 106-109 28651318-3 2017 The total concentrations of seven dissolved PAHs in surface water ranged from 1.0 to 5.1 ng L-1, decreasing with increasing latitude. Water 60-65 immunoglobulin kappa variable 1-16 Homo sapiens 92-95 28650623-3 2017 The occurrence of 6DDT (0.10-66 pg L-1) in the surface water was dominated by 4,4"-DDE. Water 56-61 immunoglobulin kappa variable 1-16 Homo sapiens 36-39 28411545-3 2017 With the increase of P content in water from 0.02 mg L-1 to 0.20 and 2.4 mg L-1, consistent release of As from sediments was observed. Water 34-39 immunoglobulin kappa variable 1-16 Homo sapiens 53-56 29964615-11 2017 In the sea area with strong water exchange, concentrations of total n-alkanes were around 2.196 mug L-1, which could be considered as the environmental background level of n-alkanes in Jiaozhou Bay. Water 28-33 immunoglobulin kappa variable 1-16 Homo sapiens 100-103 28334987-6 2017 The method was linear in the concentration range from 5 to 500 mug L-1 for DEET in baby toilet water and good linearity (r2 > 0.9998) was obtained for the calibration curve. Water 95-100 immunoglobulin kappa variable 1-16 Homo sapiens 67-70 28552303-6 2017 The method was successively applied to the determination of pyrethroid pesticides in different kinds of water samples with the limits of detection ranged from 0.16 to 0.21 mug L-1. Water 104-109 immunoglobulin kappa variable 1-16 Homo sapiens 176-179 28292723-4 2017 Water samples taken below an agriculture field in Lower Saxony revealed the permanent entrance of sulfamethazine into groundwater and concentrations up to 100 ng L-1 were determined. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 162-165 28555399-3 2017 The main target values for water parameters are the following: conductivity <10 muScm-1, TOC < 10 mg L-1, and Al < 0.1 mg L-1. Water 27-32 immunoglobulin kappa variable 1-16 Homo sapiens 107-110 28555399-3 2017 The main target values for water parameters are the following: conductivity <10 muScm-1, TOC < 10 mg L-1, and Al < 0.1 mg L-1. Water 27-32 immunoglobulin kappa variable 1-16 Homo sapiens 131-134 27924329-4 2017 The water matrix used was a simulated secondary effluent doped with 200 mug L-1 of the pesticide acetamiprid (ACTM) due to its recalcitrant nature. Water 4-9 immunoglobulin kappa variable 1-16 Homo sapiens 76-79 28357792-4 2017 This protocol was first applied to mineral water spiked by GLY and AMPA at environmental concentration levels (25-750 ng L-1). Water 43-48 immunoglobulin kappa variable 1-16 Homo sapiens 121-124 29965144-3 2017 The result showed concentrations of OCPs in water ranged from 1.89 to 90.19 ng L-1 (mean 30.16 ng L-1), and concentrations of OCPs in sediments varied from 3.10 to 16.02 ng g-1 (average 8.58 ng g-1). Water 44-49 immunoglobulin kappa variable 1-16 Homo sapiens 79-82 27335015-6 2017 Its mass concentrations of 107 to 117 ng L-1 in three tap water samples were the highest of all herbicides measured in the drinking waters. Water 58-63 immunoglobulin kappa variable 1-16 Homo sapiens 41-44 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 immunoglobulin kappa variable 1-16 Homo sapiens 98-101 27883913-5 2017 Underground mine water and leachate contained higher mean concentrations (mug L-1) of Cu (9470), Co (3430) and Ni (590) compared with background concentrations (mug L-1) in un contaminated water of 1.9, 0.21 and 0.67 for Cu, Co and Ni respectively. Water 17-22 immunoglobulin kappa variable 1-16 Homo sapiens 78-81 29744302-3 2017 The reduction of TCE under 90 mA current, 1 mL min-1 flow rate, and 1 mg L-1 initial TCE concentration, was inhibited in the presence of humic acids due to competition for direct electron transfer and/or reaction with atomic hydrogen produced at the cathode surface by water electrolysis. Water 269-274 immunoglobulin kappa variable 1-16 Homo sapiens 73-76 28151443-2 2017 The radon concentrations were in the range of 3.56-98.57, 0.88-25.49, 0.73-1.35 and 