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1 of dissolved arsenic in groundwater used for drinking.
2 t dogs would ingest copepods readily through drinking.
3 % prediction accuracy for >=50% reduction in drinking.
4 d vermis of youths who initiated substantial drinking.
5 e, but not in mice with a history of ethanol drinking.
6  protected against anxiety caused by alcohol drinking.
7 gets, which plays an important role in binge drinking.
8 sloped), using distinct paradigms to measure drinking.
9  in REM sleep when individuals with AUD stop drinking.
10 s in adolescents before and after initiating drinking.
11  responses to stress following heavy alcohol drinking.
12 ie the transition from moderate to excessive drinking.
13 1.70-2.76), those reporting moderate alcohol drinking 1.76 (1.21-2.57), and those with increased numb
14                             The reduction in drinking after naltrexone was negatively associated with
15                 Even in the absence of binge drinking, alcohol consumption during pregnancy can leave
16 hol dependence or a consequence of excessive drinking and alcohol exposure.
17 l nucleus (RMTg) decreased voluntary alcohol drinking and alcohol self-administration.
18 lective agonist pioglitazone reduces alcohol drinking and alcohol-seeking behavior in rats.
19 f naltrexone (50 mg/day) in reducing alcohol drinking and craving among FHP drinkers with beneficial
20 from the perspective of the roles of alcohol drinking and dietary factors in a rural population.
21  RCTs, we computed medication effects on any drinking and heavy drinking (k = 118 studies, 17 medicat
22  the effects of PPARgamma agonism on alcohol drinking and seeking in msP rats.
23 the effects of PPARgamma agonists on alcohol drinking and seeking.
24 y provides a foundation that shows how binge drinking and the oral microbiome dysbiosis lead to perme
25 havior relationships: one related to age and drinking and the other one related to depression.
26                                 Ozonation of drinking and wastewater relies on ozone (O(3)) and hydro
27 arious disinfection methods commonly used in drinking and wastewater treatment plants.
28 astating illness defined by periods of heavy drinking and withdrawal, often leading to a chronic rela
29 icidal ideation, suicide attempts, hazardous drinking, and opioid use.
30  physical inactivity, current smoking, heavy drinking, and oral estrogen use to assess independent as
31                                   Controlled-drinking approaches should be promoted and comorbidity m
32 ucleus is reinforcing, and increases ethanol drinking as well as consumption of sucrose and saccharin
33                     Sustained male hazardous drinking (as measured by the AUDIT-C scale) was also ass
34 S) to examine the association between coffee drinking, as assessed by a semi-quantitative food freque
35 on paradigm followed by a compulsive ethanol drinking assay.
36                                      Current drinking at 19-21 weeks (RR 3.96 95% CI [1.04-15.05]) an
37                                              Drinking behavior and osmotic regulatory mechanisms exhi
38 trols metabolic organ homeostasis and eating/drinking behavior via FGF receptor 1/Klothobeta (FGFR1/K
39 s, current drinker, defined as any recurrent drinking behavior, and regular drinker, defined as the s
40 that these contribute to daily regulation of drinking behavior.
41  generated and how it subsequently motivates drinking behavior.
42 t from reward contribute to predicting risky drinking behaviors.
43 e, would have a greater influence on alcohol drinking behaviors.
44 ioid systems play important roles in alcohol drinking behaviors.
45  were developed to identify pig postures and drinking behaviours of group-housed pigs.
46 eding routine in standing, lateral lying and drinking behaviours.
47 l, E2) are associated with increased alcohol drinking by women and experimentally in rodents.
48 werfully drive later alcohol use in familiar drinking contexts, yet we know little about what patient
49 mpared with healthy controls (HCs) and heavy drinking controls (HDCs).
50 tes that rely upon nonpublic water wells for drinking, cooking, and other household uses.
51 ransferase (ALT), and higher number of heavy drinking days (all ps < 0.05).
