PMID-sentid Pub_year Sent_text comp_official_name comp_offsetprotein_name organism prot_offset 3403426-2 1988 A positive balance of Na was also observed in the 0.45 (approximately 250%) and 2.0% NaCl groups (300%), whereas the 0.2% NaCl group regained lost water and Na simultaneously at 10 h. With tap water, additional loss of cations was observed. Water 193-198 nuclear RNA export factor 1 Rattus norvegicus 189-192 34779863-3 2021 In the present study, male Sprague-Dawley rats were treated with PM2.5 suspension for 12 weeks and/or fed with tap water containing an antioxidant tempol. Water 115-120 nuclear RNA export factor 1 Rattus norvegicus 111-114 3202189-5 1988 Control animals were given vehicle (0.9% NaCl) by osmotic minipump and they drank tap water. Water 86-91 nuclear RNA export factor 1 Rattus norvegicus 82-85 2542996-11 1989 However, rats treated with desipramine were less active than those treated with tap water or ethanol. Water 84-89 nuclear RNA export factor 1 Rattus norvegicus 80-83 3207390-2 1988 The present study was undertaken to examine early changes in vascular ultrastructure of rats receiving tap water supplemented with either calcium chloride or a relatively low dosage of irradiated ergocalciferol ad libitum for 21 days. Water 107-112 nuclear RNA export factor 1 Rattus norvegicus 103-106 2853079-1 1988 Long term administration of thioacetamide (0.03% in tap water) results in a characteristic lesion in rat liver, which corresponds to cirrhosis-like patterns of micronodular cirrhosis type after treatment over 3 months. Water 56-61 nuclear RNA export factor 1 Rattus norvegicus 52-55 3319899-7 1987 for 2 weeks lowered tail-cuff pressure significantly (175 +/- 3 and 166 +/- 3 mm Hg, respectively; p less than 0.01) while rats drank tap water. Water 138-143 nuclear RNA export factor 1 Rattus norvegicus 134-137 3017491-7 1986 Adenosine 30 microM added to the superfusion fluid decreased electrically stimulated ACh release both in rats drinking tap water and rats drinking caffeine. Water 123-128 nuclear RNA export factor 1 Rattus norvegicus 119-122 3575881-3 1987 Male Wistar rats (n = 192) were divided into eight groups and they were fed either a mixture of water and 15% (v/v) ethanol or tap water combined with standard or special diets for 12 weeks. Water 131-136 nuclear RNA export factor 1 Rattus norvegicus 127-130 2450232-6 1987 Long-term enalapril prolonged survival (p = 0.014) with a median 50% survival of 164 (164-165) days, compared to 84 (64-104) days in rats receiving tap water. Water 152-157 nuclear RNA export factor 1 Rattus norvegicus 148-151 3017491-8 1986 In rats drinking tap water, caffeine added to the superfusion fluid at a concentration of 50 microM enhanced ACh release, while at 0.5 mM it decreased ACh output from the slices. Water 21-26 nuclear RNA export factor 1 Rattus norvegicus 17-20 3749229-6 1986 Rats down-shifted from a 32% to 4% sucrose solution generated response profiles more similar to rats shifted to plain tap water than rats maintained on a 32% sucrose solution and administered PIM. Water 122-127 nuclear RNA export factor 1 Rattus norvegicus 118-121 3774909-3 1986 In the first experiment, sham-operated and adrenal demedullated rats were provided with 1.5% NaCl or tap water for drinking for 5 days. Water 105-110 nuclear RNA export factor 1 Rattus norvegicus 101-104 3639155-2 1986 The rats were housed in individual metabolic cages and were allowed free access to food having normal sodium content and to tap water. Water 128-133 nuclear RNA export factor 1 Rattus norvegicus 124-127 6888193-7 1983 Spontaneous locomotor of the chronic caffeine group was reduced significantly for 4 days after drug-free tap water was substituted for the caffeine solution. Water 109-114 nuclear RNA export factor 1 Rattus norvegicus 105-108 3938241-2 1985 The rats were placed into individual metabolic cages and allowed free access to food having normal sodium content and to tap water. Water 125-130 nuclear RNA export factor 1 Rattus norvegicus 121-124 3989425-7 1985 Hypo-osmotic stimulation, induced by an intragastric injection of 10 ml tap water, reduced the discharge rate of each of four neurones from DI rats by 50% or more. Water 76-81 nuclear RNA export factor 1 Rattus norvegicus 72-75 24896988-2 1985 The rats were then tested for the aversion of tap water in compound with the illness-paired odor offered together with an alternative new odor not paired with toxicosis. Water 50-55 nuclear RNA export factor 1 Rattus norvegicus 46-49 6463044-4 1984 on Purina laboratory rat chow and tap water. Water 38-43 nuclear RNA export factor 1 Rattus norvegicus 34-37 4026920-1 1985 Female albino rats were treated with sodium salicylate dissolved in tap water orally by intubation. Water 72-77 nuclear RNA export factor 1 Rattus norvegicus 68-71 4075543-3 1985 Fluid consumption in animals drinking tap water was constant at between 35-40 ml/day throughout the six-month study period. Water 42-47 nuclear RNA export factor 1 Rattus norvegicus 38-41 6865335-3 1983 After uninephrectomy of rats on a normal diet with tap water, the maximal increase in relative weight of the remaining kidney occurred within 2 weeks, and the degree of hypertrophy was estimated as 64%. Water 55-60 nuclear RNA export factor 1 Rattus norvegicus 51-54 6873379-1 1983 Injections of 0.2 M LiCl i. p. (1 ml/100 g/day) induced polydipsia in rats drinking tap water. Water 88-93 nuclear RNA export factor 1 Rattus norvegicus 84-87 6873379-2 1983 The plasma lithium concentration and its content in the erythrocytes, skeletal muscles, renal tissue were significantly higher in the rats drinking tap water as compared with rats drinking saline. Water 152-157 nuclear RNA export factor 1 Rattus norvegicus 148-151 6873379-4 1983 Na content in the plasma and the renal cortex--medullar Na gradient were decreased in the "lithium" rats drinking tap water. Water 118-123 nuclear RNA export factor 1 Rattus norvegicus 114-117 6829795-4 1983 Slowly most of the KAL rats began to eat chow and drink tap water but remained hypophagic and hypodipsic. Water 60-65 nuclear RNA export factor 1 Rattus norvegicus 56-59 6829795-6 1983 During water deprivation the recovered KAL rats that would drink tap water ate, and following it they responded with an adequate increase in water consumption. Water 7-12 nuclear RNA export factor 1 Rattus norvegicus 65-68 6829795-6 1983 During water deprivation the recovered KAL rats that would drink tap water ate, and following it they responded with an adequate increase in water consumption. Water 69-74 nuclear RNA export factor 1 Rattus norvegicus 65-68 6829795-6 1983 During water deprivation the recovered KAL rats that would drink tap water ate, and following it they responded with an adequate increase in water consumption. Water 69-74 nuclear RNA export factor 1 Rattus norvegicus 65-68 7018268-6 1981 Conversely, 6- or 48-h access to tap water did not increase RCRC of previously Na-loaded rats, but did increase severity of ARF. Water 37-42 nuclear RNA export factor 1 Rattus norvegicus 33-36 6124483-3 1982 Controls drank tap water. Water 19-24 nuclear RNA export factor 1 Rattus norvegicus 15-18 7096899-3 1982 Ten rats from each group were killed at this time and the remaining animals were fed tap water for a further 90 days before they were sacrificed. Water 89-94 nuclear RNA export factor 1 Rattus norvegicus 