0.24-1.03 Bq.L-1 for borehole, well, packaged and utility water, respectively. Water 142-147 immunoglobulin kappa variable 1-16 Homo sapiens 97-100 28219320-3 2017 Although, World Health Organization (WHO) has set the limit of Cd in drinking water is 0.005 mg L-1, the industrial activities release much higher concentrations of metal ions to the water stream than the prescribed limits, which leads to the increasing health hazards and environmental pollution. Water 78-83 immunoglobulin kappa variable 1-16 Homo sapiens 96-99 27916130-3 2017 Under the established conditions, the detection and quantification limits were 0.002 mug L-1 and 0.007 mug L-1 by using 5 mL of waste water and the intra- and inter-day relative standard deviations were less than 10.2% at concentrations of 0.02 and 0.1 mug L-1. Water 134-139 immunoglobulin kappa variable 1-16 Homo sapiens 107-110 27916130-3 2017 Under the established conditions, the detection and quantification limits were 0.002 mug L-1 and 0.007 mug L-1 by using 5 mL of waste water and the intra- and inter-day relative standard deviations were less than 10.2% at concentrations of 0.02 and 0.1 mug L-1. Water 134-139 immunoglobulin kappa variable 1-16 Homo sapiens 107-110 27916130-5 2017 Hydrazine was detected over a concentration range of 0.011-0.074 mug L-1 in 5 of 20 waste water samples. Water 90-95 immunoglobulin kappa variable 1-16 Homo sapiens 69-72 27541153-5 2016 The average concentrations of Cr, Cu, Ni, Pb, and Zn in surface pore water were 18.8, 23.4, 12.0, 13.5, and 42.5 mug L-1, respectively. Water 69-74 immunoglobulin kappa variable 1-16 Homo sapiens 117-120 27649310-6 2016 In fouling experiments using tap water containing 50 mg L-1 alginate, a simple backwash could remove the fouling on Alg L immobilized membrane, but not that on the control membrane. Water 33-38 immunoglobulin kappa variable 1-16 Homo sapiens 56-59 27619495-7 2016 Post-fire water was amenable to conventional treatment at a 10 mg L-1 higher average alum dose than reference samples. Water 10-15 immunoglobulin kappa variable 1-16 Homo sapiens 66-69 27619373-2 2016 Total heavy metal concentrations ranged from 34.88 to 4201.23 mug L-1 in water (as the sum of the water dissolved phase and suspended particulate matter) and from 42.81 to 1686.84 mg kg-1 in sediment samples. Water 73-78 immunoglobulin kappa variable 1-16 Homo sapiens 66-69 29964410-3 2016 The results indicated that the concentration of total PAHs ( PAHs) in the surface water ranged from 17.7-110 ng L-1 with an average value of 42.6 ng L-1. Water 82-87 immunoglobulin kappa variable 1-16 Homo sapiens 112-115 27711833-5 2016 In this experiment, aqueous arsenic in released pore water ranged from 17.5 to 21.3 mug L-1 and the accumulated content of the released arsenic was 17.576 mug during the compaction. Water 53-58 immunoglobulin kappa variable 1-16 Homo sapiens 88-91 28891611-3 2016 The results showed that the IC50 concentration values of water extract, water extract from alcohol precipitation, alcohol extract, and alcohol and water extract were 0.801 4, 0.859 1, 0.796 1, 0.918 0 g L-1; and the alcohol extract is the best method to extract antioxidative components, with the highest antioxidant activity and lowest IC50. Water 57-62 immunoglobulin kappa variable 1-16 Homo sapiens 203-206 30035925-11 2016 Adding PAC(180 mesh) at a dosage of 15 mg L-1 into source water with the concentration of styrene was 0.02 mg L-1, which is the limited value in sanitary standard for drinking water, the concentration could be reduced to 0.001 mg L-1 and the removal rate of styrene was as high as 95.5% . Water 58-63 immunoglobulin kappa variable 1-16 Homo sapiens 42-45 30035925-11 2016 Adding PAC(180 mesh) at a dosage of 15 mg L-1 into source water with the concentration of styrene was 0.02 mg L-1, which is the limited value in sanitary standard for drinking water, the concentration could be reduced to 0.001 mg L-1 and the removal rate of