ライフサイエンスコーパス: water quality

1 al scenarios (rainfall, river flow rate, and water quality).

2 but there are no guidelines for handwashing water quality.

3 ting the benefits of treatment to downstream water quality.

4 g strategies for managing inland and coastal water quality.

5 ortant for the effective management of local water quality.

6 FWs on nutrient-based (nitrogen, phosphorus) water quality.

7 s a risk for aquatic ecosystems and drinking water quality.

8 monstrating its potential use for monitoring water quality.

9 trophication in fresh waters and maintaining water quality.

10 vestigating future climate change impacts on water quality.

11 fectant exposure, causing the degradation of water quality.

12 understanding of how NFWs affect downstream water quality.

13 and expenditures by the groups also improved water quality.

14 onments for removing pathogens and improving water quality.

15 rovide ecosystem services that help maintain water quality.

16 ng the monetary impact of efforts to improve water quality.

17 al alteration of soil by wildfire can affect water quality.

18 alence of harmful algal blooms that threaten water quality.

19 treatment is an important aspect in terms of water quality.

20 so impact pollutant sources and trigger poor water quality.

21 can result in severe degradation of product water quality.

22 ify mechanisms by which urbanization impacts water quality.

23 rship with child growth and household stored water quality.

24 efforts to mitigate the impacts of runoff on water quality.

25 ess hydrologic systems and impact downstream water quality.

26 own to cause detrimental loss of the product water quality.

27 study challenges to maintaining private-well water quality.

28 nitation access on child health and drinking water quality.

29 ng plumbing following a transition in source water quality.

30 owth conditions affecting the final drinking water quality.

31 mination, and the effect of rainfall on well water quality.

32 purposes and in risk assessment of microbial water quality.

33 eds have not seen substantial improvement in water quality.

34 om overfishing, habitat destruction and poor water quality.

35 entiate hydrological processes that affected water quality: (1) in the upper watershed, runoff dilute

36 idual wetlands have the potential to improve water quality(2-9), little is known about the current ma

37 ions need to be clarified to ensure food and water quality across different irrigation systems.

38 stry to high-frequency measurements of river water quality across six watersheds (five impacted by oi

39 lthough 60% of studies found improvements in water quality after implementation of Best Management Pr

40 ies that were unable to find improvements in water quality after the implementation of BMPs, the lack

41 ng to Lake Erie as a part of the Great Lakes Water Quality Agreement, Lake Erie appears to be undergo

42 Improvements to source water quality alone are unlikely to prevent exposure to

43 In this study, the well-known Water Quality Analysis Simulation Program (WASP) was upd

44 water resources, while soil erosion reduces water quality and agronomic productivity.

45 t than private latrine access for protecting water quality and child health.

46 re environments has been linked to declining water quality and ecosystem health.

47 Water quality and fishing pressure had minimal effect on

48 hough bedrock weathering strongly influences water quality and global carbon and nitrogen budgets, th

49 bacterial blooms are an increasing threat to water quality and global water security caused by the nu

50 e utilised as a bio-indicator, for assessing water quality and health status of a given freshwater sy

51 tion should be included in future studies of water quality and health.

52 n environmental analysis because they impact water quality and introduce potential (eco)toxicological

53 cation of LSWT has numerous consequences for water quality and lake ecosystems, so quantifying this a

54 egy to strike a balance between good surface water quality and low greenhouse gas emissions.

55 ollecting wildlife observations, measures of water quality and much more.

56 ing cryosphere, with implications for future water quality and productivity at high latitudes.

57 oms (cyanoHABs) are a serious environmental, water quality and public health issue worldwide because

58 kstoves have been widely promoted to improve water quality and reduce fuel use, but there is limited

59 the intervention improved household drinking water quality and reduced caregiver-reported diarrhea am

60 g (MST) methods are powerful tools to manage water quality and support public health risk assessment.

61 f can salinize freshwaters and threaten lake water quality and the many ecosystem services lakes prov

62 ) and patterns of intervention use, drinking water quality, and air quality.

63 plications for land productivity, downstream water quality, and biogeochemical cycles.

64 rivers regulates aquatic food web dynamics, water quality, and carbon storage.

65 s area was lost due to disease, deteriorated water quality, and coastal development, with losses peak

66 sses, which provide nursery habitat, improve water quality, and constitute a globally important carbo

67 complex interactions of land-use practices, water quality, and ecological integrity of streams, the

68 f environmental conditions, photoreactivity, water quality, and engineering design in the sunlight in

69 ces may reshape the structure of watersheds, water quality, and the health of aquatic organisms.