85-88 7316567-5 1981 day) and diatomaceous earth; a control group drank fiber-free well water or filtered city tap water. Water 94-99 nuclear RNA export factor 1 Rattus norvegicus 90-93 6818357-4 1982 In rats pretreated with phenobarbital (0.05%), Zn (10 mg/l) and Cu (10 mg/l) in tap water and cysteine (200 mg/kg s.c.), fetal toxicity of ASA was reduced, whereas it was enhanced in rats pretreated with SKF-525A (200 mg/kg s.c.) and alpha-naphthyl acetic acid (200 mg/kg p.o.) Water 84-89 nuclear RNA export factor 1 Rattus norvegicus 80-83 7029856-1 1981 Previous studies have demonstrated that after intravesical inoculation of Escherichia coli, rats drinking 5% glucose-water remained bacteriuric for up to 21 days while rats drinking tap water became abacteriuric within a few days. Water 186-191 nuclear RNA export factor 1 Rattus norvegicus 182-185 7071085-6 1982 Animals treated with cocaine had lower preference ratios than saline controls although both groups consumed more novel fluid than tap water. Water 134-139 nuclear RNA export factor 1 Rattus norvegicus 130-133 6266956-3 1981 In the rats drinking tap water, systolic pressure gradually increased over a period of several weeks and then was sustained in a dose-related manner for the duration of the treatment. Water 25-30 nuclear RNA export factor 1 Rattus norvegicus 21-24 7029856-4 1981 Of rats drinking tap water, 6 of 7 (85%) with intrapelvic bladders and 8 of 9 (89%) with ventral hernias had less than 10 colony forming units per ml of urine within 9 days of inoculation. Water 21-26 nuclear RNA export factor 1 Rattus norvegicus 17-20 6769337-4 1980 Tap water alone also induced a transient elevation in insulinemia but was much smaller than the saccharin-induced response. Water 4-9 nuclear RNA export factor 1 Rattus norvegicus 0-3 6256110-10 1980 Unlike the normotensive rats, which did not show a relationship between beta-adrenoreceptor number and blood pressure, spontaneously hypertensive rats on tap water and 1% NaCl showed a significant negative logarithmic relationship between these two variables. Water 158-163 nuclear RNA export factor 1 Rattus norvegicus 154-157 7393974-3 1980 Exposure to the CS+ stimulated more drinking than comparable exposure to tap water following 2-8 differential conditioning trials (Experiment 1), following conditioning with lithium doses of 0.75-3.0 mEq/kg (Experiment 2), and in comparison with both exposure to water and exposure to the CS- (Experiment 3). Water 77-82 nuclear RNA export factor 1 Rattus norvegicus 73-76 7365004-1 1980 The results of three experiments indicated that male hooded rats exhibit marked corticosterone elevations when they freely consume .740 mol/l (23.2% w/w) sucrose in tap water while nondeprived or .298 mol/l (9.8% w/w) sucrose when deprived of water for 36 hr. Water 169-174 nuclear RNA export factor 1 Rattus norvegicus 165-168 7365004-3 1980 Free ingestion of tap water following sucrose consumption accelerated the decline from peak level of corticosterone during the period 60-120 min following the onset of sucrose consumption. Water 22-27 nuclear RNA export factor 1 Rattus norvegicus 18-21 750489-2 1978 Twenty-four hour water deprived rats were habituated for two consecutive days to drinking tap water in the drinking box for 15 minutes daily. Water 94-99 nuclear RNA export factor 1 Rattus norvegicus 90-93 667487-3 1978 Treated animals gained weight more slowly and consumed less food and water than control rats that drank tap water. Water 108-113 nuclear RNA export factor 1 Rattus norvegicus 104-107 6769337-5 1980 In streptozotocin diabetic rats bearing intrahepatic, presumably denervated islet isografts, these rapid insulin responses to oral saccharin and tap water stimulation were completely abolished, whereas the early insulin response to intravenous glucose was decreased by only about 30%. Water 149-154 nuclear RNA export factor 1 Rattus norvegicus 145-148 752211-1 1978 In preliminary experiments it had been shown that the total catecholamines in the urine of rats collected during 5 hrs after stimulation of diuresis with 50 ml tap water/kg body weight per os were not changed significantly following a 3-week training in individual metabolic cages, a short pressing of the animals against the laboratory table, a single i. p. injection of 2 ml sodium chloride solution (145 mmol/l)/kg body weight, or a single s. c. injection of 40 ml air per animal. Water 164-169 nuclear RNA export factor 1 Rattus norvegicus 160-163 915435-2 1977 Subjects infused with either the D solution or tap water immediately before backward conditioning learned weaker saccharin aversions than animals infused with the ND solution and animals given no infusion at this time (Experiments 1 and 3). Water 51-56 nuclear RNA export factor 1 Rattus norvegicus 47-50 875472-2 1977 The rats were on a regular rat chow diet (0.45% sodium content) and tap water and were not hypertensive at the time of the study. Water 72-77 nuclear RNA export factor 1 Rattus norvegicus 68-71 1086619-7 1976 Application of tap water containing 2% NaCl led to a marked decrease in the amount of "classical" NSM but did only slightly impair the amount of CRF-granules. Water 19-24 nuclear RNA export factor 1 Rattus norvegicus 15-18 990906-5 1976 Chocolate milk is consumed but tap water is actively rejected. Water 35-40 nuclear RNA export factor 1 Rattus norvegicus 31-34 990906-7 1976 The results support the conclusion that rats with LH lesions require an arousing stimulus for feeding but that the same externally applied arousing stimulus enhances active rejection of tap water. Water 190-195 nuclear RNA export factor 1 Rattus norvegicus 186-189 1185597-4 1975 The highest average dose of morphine HCl consumed in tap water was 30 mg/kg within an hour session. Water 57-62 nuclear RNA export factor 1 Rattus norvegicus 53-56 31212064-6 2019 In contrast, dosing the antioxidants in the tap water (i.e., before the heat exposure and rehydration with fructose) preserved renal function, prevented renal tubule dysfunction and avoided the increase in systemic blood pressure. Water 48-53 nuclear RNA export factor 1 Rattus norvegicus 44-47 180760-1 1975 Male albino rats were deprived of water for 6 days, then they were allowed to drink tap water ad libitim. Water 88-93 nuclear RNA export factor 1 Rattus norvegicus 84-87 4412581-0 1974 Conditioned flavor aversions to familiar tap water in rats: an adjustment with implications for aversion therapy treatment of alcoholism and obesity. Water 45-50 nuclear RNA export factor 1 Rattus norvegicus 41-44 4902827-5 1970 However, when rats were fed the same solution of ammonium chloride but were allowed access to tap water ad lib., urinary osmolality values were comparable to those observed in normal animals, and susceptibility to pyelonephritis was reduced or eliminated despite a degree of systemic acidosis similar to that observed in rats fed ammonium chloride solution without access to tap water. Water 98-103 nuclear RNA export factor 1 Rattus norvegicus 94-97 14405109-1 1960 Local licking rates of eight albino rats, when the rats were given tap water at the end of a short runway after 23 hours of water deprivation, averaged a little over seven licks per second. Water 71-76 nuclear RNA export factor 1 Rattus norvegicus 67-70 33028492-5 2020 In vivo, the absorption of erlotinib administered in tap water was