52 bo had 35.58% heavy drinking days and 58.47% drinking days (heavy drinking days: odds ratio=0.14, 95%
53 al symptoms on prazosin reported 7.07% heavy drinking days and 27.46% drinking days, while those on p
54 ays, while those on placebo had 35.58% heavy drinking days and 58.47% drinking days (heavy drinking d
55    Primary outcomes were daily self-reported drinking days and heavy drinking days, and secondary out
56 relapse, and reduced the likelihood of heavy drinking days compared with midazolam.
57   Proportions of participants with any heavy drinking days decreased in both groups at 6 months but d
58 ence and also predicted greater number heavy drinking days during the subsequent 2 weeks of treatment
59 period (weeks 3-12) for drinking days, heavy drinking days, and average drinks/day.
60  daily self-reported drinking days and heavy drinking days, and secondary outcomes were average drink
61  full-dose treatment period (weeks 3-12) for drinking days, heavy drinking days, and average drinks/d
62 eported 7.07% heavy drinking days and 27.46% drinking days, while those on placebo had 35.58% heavy d
63 rinking days and 58.47% drinking days (heavy drinking days: odds ratio=0.14, 95% CI=0.058, 0.333; dri
64  days: odds ratio=0.14, 95% CI=0.058, 0.333; drinking days: odds ratio=0.265, 95% CI=0.146, 0.481).
65                 Lastly, a history of alcohol drinking did not alter synaptic transmission in PDYN neu
66 rrent (weekly) drinkers, AAI <18.1 years and drinking duration >30.0 years were associated with 18% (
67 betes, compared with AAI 18.1-29.0 years and drinking duration <10.1 years, respectively.
68  used to estimate the association of AAI and drinking duration with type 2 diabetes.
69                                              Drinking durations of <10.1 years, 10.1-20.0 years, and
70 s disruption in turn predicted greater heavy drinking during early treatment.
71  abstinence and whether they influence heavy drinking during the early treatment phase.
72 ter amount consumed in the first half of the drinking episode.
73 ate the number of copepods ingested during a drinking event.
74                             Memory for prior drinking experiences may powerfully drive later alcohol
75 .02 (95% CI: -0.05, 0.08)) and stable, heavy drinking (for Blacks, adjusted MD = 0.08 (95% CI: -0.34,
76                      Stable, low to moderate drinking (for Blacks, adjusted mean difference (MD) = 0.
77  metabolic syndrome who fasted (no eating or drinking) from dawn to sunset for more than 14 h daily f
78 ch discourages the initiation of feeding and drinking (fully recapitulating the symptoms of gastric d
79 nificant in the never-smoker and non-alcohol drinking groups.
80 y lifestyle including current smoking, heavy drinking (&gt; 30 g/day), and lack of regular exercise, and
81                 Heavy smokers tended to have drinking habits, which was associated with increased BMI
82  The process of diagnosing hazardous alcohol drinking (HAD) is based on self-reported data and is the
83                            Excessive alcohol drinking has been shown to modify brain circuitry to pre
84            In this population based setting, drinking high volumes of alcohol may contribute to the p
85  can ingest copepod intermediate hosts while drinking; however, low numbers were ingested at the dens
86  during imagined thirst relative to imagined drinking, implying functional connectivity between these
87 obability of suicidal ideation and hazardous drinking in adolescence and young adulthood as well as o
88 understanding the neural basis of compulsive drinking in alcohol use disorder.
89 nses wherein PDYN knockout decreased alcohol drinking in both male and female mice, whereas KOR knock
90 )-GPCR signaling in PFC astrocytes increased drinking in ethanol-naive mice, but not in mice with a h
91                The influence of ERs on binge drinking in female mice suggests that treatments for alc
92 ceptor in the VTA reduced binge-like ethanol drinking in female, but not male, mice.
93 nd NOV stress more effectively increased 2BC drinking in males and females, respectively.
94  female mice, whereas KOR knockout decreased drinking in males only.
95 table low, low to moderate, and stable heavy drinking in midlife are not associated with lesser and g
96 (p = 0.002) and higher subsequent (p = 0.01) drinking in patients with AUD.
97 ne infusion was found to improve measures of drinking in persons with alcohol dependence engaged in m
98  these genes and assessed the effects on the Drinking in the Dark (DID) and Intermittent Access (IA)
99  amounts of ethanol in the first days of the drinking in the dark protocol, as compared with WT mice.