70 valve molluscs quality depends mainly on the water quality, and then by a series of factors such as w

71 to improve nutrition status, sanitation, and water quality are important to reduce enteric infections

72 ex, we find that while reefs exposed to poor water quality are more resistant to coral bleaching, the

73 eased frequency of summer heatwaves and poor water quality are two of the most prevalent and severe p

74 case for universal screening of private well water quality around arsenic, the most toxic and widespr

75 Geological Survey National Water Quality Assessment Project is conducting regional-

76 outine environmental monitoring and drinking water quality assessment since the guideline value set b

77 benthic biota are still underrepresented in water quality assessment strategies.

78 ferences in accuracy related to the types of water quality assessment tools used by citizen scientist

79 l in laboratories performing microbiological water quality assessment.

80 Common water quality assessments involve quantifying indicator

81 t be fully captured in future ecological and water quality assessments, if the apparent resistance of

82 ten considered a viable option for improving water quality at local scales.

83 pipe scale and biofilm and negatively impact water quality at the distribution level.

84 endment has the potential to broadly improve water quality at the watershed scale, particularly when

85 , non-floodplain wetlands (NFWs), on surface water quality at watershed scales.

86 titioned among 6 EH topic areas: a) drinking water quality, b) wastewater management, c) healthy home

87 gineering design, and ecology to improve the water quality benefits of green infrastructure.

88 Environmental Protection Agency estimates of water quality benefits, fuel-switching benefits, and reg

89 on) in order to improve soil N retention and water quality benefits.

90 Measurements of carbon metabolism, effluent water quality, biofilm sloughing rate, and microbial div

91 In the USA, impacts to drinking water quality, biogeochemical cycles, and aquatic ecosys

92 flooding and leading to major alterations of water quality, biogeochemistry, and ecological condition

93 y functions, such as food web production and water quality, but an increasing frequency and intensity

94 g (NGS), provide new insights into microbial water quality, but considerable uncertainty remains arou

95 )-catalyzed recrystallization, can influence water quality by causing the incorporation/release of en

96 potential degradation of ground and surface water quality by high-salinity produced water generated

97 merging strategy to deliver improved surface water quality by responsive operation according to real-

98 Drinking water biofilters can improve water quality by transforming contaminants or their prec

99 Inadequate water quality can mean that water is unsuitable for a va

100 little human alterations experienced minimal water quality changes and had relatively rapid recoverie

101 vely characterised by organisms sensitive to water quality changes such as diatoms, single-celled alg

102 bed depth) and temporal variation linked to water quality changes.

103 CH(4) and dissolved organic carbon) and soil-water quality characteristics in an intact and a degrade

104 We evaluated water quality characteristics in the northern Raton Basi

105 s drinking water as a rational benchmark for water quality comparison, explicitly recognizes that con

106 response profiles is that under many typical water quality conditions, MLR- and BLM-based criteria ar

107 predictions difficult under any given set of water quality conditions.

108 rocess would be robust under a wide range of water quality conditions.

109 Concentrations of 15 water quality constituents including nutrients, major io

110 rd error) degrees C of warming was paid by a water-quality credit equivalent to 0.89 (+/-0.04) degree

111 Recent water quality crises in the United States, and recogniti

112 tection Agency (USEPA) recommended BLM-based water quality criteria (WQC) for Cu in freshwater.

113 ) in the Delaware River currently exceed the Water Quality Criteria of 16 pg/L for the sum of PCBs du

114 ation and recovery; (3) to propose numerical water-quality criteria as targets for restoration; (4) t

115 nd analyses and the development of numerical water-quality criteria.

116 e, we gathered physiochemical and biological water quality data from 2010 to 2016 to evaluate charact

117 This study collected post-Harvey water quality data in multiple streams for several weeks

118 ion in Pennsylvania has been documented with water quality data in peer-reviewed literature.

119 ars of high-resolution aerial monitoring and water quality data to elucidate the patterns and drivers

120 Microbiological measurements, chemical water quality data, and dye tracer tests provide evidenc

121 High spatial resolution hydrological and water quality datasets indicate that metal-rich groundwa

122 This study quantified the extent of water quality degradation across lake types at a nationa

123 To understand water quality degradation during hypoxia, we need to und

124 ncreased in 52 watersheds with no consistent water-quality degradation.