styrene was as high as 95.5% . Water 58-63 immunoglobulin kappa variable 1-16 Homo sapiens 110-113 30035925-11 2016 Adding PAC(180 mesh) at a dosage of 15 mg L-1 into source water with the concentration of styrene was 0.02 mg L-1, which is the limited value in sanitary standard for drinking water, the concentration could be reduced to 0.001 mg L-1 and the removal rate of styrene was as high as 95.5% . Water 58-63 immunoglobulin kappa variable 1-16 Homo sapiens 110-113 28891611-3 2016 The results showed that the IC50 concentration values of water extract, water extract from alcohol precipitation, alcohol extract, and alcohol and water extract were 0.801 4, 0.859 1, 0.796 1, 0.918 0 g L-1; and the alcohol extract is the best method to extract antioxidative components, with the highest antioxidant activity and lowest IC50. Water 72-77 immunoglobulin kappa variable 1-16 Homo sapiens 203-206 28891611-3 2016 The results showed that the IC50 concentration values of water extract, water extract from alcohol precipitation, alcohol extract, and alcohol and water extract were 0.801 4, 0.859 1, 0.796 1, 0.918 0 g L-1; and the alcohol extract is the best method to extract antioxidative components, with the highest antioxidant activity and lowest IC50. Water 72-77 immunoglobulin kappa variable 1-16 Homo sapiens 203-206 26435706-1 2015 Toxic cyanobacteria became more widely recognized as a potential health hazard in the 1990s, and in 1998 the World Health Organization (WHO) first published a provisional Guideline Value of 1 mug L-1 for microcystin-LR in drinking-water. Water 231-236 immunoglobulin kappa variable 1-16 Homo sapiens 196-199 27097089-4 2016 The results of total abundance of microphytobenthos varied from 4.2 x 108 to 2.9 x 109 organisms L-1, total density increased one order of magnitude under the effect of water for both situations of precipitation in the salt flat and in experimental conditions, an increase due to the high abundance of Microcoleus spp. Water 169-174 immunoglobulin kappa variable 1-16 Homo sapiens 97-100 27548955-4 2016 The total dissolved solid (TDS) in the river water ranged from 24.9 to 50.3 mg L-1. Water 45-50 immunoglobulin kappa variable 1-16 Homo sapiens 81-84 27209746-11 2016 The results of nitrate measurements by the field seawater tests in Yantai coast are obtained, which nitrate concentrations are about 0.2 mg L-1 in seawater, and the recoveries of samples for standard recovery tests are in 95%~110%, it shows that this system is accurate, reliability and practicability and could be developed for detected nitrate concentration in natural water. Water 52-57 immunoglobulin kappa variable 1-16 Homo sapiens 142-145 26792954-2 2016 The 238U, 210Po and 210Pb concentrations in analyzed water samples reached maximum values of 11.7 +- 0.3, 2.0 +- 0.1 and 3.2 +- 0.1 mBq L-1 and activity ratios were maximally 1.18 +- 0.01 for 234U/238U, 0.041 +- 0.018 for 235U/238U and 0.69 +- 0.10 for 210Po/210Pb. Water 53-58 immunoglobulin kappa variable 1-16 Homo sapiens 136-139 23818078-13 2014 When arsenic levels in the water were reduced to below 50 mug L(-1) (Indian permissible limit), total arsenic intake and arsenic intake through the water significantly decreased, but arsenic uptake through the diet was found to be not significantly affected. Water 27-32 immunoglobulin kappa variable 1-16 Homo sapiens 62-67 26450514-5 2015 The limits of quantification for both drugs were 5 mug L-1 in water sample and 10 mug L-1 in biological fluids with R2 values higher than 0.993. Water 62-67 immunoglobulin kappa variable 1-16 Homo sapiens 55-58 25633940-3 2015 The PAEs were detected with total concentrations (Sigma6PAEs) ranging from 0.35 to 20.70 mug L-1 in surface water and dry weight ranging from 0.88 to 5.69 mug g-1 in sediments. Water 108-113 immunoglobulin kappa variable 1-16 Homo sapiens 93-96 26060766-11 2014 The relative standard deviation and limit of detection for water samples by