decreased in omeprazole-treated (OP) rats, used as a model of gastric acid suppression, compared to control rats. Water 57-62 nuclear RNA export factor 1 Rattus norvegicus 53-56 1152298-1 1975 Kidney extract from rats which were adrenalectomized and given tap water was dialyzed, salted out, ultrafiltrated or heated. Water 67-72 nuclear RNA export factor 1 Rattus norvegicus 63-66 32294645-3 2020 METHODS: Sprague-Dawley rats were offered 20% fructose solution or tap water for 2 weeks, after which vascular reactivity was measured in isolated aortic rings. Water 71-76 nuclear RNA export factor 1 Rattus norvegicus 67-70 28228348-9 2017 Moreover, an increase in liver lipid accumulation of rats treated with gaseous drinks is shown opposed to control rats treated with degassed beverage or tap water. Water 157-162 nuclear RNA export factor 1 Rattus norvegicus 153-156 32189984-3 2019 In acute toxicity test, 4 groups of rats (n = 6/group: 3 males and 3 females) were chosen and the first control group received tap water, while the other three groups received Av seed ethanolic extract dissolved in tap water at doses of 150, 300, and 600 mg/kg, and general behavior, adverse effects, and mortality were recorded for up to 14 days. Water 219-224 nuclear RNA export factor 1 Rattus norvegicus 215-218 29376971-0 2017 [One-time effects of drinking mineral water and tap water enriched with silver nanoparticles on the biochemical markers of liver condition and metabolic parameters in healthy rats]. Water 52-57 nuclear RNA export factor 1 Rattus norvegicus 48-51 29376971-1 2017 AIM: The objective of the present research was to study the influence of tap water enriched with silver nanoparticles (NP) as well as that of <<Krasnoarmeysky>> and <<Essentuki No17>> mineral waters after their single administration through the oral gavage to the rats on the metabolism of carbohydrates and lipids, the biochemical markers of the liver condition, and the endocrine profile in the healthy animals. Water 78-83 nuclear RNA export factor 1 Rattus norvegicus 74-77 29376971-3 2017 RESULTS: The study has demonstrated that the tap water enriched with silver nanoparticles similar to the mineral waters caused stress reactions that are inferior to those induced by <<Essentuki No17>> mineral water in terms of the magnitude; however, the effect provoked by the tap water was of longer duration. Water 50-55 nuclear RNA export factor 1 Rattus norvegicus 46-49 29376971-3 2017 RESULTS: The study has demonstrated that the tap water enriched with silver nanoparticles similar to the mineral waters caused stress reactions that are inferior to those induced by <<Essentuki No17>> mineral water in terms of the magnitude; however, the effect provoked by the tap water was of longer duration. Water 50-55 nuclear RNA export factor 1 Rattus norvegicus 291-294 29376971-4 2017 Moreover, the tap water enriched with silver nanoparticles stimulates prooxidant reactions, and inhibit the activity of antioxidant protection. Water 18-23 nuclear RNA export factor 1 Rattus norvegicus 14-17 29376971-6 2017 CONCLUSION: The silver nanoparticles present in the tap water have a significant biological potential of their own. Water 57-62 nuclear RNA export factor 1 Rattus norvegicus 53-56 29376971-8 2017 The single intake of the tap water enriched with silver nanoparticles by the healthy laboratory animals produces the response that resembles that of the drinking mineral water. Water 29-34 nuclear RNA export factor 1 Rattus norvegicus 25-28 29376971-8 2017 The single intake of the tap water enriched with silver nanoparticles by the healthy laboratory animals produces the response that resembles that of the drinking mineral water. Water 170-175 nuclear RNA export factor 1 Rattus norvegicus 25-28 29165388-2 2017 Male Sprague-Dawley rats had free access to a drinking solution containing 10% d-glucose or tap water for 12 weeks. Water 96-101 nuclear RNA export factor 1 Rattus norvegicus 92-95 28361577-2 2017 Rats were fed ad libitum with normal tap water or tap water with extract of N. sativa seed, Ramaria condensata, Lactarius salmonicolor, Lactarius piperatus, and Tricholoma terreum for 3 days. Water 54-59 nuclear RNA export factor 1 Rattus norvegicus 50-53 26892488-2 2016 Hypothyroidism was induced in young-adult rats by the administration of 6-n-propyl-2-thiouracil (PTU) in tap water for 21 days. Water 109-114 nuclear RNA export factor 1 Rattus norvegicus 105-108 27061931-6 2016 Following exposure of rats to a concentration of a pharmaceutical which was 10 times higher than the concentration known to be present in tap water, trace levels of some pharmaceuticals and their metabolites were detected in biological samples. Water 142-147 nuclear RNA export factor 1 Rattus norvegicus 138-141 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 26022140-5 2015 Male Fischer 344 rats were randomly assigned into 4 groups: young rats (3 months old) provided with tap water or with 15 g/L GP dissolved in tap water for 3 weeks, aged rats (21 months old) provided with tap water or with GP-treated tap water for 3 weeks (AG-GP). Water 145-150 nuclear RNA export factor 1 Rattus norvegicus 141-144 25803851-12 2015 Drinking tap water, which contains adequate minerals, was found to be better for bone health. Water 13-18 nuclear RNA export factor 1 Rattus norvegicus 9-12 25539033-3 2015 The first group served as a control and was provided tap water. Water 57-62 nuclear RNA export factor 1 Rattus norvegicus 53-56 26685510-8 2015 In rats receiving tap water, PBG produced bradycardia, hypotension and tachypnoea. Water 22-27 nuclear RNA export factor 1 Rattus norvegicus 18-21 25323423-3 2015 Control rat dams consumed tap water without added Mn. Water 30-35 nuclear RNA export factor 1 Rattus norvegicus 26-29 25051748-8 2014 In the experimental study of the effect of water with different content of LCA on heart rate and cardiac output of the frog it was found that the optimum level of structuredness of water is within the range of 5.06 +/- 0.09% (in water "Lekor") - 6.9 +/- 0.23% (tap water treated with Bioptron). Water 181-186 nuclear RNA export factor 1 Rattus norvegicus 261-264 25560240-6 2014 Over a seven-week period, animals had access to one of the following three drinking solutions: 1) tap water (control group; TW), 2) tap water with added Na(+) (to make the same concentration as in the MW group (TWNaCl group), or 3) natural mineral-rich water [Pedras Salgadas( ), which is very rich in bicarbonate, and with higher sodium, calcium and magnesium content than control tap water (MW group)]. Water 136-141 nuclear RNA export factor 1 Rattus norvegicus 132-135 25560240-6 2014 Over a seven-week period, animals had access to one of the following three drinking solutions: 1) tap water (control group; TW), 2) tap water with added Na(+) (to make the same concentration as in the MW group (TWNaCl group), or 3) natural mineral-rich water [Pedras Salgadas( ), which is very rich in bicarbonate, and with higher sodium, calcium and magnesium content than control tap water (MW group)]. Water 136-141 nuclear RNA export factor 1 Rattus norvegicus 132-135 25560240-6 2014 Over a seven-week period, animals had access to one of the following three drinking solutions: 1) tap water (control group; TW), 2) tap water with added Na(+) (to make the same concentration as in the MW group (TWNaCl group), or 3) natural