125 edox-sensitive processes) that could improve water quality during managed recharge.

126 This study documents water quality during the September 2013 extreme flood in

127 that ASGM is fundamentally altering optical water quality dynamics of a critical tropical biodiversi

128 solar water purification system with assured water quality, especially for economically stressed comm

129 to conventional tillage (CT), its impact on water quality, especially nitrate (NO3(-)) loss remain c

130 applications such as metabolomic profiling, water quality evaluation, and fundamental research.

131 Assessment of water quality evolution in the thousands of existing and

132 Our results show that inadequate water quality exacerbates China's water scarcity, which

133 ovide critical information to policy makers, water quality experts, and risk assessment professionals

134 h) promoted rapid aggregation while improved water quality favored stability.

135 Unusual water quality findings such as low pH were observed that

136 mmit to identify options to improve drinking-water quality for N.C. residents served by private wells

137 e been used as a proxy for faecal matter and water quality from a variety of environments.

138 thmandu Valley, there is high variability of water quality from different sources, including for trea

139 propose that a reduced hydroperiod and lower water quality from reduction in water level and flow lim

140 11.3%) was then used to evaluate the product water quality from the large-scale DCMD treatment of oil

141 (DBP) formation are necessary for predicting water quality from the treatment plant to the tap.

142 o meet global, national, regional, and local water quality goals effectively and comprehensively.

143 ons to water utilities to strategically meet water quality goals while reducing energy demands.

144 Water quality guidance values for Legionella are availab

145 ed this method to calculate climate-adjusted water quality guideline values (GVs) for two reference t

146 ns to the Australian and New Zealand default water quality guideline values (WQGVs) showed no marine

147 In contrast, drinking water quality guidelines are defined: water must be "fre

148 Water quality guidelines for any single chemical or suit

149 Chloride can be toxic, and water quality guidelines have been created to regulate i

150 ssments and in the development of regulatory water quality guidelines in Europe, and in 2007 the Unit

151 ic marine species using methods adapted from water quality GV derivation.

152 PAF method enabled the adjustment of current water quality GVs to account for thermal stress events.

153 ge, while child weight-for-age and household water quality had nonlinear relationships that leveled o

154 Excessive nitrogen runoff leads to degraded water quality, harming human and ecosystem health.

155 LAGOS-NE was used to quantify whether lake water quality has changed from 1990 to 2013, and whether

156 While degraded water quality has long been known to influence underwate

157 counterparts in an effort to understand the water quality impacts of Harvey on the natural water sys

158 Results show persistent secondary water quality impacts related to the biodegradation of m

159 Yet, these water quality impacts that affect both human and natural

160 ed as key factors affecting short-term acute water quality impacts.

161 past several decades have led to widespread water quality impairments across the U.S.

162 od extent mapping method, examined potential water quality implications of two "500-year" hurricanes

163 ting additional climate warming in this way, water quality improvements appear to have offset recent

164 These results suggest that water quality improvements, as well as other types of ec

165 ecreased in 91 watersheds with no consistent water-quality improvements, and balances increased in 52

166 face waters have not resulted in significant water-quality improvements.

167 to be able to rapidly and accurately measure water quality in a cost-effective manner using e.g., a t

168 to test alternative hypothesized controls on water quality in a pit lake over approximately 8 years.

169 Improving stream water quality in agricultural landscapes is an ecologica

170 However, it is unclear whether or how water quality in lakes across diverse ecological setting

171 pounds reflects nutrient loss and influences water quality in large rivers.

172 e impact of Hurricane Maria (HM) on drinking water quality in Puerto Rico (PR) by integrating targete

173 be a useful analytical tool for screening of water quality in resource limited settings.

174 Degradation of coastal water quality in the form of low dissolved oxygen levels

175 A major challenge for assessment of water quality in tropical environments is the natural oc

176 ts suggest that flushing can quickly improve water quality in unoccupied buildings, but the improveme

177 respective amphibian tissues due to varying water quality in urban and agricultural ponds.

178 Using a composite water quality index, we find that while reefs exposed to

179 quantity indicators, and inconsistently met water quality indicators.

180 < 0.05), a result supporting their roles as water quality indicators.

181 laria, HIV, schistosomiasis, sanitation, and water-quality indicators.