introduced selective solid phase extraction were 4.8% and 0.9 mug L-1, and these data for urine samples were 4.5% and 1.60 mug L-1, respectively. Water 59-64 immunoglobulin kappa variable 1-16 Homo sapiens 142-145 24813017-3 2014 The arsenic concentration in drinking water ranged from 12.8 to 132.2 mug l-1. Water 38-43 immunoglobulin kappa variable 1-16 Homo sapiens 74-77 24813017-4 2014 The depth of source of drinking water (10-60 m) was also found with a mean of 36.12 +- 13.61 mug l-1 arsenic concentration. Water 32-37 immunoglobulin kappa variable 1-16 Homo sapiens 97-100 24813017-10 2014 Correlation analysis also showed a significant positive correlation (r = 0.801, t = 5.66, P < 0.05) between age of drinking water sources and their respective arsenic concentration (mug l-1). Water 127-132 immunoglobulin kappa variable 1-16 Homo sapiens 189-192 25098870-4 2014 The reject water total P (TP) content from dewatering biosolids alone (250 mg L-1) was reduced to 60 mg L-1 for a BR = 1.5. Water 11-16 immunoglobulin kappa variable 1-16 Homo sapiens 78-81 25098870-4 2014 The reject water total P (TP) content from dewatering biosolids alone (250 mg L-1) was reduced to 60 mg L-1 for a BR = 1.5. Water 11-16 immunoglobulin kappa variable 1-16 Homo sapiens 104-107 24121432-4 2013 The best conditions were achieved when a PDMS/DVB 65 mum fibre was exposed for 45 min in the headspace of 10 mL water samples at 100 C. Method detection limits were found in the low ng L-1 range between 0.75 and 5 ng L-1 depending on the target analytes. Water 112-117 immunoglobulin kappa variable 1-16 Homo sapiens 186-189 23807682-2 2013 Median drug concentrations were quite similar in the majority of samples, cerca 1 mug L-1 ranging from 0.06 to 2.67 mug L-1 in both water. Water 132-137 immunoglobulin kappa variable 1-16 Homo sapiens 120-123 20615510-6 2010 Water samples collected from the Pearl River were analyzed with the proposed method, the concentrations of NP and OP were found to be 2.40 +- 0.16 mug L-1 and 0.037 +- 0.001 mug L-1, respectively. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 178-181 23523120-6 2013 Water concentrations of PCBs using sediment data was found as between 0.001 and 11.0 ng L-1. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 88-91 22872375-2 2012 Significant highest metal concentration in water (0.45 mg L(-1) Cd and 3.94 mg L(-1) Pb) and sediment (2.83 mg kg(-1) Cd and 6.61 mg kg(-1) Pb) were found at the mouth of the Tigre River, where the fishing town of El Moron is located. Water 43-48 immunoglobulin kappa variable 1-16 Homo sapiens 79-87 22770964-5 2012 At a low Al dosage (2.16 mg L-1), a much higher removal of NOM from synthetic water, as evidenced from UV254 and Dissolved Organic Carbon (DOC) measurements, was achieved by the composite coagulants in comparison to that removed by PACl or PACl and chitosan added separately. Water 78-83 immunoglobulin kappa variable 1-16 Homo sapiens 28-31 22285066-6 2012 Water containing the most elevated concentrations of As are mature Na-Cl fluids with relatively low sulfate content and As concentrations reaching up to 73.6 mg L-1 (Los Humeros geothermal field in Mexico), but more commonly ranging from a few mg L-1 to tens of mg L-1. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 161-164 22285066-6 2012 Water containing the most elevated concentrations of As are mature Na-Cl fluids with relatively low sulfate content and As concentrations reaching up to 73.6 mg L-1 (Los Humeros geothermal field in Mexico), but more commonly ranging from a few mg L-1 to tens of mg L-1. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 247-250 22285066-6 2012 Water containing the most elevated concentrations of As are mature Na-Cl fluids with relatively low sulfate content and As concentrations reaching up to 73.6 mg L-1 (Los Humeros geothermal field in Mexico), but more commonly ranging from a few mg L-1 to tens of mg L-1. Water 0-5 immunoglobulin kappa variable 1-16 Homo sapiens 247-250 21165598-5 2011 The limits of detection for the pesticides in water and sediment were below 0.003 mg L-1 and 0.02 mg kg-1, respectively. Water 46-51 immunoglobulin kappa variable 1-16 Homo sapiens 85-94 23911977-3 2013 Our model system consists of ubiquitin, a protein whose dynamic features are closely related to its ability to bind to multiple partners, in a 325 g L-1 solution of glucose in water, a condition widely employed in in vitro studies of crowding effects. Water 176-181 immunoglobulin kappa variable 1-16 Homo sapiens 149-152 21872331-2 2011 Levels of total HCHs ( HCH) and total DDTs ( DDT) in water detected by GC-ECD ranged from 0.85 to 12.77 ng L-1 and from 3.54 to 33.59 ng L-1, respectively. Water 53-58 immunoglobulin kappa variable 1-16 Homo sapiens 107-110 21088889-3 2011 A quantitative analysis showed the total MC-LR concentrations of water samples ranged from non-detectable to 0.57 mug L-1 among the seven sampling sites. Water 65-70 immunoglobulin kappa variable 1-16 Homo sapiens 118-121 20924919-7 2010 Synthetic drinking water could be treated effectively by the IOCS- and CIM-based filters reducing As to concentrations lower than 10 mu g L-1. Water 19-24 immunoglobulin kappa variable 1-16 Homo sapiens 138-141 19886730-6 2010 In Phase I of the risk assessment, the initial predicted environmental concentration (PEC) of atenolol in surface water (500 ng L-1) exceeded the action limit of 10 ng L-1. Water 114-119 immunoglobulin kappa variable 1-16 Homo sapiens 128-131 11329675-6 2001 Significant DMTS production also occurred with Wanneroo water that contained added omega-thio-containing compounds such as cysteine (1400 ng L-1 DMTS), and 3-mercaptopropionate (210 ng L-1). Water 56-61 immunoglobulin kappa variable 1-16 Homo sapiens 141-144 17582460-0 2007 Determination of benzene, toluene, ethylbenzene, xylenes in water at sub-ng l-1 levels by solid-phase microextraction coupled to cryo-trap gas chromatography-mass spectrometry. Water 60-65 immunoglobulin kappa variable 1-16 Homo sapiens 76-79 11329675-6 2001 Significant DMTS production also occurred with Wanneroo water that contained added omega-thio-containing compounds such as cysteine (1400 ng L-1 DMTS), and 3-mercaptopropionate (210 ng L-1). Water 56-61 immunoglobulin kappa variable 1-16 Homo sapiens 185-188 1735647-3 1992 Results showed a uranium concentration in drinking water of 0.67-20.26 micrograms L-1. Water 51-56 immunoglobulin kappa variable 1-16 Homo sapiens 82-85 10063642-1 1999 Helicobacter pylori NCTC 11637 produces a water-insoluble biofilm when grown under defined conditions with a high carbon:nitrogen ratio in continuous culture and in 10% strength Brucella broth supplemented with 3 g l-1 glucose. Water 42-47 immunoglobulin kappa variable 1-16 Homo sapiens 215-218 8887526-1 1996 A lower limit of detection of 0.04 Bq L-1 for measuring 131I in milk or water with a gamma-ray spectrometer was achieved with a large 118% intrinsic germanium detector. Water 72-77 immunoglobulin kappa variable 1-16 Homo sapiens 38-41 7883561-2 1995 The mean 3H concentration was found to be 1.4 +/- 0.4 Bq L-1 and 1.0 +/- 0.4 Bq L-1 (combustion water) for free water 3H and organically-bound 3H, respectively, excluding the abnormally high data of one city. Water 96-101 immunoglobulin kappa variable 1-16 Homo sapiens 57-68 7883561-2 1995 The mean 3H concentration was found to be 1.4 +/- 0.4 Bq L-1 and 1.0 +/- 0.4 Bq L-1 (combustion water) for free water 3H and organically-bound 3H, respectively, excluding the abnormally high data of one city. Water 112-117 immunoglobulin kappa variable 1-16 Homo sapiens 57-68 8244709-4 1993 For tritium-in-water analysis, commercial low-level liquid scintillation spectrometers capable of detecting tritium-in-water concentrations as low as 0.65 Bq L-1 for counting times of 500 min are available. Water 119-124 immunoglobulin kappa variable 1-16 Homo sapiens 158-161