100 an those traditionally associated with binge drinking in young adults.
101 mbining alcohol use disorder and problematic drinking, in 435,563 European-ancestry individuals.
102 kers have been administered to heavy alcohol drinking individuals.
103 age, sex, education, race/ethnicity, alcohol drinking intensity, cigarette smoking duration and inten
104                                        Binge drinking is associated with disease and death, and devel
105 medication effects on any drinking and heavy drinking (k = 118 studies, 17 medications).
106  D. medinensis, but due to the method of dog drinking (lapping) compared to humans (suction and/or re
107 t cerebellar structures affected by youthful drinking may be vulnerable to age-alcohol interactions i
108 NTX + MEM resulted in a further reduction in drinking (mean: -1.94; 95% CI: -2.6, -0.8, p = 0.0005).
109 ocampus and following a rat adolescent binge drinking model.
110                                     For men, drinking more than 21 units (approximately 168 grams) of
111 is did not support a causal effect of coffee drinking on IOP (P > 0.1).
112 o psychological decompensation and increased drinking or relapse.
113 ages combined with prospective assessment of drinking outcomes during early outpatient treatment, in
114 ta = 3.28, p < 0.001) in the laboratory, and drinking outcomes in RCTs, such that medications that re
115  in motivational enhancement therapy affects drinking outcomes.
116 were prospectively predictive of early heavy drinking outcomes.
117         Men who maintained a heavy volume of drinking over the three decades of observation, or who h
118  number of drinks consumed during an alcohol drinking paradigm (ADP) before and after 1 week of super
119 intake of alcohol without accounting for the drinking pattern.
120  intake in a two-bottle choice, intermittent drinking procedure without affecting saccharin intake, e
121 intermittent ethanol vapor two-bottle choice drinking procedure.
122 ce for alcohol in a 24 h intermittent access drinking procedure.
123           To assess which memories predicted drinking, real-world behavior was assessed in patients w
124  in preclinical models as a target to reduce drinking-related behaviors and cue-induced reinstatement
125 e neural representation of thirst contains a drinking-related component.
126                                     However, drinking-resilient males showed the highest G-CSF, IL-13
127 tracted withdrawal from intermittent alcohol drinking resulted in enhanced prefrontal cortex (PFC)-dr
128 ific mechanisms that drive excessive alcohol drinking.SIGNIFICANCE STATEMENT Estrogen has potent effe
129               Brain processes underlie risky drinking, so we examined whether neural and psychosocial
130        Two fMRI-based models predicted binge drinking status better than chance, corresponding to the
131                          Smoking and alcohol-drinking status were not associated with unilateral or b
132 oms, number of cigarettes smoked per day and drinking status were related to suicide attempts in SCZ
133 cs, dietary intake, and detailed smoking and drinking status.
134  regions were also activated during imagined drinking, suggesting the neural representation of thirst
135 , and paraoxon, and without matrix effect in drinking, surface, and wastewater.
136 e analysis of nanoplastics of up to 1 mum in drinking, tap, and river water.
137 VTA had a more dramatic effect on binge-like drinking than reducing ERbeta, consistent with the abili
138 s method to establish the link between binge drinking, the oral microbiome and AD.
139           In Study 1 (N = 200), though total drinking time was equivalent, participants consumed a so
140 me in relation to alcohol misuse- from binge drinking to addiction.
141 but later stages of AUD are characterized by drinking to alleviate withdrawal-induced negative emotio
142 l use disorder (AUD) involves binge or heavy drinking to high levels of intoxication that leads to co
143 te of intense thirst and while they imagined drinking to satiate thirst.
144  observed for the stable former and "mostly" drinking trajectories with 15-year cognitive decline.
145               Stressed male rats, especially drinking-vulnerable individuals (>=0.8 g/kg average 2-h
146 rams) of alcohol per week, compared with not drinking, was associated with waking several times a nig
147 n in the galc gene were given fingolimod via drinking water (1 mg/kg/d).
148 compassing the current EPA limit for lead in drinking water (15 ppb).