mineral-rich water [Pedras Salgadas( ), which is very rich in bicarbonate, and with higher sodium, calcium and magnesium content than control tap water (MW group)]. Water 136-141 nuclear RNA export factor 1 Rattus norvegicus 132-135 25560240-6 2014 Over a seven-week period, animals had access to one of the following three drinking solutions: 1) tap water (control group; TW), 2) tap water with added Na(+) (to make the same concentration as in the MW group (TWNaCl group), or 3) natural mineral-rich water [Pedras Salgadas( ), which is very rich in bicarbonate, and with higher sodium, calcium and magnesium content than control tap water (MW group)]. Water 136-141 nuclear RNA export factor 1 Rattus norvegicus 132-135 25560240-6 2014 Over a seven-week period, animals had access to one of the following three drinking solutions: 1) tap water (control group; TW), 2) tap water with added Na(+) (to make the same concentration as in the MW group (TWNaCl group), or 3) natural mineral-rich water [Pedras Salgadas( ), which is very rich in bicarbonate, and with higher sodium, calcium and magnesium content than control tap water (MW group)]. Water 136-141 nuclear RNA export factor 1 Rattus norvegicus 132-135 25560240-6 2014 Over a seven-week period, animals had access to one of the following three drinking solutions: 1) tap water (control group; TW), 2) tap water with added Na(+) (to make the same concentration as in the MW group (TWNaCl group), or 3) natural mineral-rich water [Pedras Salgadas( ), which is very rich in bicarbonate, and with higher sodium, calcium and magnesium content than control tap water (MW group)]. Water 136-141 nuclear RNA export factor 1 Rattus norvegicus 132-135 25051748-8 2014 In the experimental study of the effect of water with different content of LCA on heart rate and cardiac output of the frog it was found that the optimum level of structuredness of water is within the range of 5.06 +/- 0.09% (in water "Lekor") - 6.9 +/- 0.23% (tap water treated with Bioptron). Water 181-186 nuclear RNA export factor 1 Rattus norvegicus 261-264 25051748-8 2014 In the experimental study of the effect of water with different content of LCA on heart rate and cardiac output of the frog it was found that the optimum level of structuredness of water is within the range of 5.06 +/- 0.09% (in water "Lekor") - 6.9 +/- 0.23% (tap water treated with Bioptron). Water 181-186 nuclear RNA export factor 1 Rattus norvegicus 261-264 24114638-5 2013 One group received fructose (10%) in tap water for six weeks and the other one received tap water without fructose. Water 92-97 nuclear RNA export factor 1 Rattus norvegicus 88-91 23596160-3 2013 Four groups of rats were used: 1) control (C; injected with vehicle and provided with tap water), 2) grape powder-treated (GP; injected with vehicle and provided for 3 wk with 15 g/L grape powder dissolved in tap water), 3) BSO-treated [injected with BSO (300 mg/kg body weight), i.p. Water 213-218 nuclear RNA export factor 1 Rattus norvegicus 209-212 24749281-2 2014 As the solvent to obtain a working solution there was used distilled water solutions of different conccentrations were obtained on the base of Moscow tap water cleaned out by a charcoal filter. Water 154-159 nuclear RNA export factor 1 Rattus norvegicus 150-153 23466145-2 2013 Tap water samples were monthly collected from the three sampling sites with different distances of distribution network from the plant during April 2010-March 2011: Min (less than 0.1km), Mid (approximately 4km) and Max (approximately 8km). Water 4-9 nuclear RNA export factor 1 Rattus norvegicus 0-3 23466145-4 2013 Pro-estrogenic and estrogenic activity in tap water ranged from 151.4 to 1395.6pg EEQ/L and 35.2 to 1511pg EEQ/L, respectively. Water 46-51 nuclear RNA export factor 1 Rattus norvegicus 42-45 20834182-3 2010 Tap water was given to the control group. Water 4-9 nuclear RNA export factor 1 Rattus norvegicus 0-3 22890080-7 2012 At the end of this period, tap water was added as an option for drinking liquid (voluntary alcohol ingestion) for another 10 days. Water 31-36 nuclear RNA export factor 1 Rattus norvegicus 27-30 21822760-6 2012 Control rats consumed tap water. Water 26-31 nuclear RNA export factor 1 Rattus norvegicus 22-25 22063564-10 2011 A total of 6 samples of urine and 12 samples of brain from control rats and another 6 samples of urine and 12 samples of brain from rats fed with tap water rich in lead acetate were used in this research. Water 150-155 nuclear RNA export factor 1 Rattus norvegicus 146-149 20369314-5 2011 Control rats consumed tap water. Water 26-31 nuclear RNA export factor 1 Rattus norvegicus 22-25 21532276-10 2011 Cumulative urinary excretion recoveries with tap water, evian( ) and 100% deep ocean water were 0.98+-0.17%, 0.80+-0.18% and 1.01+-0.16% (mean+-S.E., n=4). Water 49-54 nuclear RNA export factor 1 Rattus norvegicus 45-48 25874708-1 2012 UNLABELLED: The aim of this study was to investigate the influence of tap water on microbial colonization of skin wounds in rats. Water 75-80 nuclear RNA export factor 1 Rattus norvegicus 71-74 25587250-4 2011 The experimental groups after pregnancy received an oral dose of 0.05 mg/ml of morphine by tap water while the control group received only tap water. Water 95-100 nuclear RNA export factor 1 Rattus norvegicus 91-94 21423434-5 2010 Wistar rats were trained to self-administer tap water or ACD by nose-poking in daily 30 min sessions for 15 consecutive days. Water 48-53 nuclear RNA export factor 1 Rattus norvegicus 44-47 21423434-6 2010 Response on active nose-poke caused delivery of ACD solution or tap water, whereas responses on inactive nose-poke had no consequences. Water 68-73 nuclear RNA export factor 1 Rattus norvegicus 64-67 19921479-4 2010 In vivo, taurine were administered to male rats by tap water. Water 55-60 nuclear RNA export factor 1 Rattus norvegicus 51-54 19356308-7 2009 Between exposure and re-exposure, rats drank tap water for 4 days. Water 49-54 nuclear RNA export factor 1 Rattus norvegicus 45-48 20107868-8 2010 The results are compatible with the view that a low amount of Cd given in tap water brought about significant changes in circadian expression of redox enzyme and clock genes in rat MBH. Water 78-83 nuclear RNA export factor 1 Rattus norvegicus 74-77 19966145-0 2009 Chronic exposure to arsenic in tap water reduces acetylcholine-induced relaxation in the aorta and increases oxidative stress in female rats. Water 35-40 nuclear RNA export factor 1 Rattus norvegicus 31-34 19966145-1 2009 The aim of this work is to determine whether consuming tap water containing arsenic (20 microg/L) alters oxidative stress levels in female rats and changes vascular response. Water 59-64 nuclear RNA export factor 1 Rattus norvegicus 55-58 19906108-5 2009 Starting from week 21 all the rats were fed with normal rat chow and tap water. Water 73-78 nuclear RNA export factor 1 Rattus norvegicus 69-72 19216812-3 2009 Hypertriacylglycerolaemia was induced in male Sprague-Dawley rats (ten rats per group) by supplementing tap water with 10 % fructose. Water 108-113 nuclear RNA export factor 1 Rattus norvegicus 104-107 19201744-4 2009 The hindlimb unloaded rats maintained on tap water had significantly elevated MDA levels in 7 tissues (brain, lung, pancreas, kidney, intestine, heart, liver) when compared to the paired hindlimb loaded controls (p <0.05). Water 45-50 nuclear RNA export factor 1 Rattus norvegicus 41-44 18243045-5 2008 Experiment 2 was performed to investigate the effects of KBrO3 at the 0.002 ppm dose approximately contained in the tap water on rat kidneys. Water 120-125 nuclear RNA export factor 1 Rattus norvegicus 116-119 19035047-5 2008 RESULTS: Under the same lead exposure, no significant differences were observed in blood lead, however, brain lead level showed higher in drinking purified water group than that in tap water group. Water 185-190 nuclear RNA export factor 1 Rattus norvegicus 181-184 19035047-6 2008 Expression of NR1, NR2A and NR2B in hippocampus of the rats drinking purified water was lower than those drinking tap water, especially at low lead exposure (50 mg/L) (P < 0.05). Water 118-123 nuclear RNA export factor 1 Rattus norvegicus 114-117 17720948-2 2007 Experimental hypothyroidism was induced in weanling rats by exposing their mothers to propylthiouracil (PTU) diluted in tap water (0.05% w/ v), ad libitum, during the lactational period (PTU group). Water 124-129 nuclear RNA export factor 1 Rattus norvegicus 120-123 18371829-5 2008 The sensor was applied to tap water, blood, and rat tail vascular (in vivo). Water 30-35 nuclear RNA export factor 1 Rattus norvegicus 26-29 18642774-6 2008 RESULTS: The expression rates of HA and CD44, and proportion of crystal retention of the tap water 1-day group were 25.0%, 25.0%, and 16.7% respectively, all not significantly different from those of the EG 1-day group (8.3%, 16.7%, and 25.0% respectively, all P > 0.05). Water 93-98 nuclear RNA export factor 1 Rattus norvegicus 89-92 18642774-7 2008 The expression rates of HA and CD44, and proportion of crystal retention of the tap water 5-day group were 33.3%, 25.0%, and 16.7% respectively, all significantly lower than those of the EG 5-day group (83.3%, 75.0%, and 66.7% respectively, all P < 0.05). Water 84-89 nuclear RNA export factor 1 Rattus norvegicus 80-83 17058453-5 2006 According to the same protocol, the rats in the second group were treated with tap water containing 20 mg/kg RVT. Water 83-88 nuclear RNA export factor 1 Rattus norvegicus 79-82 17174719-3 2007 METHODS: Liver cirrhosis was produced by the administration of thioacetamide (0.3 g/L of tap water) for a period of 3 months in rats. Water 93-98 nuclear RNA export factor 1 Rattus norvegicus 89-92 17526630-4 2007 Rats which were chronically treated with alcohol alone or in combination with nicotine, 0.3 mg/kg, showed an increase in ethanol intake when the free choice was performed between ethanol 10% and tap water; on the contrary, when the free choice was performed between ethanol 10% versus nicotine, 0.3 mg/kg, results showed a decrease in ethanol preference and a concomitant increase in nicotine preference. Water 199-204 nuclear RNA export factor 1 Rattus norvegicus 195-198 17005368-3 2006 in the striatum of rats exposed prenatally to both ethanol and cadmium, vs. a 2000% evoked release by AMPH in rats exposed prenatally to only ethanol or cadmium or tap water. Water 168-173 nuclear RNA export factor 1 Rattus norvegicus 164-167 17143008-2 2006 Colonic lesions were induced by 2.5% DSS in the drinking water for 7 days, and then the animals were fed with tap water for subsequent 7 days. Water 114-119 nuclear RNA export factor 1 Rattus norvegicus 110-113 16417942-7 2006 The other two groups; control and diabetic animals, only received tap water. Water 70-75 nuclear RNA export factor 1 Rattus norvegicus 66-69 16404879-3 2005 Moscow tap water served as a control for all waters and was Moscow dechlorinated water after ozone-sorption purification, by passing Moscow tap water from a tap into a 3-liter vessel through a household ozone device for 5 min and then passing it through a household coal filter (500 ml). Water 11-16 nuclear RNA export factor 1 Rattus norvegicus 7-10 16099321-2 2005 METHODS: Liver cirrhosis was produced by the administration of TAA (0.3 g/L of tap water) for a period of 3 months in rats. Water 83-88 nuclear RNA export factor 1 Rattus norvegicus 79-82 16111891-4 2005 The control group rats received tap water. Water 36-41 nuclear RNA export factor 1 Rattus norvegicus 32-35 15735363-5 2005 By using Laurdan, an increase was observed in generalized polarization (GP(340)) in both groups of rats (the one that drank tap water and the one that drank SMW) compared with the controls. Water 128-133 nuclear RNA export factor 1 Rattus norvegicus 124-127 15075460-8 2003 In this model, rats are given free access to different of alcohol solutions (5% and 20% v/v) and tap water. Water 101-106 nuclear RNA export factor 1 Rattus norvegicus 88-100 15345336-1 2004 Hepatic glutathione content was measured and gene expression data were obtained using an Affymetrix RG U34 array after treatment with tap water containing 20mM l-buthionine (S, R)-sulfoximine (BSO) to male F344 rats for four consecutive days. Water 138-143 nuclear RNA export factor 1 Rattus norvegicus 134-137 14966924-5 2004 METHODS: Rats drank a nicotine solution while control rats drank tap water for 20 days. Water 69-74 nuclear RNA export factor 1 Rattus norvegicus 65-68 15577213-6 2004 Increases in indices of renal function, plasma urea nitrogen, were significantly inhibited in rats treated with the Eriobotrya japonica extract compared to rats treated with tap water. Water 178-183 nuclear RNA export factor 1 Rattus norvegicus 174-177 14632915-7 2003 Finally, by using finely milled diet, a wire mesh floor and tap water, instead of conventional breeding methods of regular diet, bedding and acidic water, it was possible to breed rats with minimal signs of periodontal disease. Water 64-69 nuclear RNA export factor 1 Rattus norvegicus 60-63 14693261-7 2003 ethanol in 0.1% saccharin or, in the Water group, drinking of tap water in 0.1% saccharin. Water 66-71 nuclear RNA export factor 1 Rattus norvegicus 62-65 12921889-4 2003 METHODS: The dams were fed increased amounts of ethanol (5% to 20%, vol/vol) in tap water for 4 wk. Water 84-89 nuclear RNA export factor 1 Rattus norvegicus 80-83 12654065-6 2003 Tap water was given to the first group. Water 4-9 nuclear RNA export factor 1 Rattus norvegicus 0-3 12773580-3 2003 Both groups showed transfer to familiar tap water, consuming less in context 1 than in context 2. Water 44-49 nuclear RNA export factor 1 Rattus norvegicus 40-43 12792994-2 2003 Increased unscheduled DNA synthesis was found in a dose-depend manner inducted by tap water, source water and tap water treated with 5, 10 and 15 milligrammes active carbon per liter water. Water 86-91 nuclear RNA export factor 1 Rattus norvegicus 82-85 12792994-3 2003 The results also showed that the mutagenicity of the source water increased with the increasing of its turbidity, and mutagenicity of the tap water is higher than that of the source water as well. Water 60-65 nuclear RNA export factor 1 Rattus norvegicus 138-141 12792994-3 2003 The results also showed that the mutagenicity of the source water increased with the increasing of its turbidity, and mutagenicity of the tap water is higher than that of the source water as well. Water 142-147 nuclear RNA export factor 1 Rattus norvegicus 138-141 12792994-3 2003 The results also showed that the mutagenicity of the source water increased with the increasing of its turbidity, and mutagenicity of the tap water is higher than that of the source