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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
19 f naltrexone (50 mg/day) in reducing alcohol drinking and craving among FHP drinkers with beneficial
21 RCTs, we computed medication effects on any drinking and heavy drinking (k = 118 studies, 17 medicat
24 y provides a foundation that shows how binge drinking and the oral microbiome dysbiosis lead to perme
28 astating illness defined by periods of heavy drinking and withdrawal, often leading to a chronic rela
30 physical inactivity, current smoking, heavy drinking, and oral estrogen use to assess independent as
32 ucleus is reinforcing, and increases ethanol drinking as well as consumption of sucrose and saccharin
34 S) to examine the association between coffee drinking, as assessed by a semi-quantitative food freque
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
48 werfully drive later alcohol use in familiar drinking contexts, yet we know little about what patient
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
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
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).
66 rrent (weekly) drinkers, AAI <18.1 years and drinking duration >30.0 years were associated with 18% (
75 .02 (95% CI: -0.05, 0.08)) and stable, heavy drinking (for Blacks, adjusted MD = 0.08 (95% CI: -0.34,
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
80 y lifestyle including current smoking, heavy drinking (> 30 g/day), and lack of regular exercise, and
82 The process of diagnosing hazardous alcohol drinking (HAD) is based on self-reported data and is the
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
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
95 table low, low to moderate, and stable heavy drinking in midlife are not associated with lesser and g
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.
101 mbining alcohol use disorder and problematic drinking, in 435,563 European-ancestry individuals.
103 age, sex, education, race/ethnicity, alcohol drinking intensity, cigarette smoking duration and inten
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).
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
118 number of drinks consumed during an alcohol drinking paradigm (ADP) before and after 1 week of super
120 intake in a two-bottle choice, intermittent drinking procedure without affecting saccharin intake, e
124 in preclinical models as a target to reduce drinking-related behaviors and cue-induced reinstatement
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
132 oms, number of cigarettes smoked per day and drinking status were related to suicide attempts in SCZ
134 regions were also activated during imagined drinking, suggesting the neural representation of thirst
137 VTA had a more dramatic effect on binge-like drinking than reducing ERbeta, consistent with the abili
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
144 observed for the stable former and "mostly" drinking trajectories with 15-year cognitive decline.
146 rams) of alcohol per week, compared with not drinking, was associated with waking several times a nig
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
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
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
164 that poor housing, which includes inadequate drinking water and sanitation facility, is associated wi
166 vels in North Carolina school and child care drinking water by building age, (ii) evaluate the effect
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
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
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
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
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
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
206 ection Agency's lifetime health advisory for drinking water may or may not be protective of vegetable
209 of microbial exposure (bacterial load in the drinking water measured during the child's first year of
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
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
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
226 om subsample of households, we tested stored drinking water samples for Escherichia coli, concurrentl
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
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
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
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
248 the life cycle environmental performance of drinking water treatment using LFMs under likely design
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
256 s, wealth index, toilet types and sources of drinking water were the most significant contributors to
259 itored to assess the biological stability of drinking water without a residual disinfectant, but the
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
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
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
293 i/L (picocuries per liter), respectively, in drinking-water supplies may pose human-health concerns.
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.
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