149 tion of water isotopes has been monitored in drinking water (DW; deltaD = -36.59 +/- 10.64 per mille
150 tions relevant to chloramine disinfection of drinking water (pH 6-9 and carbonate-buffered) was devel
151 ceive chow diet, high fat diet with sugar in drinking water (Western diet- WD).
152 onmental interventions that foster effective drinking water access, a concept that encompasses key el
153  water quality is regulated through the Safe Drinking Water Act, there are no drinking water standard
154 ater system that is regulated under the Safe Drinking Water Act.
155 FAS accounted for about 50% of total PFAS in drinking water and 90% in serum.
156 ces, evaluated the microbiological safety of drinking water and associated health outcomes, and estim
157 dy, we aimed to describe the PFAS profile in drinking water and biological samples (paired serum and
158 ed organic matter (DOM) is ubiquitous in raw drinking water and can efficiently scavenge oxidants, su
159 lacement coupled with CCT for reducing Pb in drinking water and children's BLLs, and (2) in some age
160    Research has focused on PFAS exposure via drinking water and diet, and fewer studies have focused
161  a ubiquitous source of chemical exposure in drinking water and have been associated with serious hea
162                     The presence of PFASs in drinking water and in the environment is an urgent globa
163 ) and household characteristics (ie, type of drinking water and sanitation facilities).
164 that poor housing, which includes inadequate drinking water and sanitation facility, is associated wi
165 rganisms is a low-cost approach to disinfect drinking water and wastewater.
166 vels in North Carolina school and child care drinking water by building age, (ii) evaluate the effect
167                   Decreased contamination of drinking water by C. jejuni and S. enterica was also obs
168 ve indicates that they periodically obtained drinking water by using fire to melt cave ice, and sheds
169  local and residential water use conditions, drinking water can be the dominant exposure pathway.
170 umbing and generated distinctively different drinking water chemical and microbial quality profiles.
171  and chlorine radical decrease by 38-100% in drinking water compared to ultrapure water, which is pri
172 hat likely resulted from the impact of HM on drinking water composition.
173                                              Drinking water containing no supplement or the PDK (pyru
174 r exposure to lead, a high-profile regulated drinking water contaminant.
175                                              Drinking water contamination related to the use of aqueo
176          Fragmentation in responsibility for drinking water contributes to disparities in drought vul
177  by harboring and shedding microbes into the drinking water distribution system.
178           Microbial presence and regrowth in drinking water distribution systems (DWDSs) is routinely
179 sion in contact with residual disinfectants, drinking water distribution systems have become potentia
180 ggest that corticosterone, delivered through drinking water even 24 h after acute stress, is capable
181 t Americans and discuss strategies to reduce drinking water exposure to lead, a high-profile regulate
182 nistered either vehicle or IAP (100 U/ml) in drinking water for 14 days in C57BL/6 mice.
183 ice were exposed to 5 ppm ( ~ 65 muM) iAs in drinking water for 3 months.
184 ce were administered estradiol or vehicle in drinking water for 6 weeks.
185     We obtained data on microbial content of drinking water for all participants; 585 children were r
186 ffects households' access to clean, reliable drinking water for basic needs is through the organizati
187                                              Drinking water from tube wells, compared to other source
188 threatens the availability of safe and clean drinking water globally.
189 e 0.1-0.2 mg L(-1) World Health Organization drinking water guidelines in all regimes, and inorganic
190 ze groundwater As treatment to meet relevant drinking water guidelines, while considering the As upta
191 and quantitatively measuring aqueous lead in drinking water has been developed.