182 A gradient-boosted classifier with seven water quality inputs was comparable in detecting microcy

183 As water quality is affected by eutrophication, algal commu

184 Water quality is assessed via traditional microbial indi

185 These findings show that improved water quality is attainable with sustained reversal of n

186 Information about microbial water quality is critical for managing water safety and

187 European legislation focusing on water quality is expected to broaden to encompass severa

188 r or longer recovery time for Gulf of Mexico water quality is highly uncertain, and that much shorter

189 Unlike public water systems, private well water quality is not monitored, and there are few studie

190 Although public water quality is regulated through the Safe Drinking Wat

191 Water quality is undergoing significant deterioration du

192 n water resistome is a topic of interest for water quality, mainly under re-use and One-Health perspe

193 ew viral-based assays could become important water quality management and research tools.

194 of nutrient removal efficiencies to support water quality management and urban farming.

195 loom magnitude, information that would guide water quality management decisions.

196 s-and how this may potentially affect future water quality management decisions.

197 Our findings support calls for water quality management efforts to better account for t

198 It is therefore imperative that water quality management strategies account for the impa

199 o integrate a broader perspective into local water quality management, in the Chesapeake Bay and in t

200 r assessing potential impacts and developing water-quality management strategies associated with this

201 th seasonal and climatic factors, additional water quality measures, and treatment data may enhance p

202 implications on the space and time scales of water quality mitigation efforts.

203 waters, as well in watershed-scale microbial water quality modeling.

204 sensing methods enabling sensitive and rapid water quality monitoring are needed.

205 In this study, a water quality monitoring buoy was outfitted with an auto

206 ndwater contamination and improved long-term water quality monitoring compared solely to isotopic and

207 complements to chemical analyses in standard water quality monitoring efforts would allow for more co

208 Microbial water quality monitoring is crucial for managing water r

209 potential to increase the ease and reach of water quality monitoring of trace contaminants.

210 data from any remote location to the central water quality monitoring station.

211 ising for the development of simple low-cost water quality monitoring system for monitoring of BPA in

212 approach shows promise for rapid and direct water quality monitoring to provide a holistic assessmen

213 The utility of in vitro assays in water quality monitoring was evident from both the quant

214 ies are required, for instance, in medicine, water quality monitoring, and the food industry.

215 able selective water pollutant detection for water quality monitoring.

216 S) based sensor is developed for sub-surface water quality monitoring.

217 ld-deployable molecular diagnostic tools for water quality monitoring.

218 water wells that may be targeted for further water-quality monitoring.

219 upling climate projections with a hydrologic/water quality network model of the contiguous United Sta

220 gressive nutrient reduction goals to achieve water quality objectives for the Chesapeake Bay estuary.

221 bility, requiring multiple processes to meet water quality objectives.

222 Here we use a combination of water-quality observations and simulated nitrogen discha

223 and management efforts over recent decades, water quality of lakes in the Midwest and Northeast U.S.

224 the respective WWTP but also influenced the water quality of one of Europe's most important river sy

225 g storms with potential implications for the water quality of receiving water bodies.

226 as nutrient pollution sources could improve water quality outcomes, while allowing cities to enjoy t

227 of environmental risk factors and microbial water quality over large geographical scales.

228 ns at finer spatial scales to remediate poor water quality owing to periphyton growth.

229 tter-explained the short-term variability in water quality parameters and bacterial community composi

230 linear regression analyses prioritized three water quality parameters linked to agricultural and deve

231 Samples were tested for general water quality parameters, conventional and sewage-associ

232 ere not explained by faster growth, measured water quality parameters, or innate immune enzyme activi

233 aily measurements of weather, hydrology, and water quality parameters, to generate a novel data set w

234 opportunistic bacteria, and improvements to water quality parameters.

235 firmed the importance of both phages as main water quality parameters.

236 gh concentrations and suggests impairment of water quality, particularly since 2011.

237 GeoNet was used on data in the Water Quality Portal for the Pennsylvania Marcellus regi

238 th either fluorescence spectra or a suite of water quality predictors as inputs.

239 clining globally as climate change and local water quality press environmental conditions beyond the

240 nities growing on biofilters affect filtered water quality primarily through the biotransformation of

241 g sewage physicochemical properties, using a water-quality probe, flow volume, catchment population,

242 limatic and human effects strongly influence water-quality properties in estuarine-coastal ecosystems

243 c effects; (2) to assess long-term trends of water-quality properties reflecting degradation and reco

244 ely explain high inter-annual variability of water-quality properties, requiring adjustments to resol

245 nding suggests that adequate investments for water-quality protection and water-use efficiency can pr

246 ventional drinking waters as a benchmark for water quality receiving regulatory and widespread public

247 future scenarios for several contributions: water quality regulation, coastal risk reduction, and cr

248 ting a progressive populace facing stringent water quality regulations) were interviewed.