water as well. Water 142-147 nuclear RNA export factor 1 Rattus norvegicus 138-141 12792994-5 2003 It is suggested that the development of the water treatment technics including sedimentation, filtration and treatment with active carbon is needed for decreasing or eliminating the mutagenicity of tap water. Water 44-49 nuclear RNA export factor 1 Rattus norvegicus 198-201 12172692-4 2002 One group of rats was chronically exposed to caffeine (1.0 mg/ml) dissolved in their drinking water whereas the other group was exposed to tap water. Water 143-148 nuclear RNA export factor 1 Rattus norvegicus 139-142 12367775-3 2002 METHODS: Tap water containing ethanol at the concentration of 25% (v/v) and phenobarbital (500 mg/l) was the only source of drinking water for the experimental rats for 24 months. Water 13-18 nuclear RNA export factor 1 Rattus norvegicus 9-12 12367775-3 2002 METHODS: Tap water containing ethanol at the concentration of 25% (v/v) and phenobarbital (500 mg/l) was the only source of drinking water for the experimental rats for 24 months. Water 133-138 nuclear RNA export factor 1 Rattus norvegicus 9-12 12462420-2 2002 Using high-density filter-based cDNA microarrays (GeneFilters), we analyzed the expression of over 5000 genes in the dorsal hippocampus of rats treated with 12% ethanol or tap water for 15 months. Water 176-181 nuclear RNA export factor 1 Rattus norvegicus 172-175 12211698-3 2002 rats as model animals drinking tap water with and without lead with i.p. Water 35-40 nuclear RNA export factor 1 Rattus norvegicus 31-34 12691004-3 2003 These two treatments were subdivided into dams that received tap water and dams that received 1.0 g/L L-NAME in tap water. Water 116-121 nuclear RNA export factor 1 Rattus norvegicus 112-115 12601975-6 2002 METHODS: Thirty-two adult Wistar rats fed orally with standard rat chow and tap water "ad libitum" were maintained individual metabolic cages for ten days after 80% gut resection from the duodeno-jejunal angle to 10 cm above the cecum and divided in two groups: -Group A (n = 14): served as control. Water 80-85 nuclear RNA export factor 1 Rattus norvegicus 76-79 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 Rattus norvegicus 227-230 12175467-5 2002 In the first experiment in the current study, 60 male Sprague-Dawley rats were trained to drink 10% EtOH in tap water over 3 weeks of limited-access sessions. Water 112-117 nuclear RNA export factor 1 Rattus norvegicus 108-111 11987081-6 2002 METHODS: One hundred twenty-eight adult Wistar rats fed orally with standard rat chow and tap water "ad libitum" were maintained in individual metabolic cages for 10 days and divided into 3 groups: control group (n = 71): nonmanipulated animals; RES group (n = 39): 80% gut resection from 10 cm beyond the angle of Treitz to 10 cm above the cecum; RES-PRO group (n = 18): same resection and daily 7.8 x 10(8) CFU B Lactis administration, after orogastric intubation. Water 94-99 nuclear RNA export factor 1 Rattus norvegicus 90-93 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 Rattus norvegicus 227-230 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 Rattus norvegicus 227-230 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 Rattus norvegicus 227-230 11185650-2 2000 The ethanol-fed rats drank ethanol (5 to 30% vol/vol) in tap water for 5 wk. Water 61-66 nuclear RNA export factor 1 Rattus norvegicus 57-60 12186308-5 2002 Tap water was then administered until there were no signs of fecal blood. Water 4-9 nuclear RNA export factor 1 Rattus norvegicus 0-3 11435885-5 2001 Hyperoxaluria in groups 2 and 3 rats was induced by administering 1% ethylene glycol, a precursor for oxalates, in the tap water continuously throughout the whole study. Water 123-128 nuclear RNA export factor 1 Rattus norvegicus 119-122 11346485-3 2001 Animals given a diet containing 2-acetylaminofluorene (2-AAF) for 12 weeks and then a basal diet and tap water containing caffeine for 18 weeks showed statistically significant decreases in the incidence, multiplicity (the number of hepatic tumors per rat) and histological grade compared with rats fed a diet containing carcinogen for 12 weeks followed by tap water alone. Water 105-110 nuclear RNA export factor 1 Rattus norvegicus 101-104 11346485-3 2001 Animals given a diet containing 2-acetylaminofluorene (2-AAF) for 12 weeks and then a basal diet and tap water containing caffeine for 18 weeks showed statistically significant decreases in the incidence, multiplicity (the number of hepatic tumors per rat) and histological grade compared with rats fed a diet containing carcinogen for 12 weeks followed by tap water alone. Water 105-110 nuclear RNA export factor 1 Rattus norvegicus 357-360 11346485-3 2001 Animals given a diet containing 2-acetylaminofluorene (2-AAF) for 12 weeks and then a basal diet and tap water containing caffeine for 18 weeks showed statistically significant decreases in the incidence, multiplicity (the number of hepatic tumors per rat) and histological grade compared with rats fed a diet containing carcinogen for 12 weeks followed by tap water alone. Water 361-366 nuclear RNA export factor 1 Rattus norvegicus 101-104 11476157-1 2001 Thioacetamide (TAA) administration (0.3 g/l of tap water for a period of 3 months) to rats resulted in hepatic cirrhosis as assessed by biochemical and histopathological findings. Water 51-56 nuclear RNA export factor 1 Rattus norvegicus 47-50 11686391-2 2001 The control group received solid diet (Purina rat chow) and tap water ad libitum. Water 64-69 nuclear RNA export factor 1 Rattus norvegicus 60-63 11043826-5 2000 A part of animals drank melatonin in a concentration 100 microg/ml of tap water, continuously from the beginning of irradiation and 26 weeks after its end. Water 74-79 nuclear RNA export factor 1 Rattus norvegicus 70-73 10591010-2 1999 Control rats receiving tap water did not show a significant change in blood pressure or abnormalities in the kidney. Water 27-32 nuclear RNA export factor 1 Rattus norvegicus 23-26 10400164-4 1999 The control group comprised rats that drank tap water after subtotal nephrectomy. Water 48-53 nuclear RNA export factor 1 Rattus norvegicus 44-47 10095951-0 1999 [Tap water magnesium deficiency modulate arterial blood pressure, Ca and Mg tissue distribution, and compartmentation of membrane-bound calcium in thrombocytes of normotensive WKY rats]. Water 5-10 nuclear RNA export factor 1 Rattus norvegicus 1-4 10457613-3 1999 The control group received solid diet (Purina rat chow) and tap water ad libitum. Water 64-69 nuclear RNA export factor 1 Rattus norvegicus 60-63 9476992-7 1998 All rats drinking caffeine showed tolerance to its locomotor stimulant effects, whereas rats drinking drug-free tap water did not. Water 116-121 nuclear RNA export factor 1 Rattus norvegicus 112-115 9877005-4 1998 Following the substitution of caffeine solution for tap water, behavior was temporarily disrupted as evidenced by decreases in responding and QL values which reached a maximum after 72 h (rate 60% and QL 30% below baseline levels). Water 56-61 nuclear RNA export factor 1 Rattus norvegicus 52-55 9723198-2 1998 The control group received solid diet (Purina rat chow) and tap water ad libitum. Water 64-69 nuclear RNA export factor 1 Rattus norvegicus 60-63 9835469-0 1998 Wound irrigation with tap water. Water 26-31 nuclear RNA export factor 1 Rattus