192 rs, environmental lead (Pb) exposure through drinking water has resulted in community public health c
193  and recognition of the health importance of drinking water in lieu of sugar-sweetened beverages, hav
194 pheric water capture (AWC) can provide clean drinking water in locations not connected to the central
195 nificantly with increasing bacterial load in drinking water in the first year of life (0.79 [0.70,0.8
196 anoparticles were an important form of Pb in drinking water in the Pequannock water quality zone of N
197  as well as several other divalent metals in drinking water including copper, zinc, iron, and mangane
198                       Lack of access to safe drinking water is a global problem, and methods to relia
199                     Access to clean and safe drinking water is a perpetual concern in Arctic communit
200                              Access to clean drinking water is a recognized societal need that touche
201 until centralized, or decentralized, treated drinking water is available; displacing biomass use for
202  The data reveal that ClO(4)(-) pollution in drinking water is more dangerous than previously thought
203 ribe US regulations that seek to ensure that drinking water is safe to consume for most Americans and
204 ng need in view of increasingly stringent As drinking water limits in some US states and European cou
205                                 Treatment of drinking water may decrease microbial exposure.
206 ection Agency's lifetime health advisory for drinking water may or may not be protective of vegetable
207         The co-occurrence of contaminants in drinking water may pose enhanced risks to health beyond
208          High commensal bacterial content in drinking water may protect against allergic diseases.
209 of microbial exposure (bacterial load in the drinking water measured during the child's first year of
210  There was a dominant seasonal effect on the drinking water microbiomes at all three locations.
211                  SCFA supplementation in the drinking water of male mice significantly improved recov
212         When we added indoxyl sulfate to the drinking water of rats fed an adenine-rich diet, we foun
213            Following a pH reduction in their drinking water over a span of more than 20 years, the Ci
214 ntial impacts on blood Pb levels (BLLs) from drinking water Pb reduction actions (i.e., combinations
215 ortant to OGW-impacted source waters because drinking water plants with high-bromide source waters ma
216 tic ecosystems and poses a major problem for drinking water production.
217   Research on the local political economy of drinking water provision reveals the constraints on comm
218 ent of the impact of Hurricane Maria (HM) on drinking water quality in Puerto Rico (PR) by integratin
219 terial communities in biofilters can improve drinking water quality through the biodegradation of dis
220       The results indicate that point of use drinking water quality was impacted by conditions in the
221 able regrowth conditions affecting the final drinking water quality.
222 bution to BLLs from ingestion of residential drinking water ranged from ~10 to 80%, with the highest
223 otensin receptor blocker losartan to mice in drinking water reduced both allodynia and muscle fibrosi
224                    Inadequate access to safe drinking water remains a global health problem, particul
225                            Germany's largest drinking water reservoir was sampled for 1 year, and DOM
226 om subsample of households, we tested stored drinking water samples for Escherichia coli, concurrentl
227                                              Drinking water samples were analyzed for F(-), and the r
228                   The presence of bromide in drinking water significantly accelerated Cr(VI) release
229                                              Drinking water source and sanitation facility alone were
230 s (PFAS) to the Cape Fear River, the primary drinking water source for Wilmington, North Carolina, re
231 hese biofilms were grown from groundwater (a drinking water source), and this groundwater was amended
232 ns between children's blood Pb and household drinking water source.
233 gh the Safe Drinking Water Act, there are no drinking water standards for nonpublic water well qualit
234  regional groundwater uranium exceedances of drinking water standards, 30 mug L(-1), are dependent on
235                                    Household drinking water storage is commonly practiced in rural In
236 pplied for the quantification of BPA present drinking water stored in the plastic bottles.
237               Addition of inorganic salts to drinking water such as KH(2)PO(4) + NaCl+KNO(3) resulted
238      In low-income countries, monitoring all drinking water supplies is impractical because financial
239 ultiple locations in a decentralized trucked drinking water system in Nunavut, Canada, over the cours
240  assessments that inform decisions involving drinking water systems.
241 ons of PFHxA, PFHpA, and PFBS were higher in drinking water than in serum.
242  Classical transmission to humans occurs via drinking water that contains cyclopoid copepods infected
243 tural experiment whereby individuals receive drinking water through public mains supply or individual
244 ge with water from PND 14 to 21 and received drinking water till the time of sacrifice.
245 rocess (AOP) for micropollutant abatement in drinking water treatment and water reuse plants.
246 l generation for micropollutant abatement in drinking water treatment or potable water reuse.
247                     Analysis of a full-scale drinking water treatment plant GAC filter influent, effl
248  the life cycle environmental performance of drinking water treatment using LFMs under likely design
249 w-dose individual ABX or ABX cocktail in the drinking water until the time of sacrifice.