249 cts of Fe(2+)-catalyzed recrystallization on water quality requires knowing the time scale over which

250 One factor that can help explain the lack of water-quality response is remobilization of accumulated

251 in other settings to predict weathering and water quality responses to climate change.

252 ected areas, catchment management to improve water quality), restoration, as well as global and natio

253 shwater mussels are sensitive to habitat and water quality, revealing the fastest rates of human-medi

254 portance of these compounds to final product water quality, samples were collected from six potable w

255 merous observational studies have shown that water quality, sanitation, and handwashing (WASH) in a h

256 Integration of improved water quality, sanitation, and handwashing could contrib

257 Despite improvements in water quality, sanitation, and hygiene, as well as in th

258 Improving water quality, sanitation, handwashing, and nutrition co

259 We evaluated the effects of water quality, sanitation, handwashing, and nutrition in

260 actors include poor nutrient intake and poor water quality, sanitation, or hygiene.

261 e membrane aerated bioreactor with real-time water quality sensors was used to treat household greywa

262 We find that the critical surface-water quality standard (1.0 milligrams of nitrogen per l

263 n concentrations of chloride that can exceed water quality standards intended to protect aquatic life

264 ave adopted BLM-based Cu criteria into their water quality standards on a state-wide basis, which app

265 Therefore, the development of water quality standards would benefit by including mesoc

266 ompounds are possible candidates for further water-quality studies in watersheds affected by wildfire

267 y developed countries with a strong focus on water quality, such as Switzerland.

268 y framework and uncertainty in treatment and water quality targets are barriers to wide-scale adoptio

269 We found that a microbial water quality test costs 21.0 +/- 11.3 USD, on average,

270 Because the economics of water quality testing are poorly understood, the extent

271 n scientists and compared their results from water quality testing of water samples to results obtain

272 detected as part of standard microbiological water quality testing.

273 ations, household surveys, focus groups, and water quality testing.

274 scenario, might provide better control over water quality than the status quo conditions.

275 efits provided to people, and potentially to water quality through reduction of stormwater volume by

276 Major floods adversely affect water quality through surface runoff, groundwater discha

277 mmunities in biofilters can improve drinking water quality through the biodegradation of dissolved co

278 tudies indicate that zooplankton may improve water quality through viral uptake or may serve as vecto

279 ogic model of anthropogenic impacts to urban water quality to include exchange with the subsurface.

280 racterize how a user's prior experience with water quality tools was associated with the accuracy of

281 by citizen scientists using rapid assessment water quality tools, and (2) to characterize how a user'

282 inant concentrations when using colorimetric water quality tools.

283 We quantified water quality trends in 2913 lakes using nutrient and ch

284 tect anomalies caused by technical errors in water-quality (turbidity and conductivity) data collecte

285 lls/particles in large dilute samples (e.g., water quality, urine analysis), or high-throughput scree

286 cted and evaluated the "best" model for each water-quality variable, environment, and anomaly type.

287 n to 45 million people have been affected by water quality violations in each of the past 34 years.

288 We estimate the change in sales due to water quality violations, using a panel dataset of weekl

289 Improved water quality was coincident with a 2013 bird exclusion

290 results indicate that point of use drinking water quality was impacted by conditions in the source w

291 erformance of high salt removals and product water quality was maintained in three repeated semibatch

292 ved empirical knowledge of the links between water quality, water level fluctuations, and emissions a

293 Child growth and water quality were not associated with individual househ

294 h well/hauled water accurately predict their water quality, while those with treated+piped water tend

295 step to reducing nitrogen load and improving water quality will be containment and careful management

296 onditions, we find that 6-17% improvement in water quality will be necessary to bring recovery rates

297 Tests on water samples indicated good water quality with low levels of fecal indicator bacteri

298 The energy needed to maintain suitable water quality, with associated emissions, has however be

299 esigned to reduce eutrophication and improve water quality, WWTPs increasingly release a multitude of

300 rm of Pb in drinking water in the Pequannock water quality zone of Newark.