norvegicus 22-25 9835469-1 1998 OBJECTIVE: The study hypothesis was that irrigation with tap water is as efficacious as irrigation with sterile saline in removing bacteria from simple lacerations in preparation for wound closure. Water 61-66 nuclear RNA export factor 1 Rattus norvegicus 57-60 9835469-9 1998 The wounds irrigated with saline had a mean reduction in bacterial count of 54.7% (SD=+/-28%), while the wounds irrigated with tap water had a mean reduction in bacterial count of 80.6% (SD=+/-20%) (p < 0.05, 2-tailed, paired t-test). Water 131-136 nuclear RNA export factor 1 Rattus norvegicus 127-130 9835469-12 1998 In certain instances, such as with upper-extremity lacerations, tap water irrigation would likely be cheaper and less labor-intensive than irrigation with normal saline from a syringe. Water 68-73 nuclear RNA export factor 1 Rattus norvegicus 64-67 9672456-6 1998 There was a mean reduction in bacterial counts of 81.6% with saline and 65.3% with tap water (P = .34). Water 87-92 nuclear RNA export factor 1 Rattus norvegicus 83-86 9672456-7 1998 One tap water specimen had markedly aberrant bacterial counts compared with others. Water 8-13 nuclear RNA export factor 1 Rattus norvegicus 4-7 9672456-8 1998 Excluding this specimen, the mean reduction for tap water was 80.2%. Water 52-57 nuclear RNA export factor 1 Rattus norvegicus 48-51 9570001-5 1998 Nifedipine plasma concentration-time profiles in the GJRS, OJRS, and (tap) water groups displayed a single peak. Water 75-80 nuclear RNA export factor 1 Rattus norvegicus 70-73 9014028-10 1997 The control group was not made thiamin deficient and consumed lab chow and tap water throughout. Water 79-84 nuclear RNA export factor 1 Rattus norvegicus 75-78 9520346-4 1998 A control group was given tap water (< 0.001 mg U/L). Water 30-35 nuclear RNA export factor 1 Rattus norvegicus 26-29 9198011-1 1997 Alkaline ionized water (AKW) produced by the electrolysis of tap water (TPW) was given to pregnant rats throughout gestation. Water 17-22 nuclear RNA export factor 1 Rattus norvegicus 61-64 9198011-1 1997 Alkaline ionized water (AKW) produced by the electrolysis of tap water (TPW) was given to pregnant rats throughout gestation. Water 65-70 nuclear RNA export factor 1 Rattus norvegicus 61-64 9115611-4 1997 The wound produced by applying a lint for 10 s, and no treatment applied thereafter, and the wound produced by applying a lint for 10 s and immediately after soaked with tap water for 1 min, resulted in moderate damage. Water 174-179 nuclear RNA export factor 1 Rattus norvegicus 170-173 9337079-6 1997 This effect was attributed to taurine depletion since maintenance of the taurine-depleted rats on tap water for 2 days to remove the effects of beta-alanine yielded the same pattern as the taurine-depleted rats exposed to beta-alanine at the time of the experiment. Water 102-107 nuclear RNA export factor 1 Rattus norvegicus 98-101 9252963-5 1997 When 1% NaCl was replaced with tap water, the survival time was prolonged by approximately 80%. Water 35-40 nuclear RNA export factor 1 Rattus norvegicus 31-34 9200142-3 1997 The G-Cd group was given Cd during pregnancy, but given tap water after birth. Water 60-65 nuclear RNA export factor 1 Rattus norvegicus 56-59 8867877-2 1996 Rats lapped drops of tap water from a force-sensing disk. Water 25-30 nuclear RNA export factor 1 Rattus norvegicus 21-24 8851540-8 1996 In Experiment 3, monkeys obtained food or saccharin by pressing keys; the fixed ratio of presses per food pellet was increased once when tap water was each monkey"s only source of fluid, again when each monkey"s water was sweetened with saccharin, and a third time when each monkey had concurrent access to the saccharin solution and plain water. Water 141-146 nuclear RNA export factor 1 Rattus norvegicus 137-140 8762459-4 1996 After the onset of stroke, tap water and normal food was given instead of that containing NaCl. Water 31-36 nuclear RNA export factor 1 Rattus norvegicus 27-30 8072247-7 1994 Random migration of peritoneal macrophages obtained from rats with urethral obstruction given L-arginine prior to obstruction was significantly lower than that of peritoneal macrophages obtained from similar rats given tap water alone prior to obstruction. Water 223-228 nuclear RNA export factor 1 Rattus norvegicus 219-222 8845824-5 1995 The sham-operated rats (sham group) were fed a normal diet and tap water. Water 67-72 nuclear RNA export factor 1 Rattus norvegicus 63-66 8963034-2 1995 Rats drank a solution of nicotine 25 micrograms/mL tap water for periods of 10, 30 or 45 days. Water 55-60 nuclear RNA export factor 1 Rattus norvegicus 51-54 8963034-3 1995 Pentagastrin increased the gastric secretory volume and acid output in pylorus-ligated control animals that drank tap water. Water 118-123 nuclear RNA export factor 1 Rattus norvegicus 114-117 7733406-3 1995 The experiment was performed at the 10th to 12th wk in conscious, chronically instrumented rats hydrated with tap water (2% body wt). Water 114-119 nuclear RNA export factor 1 Rattus norvegicus 110-113 7603640-4 1995 We gavaged simulated tap water, containing a low level of radioactive soluble aluminum (26Al), into the stomachs of rats. Water 25-30 nuclear RNA export factor 1 Rattus norvegicus 21-24 8024453-10 1994 Survival was poor in both groups when only tap water was offered to the animals after hepatectomy (31% vs 12%). Water 47-52 nuclear RNA export factor 1 Rattus norvegicus 43-46 7670125-3 1995 Treatment with TRH resulted in significantly decreased hypothalamic oxytocin content in both euhydrated (i.e. given tap water ad libitum) and salt-loaded rats. Water 120-125 nuclear RNA export factor 1 Rattus norvegicus 116-119 7670125-4 1995 In rats drinking tap water, neurohypophysial oxytocin content decreased. Water 21-26 nuclear RNA export factor 1 Rattus norvegicus 17-20 8242374-10 1993 The first experiment showed that rats preferred a corticosterone solution to tap water, developing self-administration in a dose-dependent manner. Water 81-86 nuclear RNA export factor 1 Rattus norvegicus 77-80 8003666-2 1994 Thirteen animals received 20% alcohol for 15 weeks ad libitum, and 18 were kept under identical conditions drinking tap water. Water 120-125 nuclear RNA export factor 1 Rattus norvegicus 116-119 8059586-3 1994 We can conclude that: 1) a remarkable variance in saline and tap water pH is observed. Water 65-70 nuclear RNA export factor 1 Rattus norvegicus 61-64 7517730-3 1994 Male Donryu rats were divided into three groups given 0.02% ammonia, 0.1% ammonia or tap water. Water 89-94 nuclear RNA export factor 1 Rattus norvegicus 85-88 8011979-6 1994 However, by 15 to 16 wk postnephrectomy, values of glomerular capillary pressure and efferent arteriolar resistance were significantly greater and the glomerular capillary ultrafiltration coefficient was significantly lower in rats drinking tap water than in rats drinking tap water supplemented with L-arginine. Water 245-250 nuclear RNA export factor 1 Rattus norvegicus 241-244 8011979-6 1994 However, by 15 to 16 wk postnephrectomy, values of glomerular capillary pressure and efferent arteriolar resistance were significantly greater and the glomerular capillary ultrafiltration coefficient was significantly lower in rats drinking tap water than in rats drinking tap water supplemented with L-arginine. Water 277-282 nuclear RNA