250                                        5b in drinking water was given to mice expressing wild-type hu
251                 Cumulative bacterial load in drinking water was higher (median [IQR]: 6390 [4190-9550
252     This multitool approach was applied to a drinking water well, where bentazon and dichlorprop cont
253 ifying the source and age of contaminants in drinking water wells by combining depth-specific samplin
254                                           In drinking water wells, where water is typically abstracte
255 l elephant food, soil from enclosure(s), and drinking water were also sampled.
256 s, wealth index, toilet types and sources of drinking water were the most significant contributors to
257                              Mice were given drinking water with ampicillin or without (controls).
258                    Germ-free mice were given drinking water with TLR2 agonist or without (controls).
259 itored to assess the biological stability of drinking water without a residual disinfectant, but the
260 ce treated with deferiprone (1 or 3 mg/mL in drinking water) for 26 weeks was reversed.
261 ne of the dominant genera in the distributed drinking water, already occurred in the clean water rese
262 minants, and increases lead contamination of drinking water, but its effects are not well integrated
263 uent antibiotic misuse; and (3) insufficient drinking water, drainage and sanitation infrastructure.
264 s of 5-bromo-2'-deoxyuridine (BrdU) in their drinking water, followed by chase periods without BrdU,
265 is study used data on fecal contamination of drinking water, food, soil, hands, and objects and secon
266 on comparing improved housing (with improved drinking water, improved sanitation, sufficient living a
267                                              Drinking water, in an attempt to release it, led to a to
268 ses ultimately depends on the access to safe drinking water, properly managed sanitation, and hygiene
269 costerone, given 1 day after acute stress in drinking water, reversed enhanced anxiety-like behavior
270    Ensuring urban areas have access to clean drinking water, safe food supply, and uncontaminated wat
271                         We hypothesized that drinking water, sanitation, handwashing (WSH), and nutri
272 followed 24 h later by corticosterone in the drinking water, the surge in corticosterone was prevente
273 e presence of this cyanotoxin in freshwater, drinking water, water reservoir supplies and food (veget
274  potential to displace other sources of safe drinking water, which could in turn hamper efforts in Ch
275 F(-)) is one of the most harmful elements in drinking water.
276  quantitative measurement of aqueous lead in drinking water.
277 ally exposed to nicotine (100 mug/ml) in the drinking water.
278 ose of nitrate-depleted BRJ (BRJ-) or normal drinking water.
279 nganese) and lead and copper in point of use drinking water.
280 on by bacteria, but not bacterial growth, in drinking water.
281 y PFAS (i.e., PFOA, PFHxS, and PFOS) through drinking water.
282 cterize microplastics in both wastewater and drinking water.
283  dispersed insoluble and soluble toxins from drinking water.
284 ormal chow, or zero-fiber diets, or SCFAs in drinking water.
285  which have been reported as contaminants in drinking water.
286 kout mice overloaded with indoxyl sulfate in drinking water.
287  induced by administration of doxycycline in drinking water.
288 le soluble lead concentrations in the city's drinking water.
289 ericans depending on private wells for their drinking water.
290  levels in rats that received vehicle in the drinking water.
291 al indicator bacteria in groundwater-derived drinking water.
292 ation infrastructure to separate sewage from drinking water.
293 i/L (picocuries per liter), respectively, in drinking-water supplies may pose human-health concerns.
294 etermination of Al(3+) in real food samples, drinking waters and herbal teas, were employed.
295 0.11)) in midlife compared with stable never-drinking were not associated with 15-year decline in gen
296 e is fundamental to survival as it motivates drinking, which subsequently corrects the fluid deficit.
297 15-year cognitive decline, and stable, heavy drinking with greater 15-year cognitive decline.
298  alcohol consumption and duration of alcohol drinking with type 2 diabetes mellitus among Chinese adu
299 We hypothesized that stable, low to moderate drinking would be associated with lesser 15-year cogniti
300 s negatively associated with number of years drinking (YOD) in FH positive, but not FH negative, part

 
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