export factor 1 Rattus norvegicus 241-244 8055345-3 1994 Male rats were osmotically stimulated by supplying with 2% NaCl solution instead of tap water for 10 days, and then they were rehydrated with tap water. Water 146-151 nuclear RNA export factor 1 Rattus norvegicus 142-145 8263611-4 1993 On d 19 of pregnancy, the fructose-fed dams had significantly heavier livers and significantly higher plasma glucose and insulin concentrations than dams consuming tap water. Water 168-173 nuclear RNA export factor 1 Rattus norvegicus 164-167 8263611-5 1993 Five days after litters were weaned, dams fed fructose had the heaviest body weights, significantly higher plasma glucose concentration compared with the group receiving tap water and significantly higher plasma triglyceride concentration compared with the glucose-fed group. Water 174-179 nuclear RNA export factor 1 Rattus norvegicus 170-173 8263611-6 1993 Weanlings of the fructose-fed dams had significantly lower plasma glucose concentration but a significantly higher plasma insulin concentration than the weanlings of the group receiving tap water. Water 190-195 nuclear RNA export factor 1 Rattus norvegicus 186-189 8216891-1 1993 Experiments replicated the previous finding that rats with high immobilization time in the forced swim test (passive rats) consumed more 15% ethanol solution in a free choice situation with tap water than rats with active behavior (active rats). Water 194-199 nuclear RNA export factor 1 Rattus norvegicus 190-193 7685786-10 1993 Frozen sections of the thyroids and livers from iodine-treated rats were compared to tap-water controls after staining with Mercury Orange for GSH and Schiff"s reagent for evidence of lipid peroxidation. Water 89-94 nuclear RNA export factor 1 Rattus norvegicus 85-88 8376293-2 1993 Overdrinking was obtained by presenting tap water and sweet water to the rats. Water 44-49 nuclear RNA export factor 1 Rattus norvegicus 40-43 1902909-1 1991 The potent bacterial mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]- furanone) (MX), which is formed during chlorination of drinking water and accounts for about one third of the Ames mutagenicity of tap water, has been studied with respect to its genotoxicity in vitro and in vivo. Water 138-143 nuclear RNA export factor 1 Rattus norvegicus 205-208 1436630-2 1992 Morphine was self-administered orally in tap water by the rats. Water 45-50 nuclear RNA export factor 1 Rattus norvegicus 41-44 1434117-6 1992 A 1% NaCl solution was given as drinking water to the second group (control-saline), while tap water was given to the third group (control-water). Water 95-100 nuclear RNA export factor 1 Rattus norvegicus 91-94 1434117-6 1992 A 1% NaCl solution was given as drinking water to the second group (control-saline), while tap water was given to the third group (control-water). Water 95-100 nuclear RNA export factor 1 Rattus norvegicus 91-94 1387698-6 1992 Urinary albumin excretion was significantly increased in salt-loaded groups (1,790 +/- 272 micrograms/d in control, 1,617 +/- 174 micrograms/d in NIDDM rats) compared with tap-water groups (691 +/- 75 micrograms/d in control, P less than .05; 616 +/- 69 micrograms/d in NIDDM rats, P less than .001), irrespective of STZ injection, but endogenous creatinine clearance was not different among the groups. Water 176-181 nuclear RNA export factor 1 Rattus norvegicus 172-175 2378427-2 1990 The present study describes alterations in brain CRF neuronal systems that accompanied the voluntary high consumption of ethanol by Wistar rats presented with a free choice between 6% ethanol and tap water. Water 200-205 nuclear RNA export factor 1 Rattus norvegicus 196-199 1713498-3 1991 ), a cholecystokinin analog, decreased the intake of ethanol while the consumption of tap water remained unchanged in a choice paradigm. Water 90-95 nuclear RNA export factor 1 Rattus norvegicus 86-89 1668636-2 1991 If the experimental rats are changed to tap water after 15 months of the high sodium diet, the results are partially reversed. Water 44-49 nuclear RNA export factor 1 Rattus norvegicus 40-43 1668636-5 1991 On the other hand, when the rats on the high sodium diet are changed to control conditions (drinking tap water), their Na+ and Cl- contents decrease, approaching control values. Water 105-110 nuclear RNA export factor 1 Rattus norvegicus 101-104 1846120-7 1991 Restriction of dietary NaCl (0.13% in chow, tap water to drink) completely prevented DOCA-induced hypertension, organ and CCT hypertrophy, and enhancement of vasopressin-stimulated cAMP formation in the CCT. Water 48-53 nuclear RNA export factor 1 Rattus norvegicus 44-47 2280429-5 1990 The experimental animals receiving tap water plus table salt had the highest blood pressure levels, although they consumed the lowest quantity of sodium. Water 39-44 nuclear RNA export factor 1 Rattus norvegicus 35-38 2280429-6 1990 Analysis of the tap water samples showed "soft water" by analysis of calcium and magnesium concentration. Water 20-25 nuclear RNA export factor 1 Rattus norvegicus 16-19 2280429-6 1990 Analysis of the tap water samples showed "soft water" by analysis of calcium and magnesium concentration. Water 47-52 nuclear RNA export factor 1 Rattus norvegicus 16-19 2280429-9 1990 The zinc and copper present in tap water may play an exacerbating role. Water 35-40 nuclear RNA export factor 1 Rattus norvegicus 31-34 2176710-3 1990 In rats drinking 2% NaCl-water for 0,2,4, or 10 days, or for 10 days and then tap water for 14 days, the levels of VP mRNA in the NIL were altered in a fashion that paralleled changes in the hypothalamus. Water 82-87 nuclear RNA export factor 1 Rattus norvegicus 78-81 1851783-6 1991 Arteries from rats undergoing DOCA-salt treatment for 5-7 days and from DOCA-treated rats drinking tap water for 4-6 weeks were less responsive to TPA than were arteries from the DOCA-salt hypertensive rats after 4-6 weeks of treatment. Water 103-108 nuclear RNA export factor 1 Rattus norvegicus 99-102 2078164-8 1990 Also, short-term loss of body weight when saline drinking water is replaced with tap water predicts the degree of degeneration of the granule cell layer. Water 85-90 nuclear RNA export factor 1 Rattus norvegicus 81-84 2154994-3 1990 Cardiac taurine levels were reduced by half in rats given tap water containing a beta-amino transport inhibitor, beta-alanine. Water 62-67 nuclear RNA export factor 1 Rattus norvegicus 58-61 2163414-3 1990 However, the magnitude of the increase in mean arterial pressure was significantly lower in the DOCA-hypertensive rats than in the two groups of rats drinking tap water and 1% NaCl after 4 and 6 weeks, but there was no significant difference after 2 weeks. Water 163-168 nuclear RNA export factor 1 Rattus norvegicus 159-162 2163414-5 1990 However, the extent of the fall in renal blood flow was reduced in the DOCA-hypertensive rats compared with the control rats drinking tap water. Water 138-143 nuclear RNA export factor 1 Rattus norvegicus 134-137 2273635-1 1990 Thermally dehydrated rats were given isotonic KCl, NaCl solution, or tap water ad libitum for 17 h and the differences of the restoration rate in fluid and cation were compared between the groups to elucidate the effect of Na+ and K+ ions on the replacement of each body fluid compartment during rehydration. Water 73-78 nuclear RNA export factor 1 Rattus norvegicus 69-72