ライフサイエンスコーパス: municipal

1 e geographic levels: national, regional, and municipal.

2 The sectoral E4W allocation includes municipal (45%), industrial (30%), and agricultural (25%

3 Municipal ACCWW% at drinking water treatment plant surfa

4 p book system for use in urban slums with no municipal address systems, where classification has been

5 During this time period, the mean crude municipal adult mortality rate increased by 8.0% from 14

6 This study is limited by the use of municipal-aggregate data, which precludes individual-lev

7 In 2018 it was detected that employees at a municipal airport in northern Sweden had been exposed to

8 second, lower-risk group, was recruited from municipal alcohol rehabilitation centers and the Danish

9 Outcomes were municipal all-cause and cause-specific mortality rates f

10 poultry litter (PL), PL-fertilized soil, and municipal anaerobic sludge.

11 ave serious implications for the hydropower, municipal and agricultural sectors in the region.

12 +/- 59 million people, or most of the annual municipal and industrial needs of Pakistan, Afghanistan,

13 of 136 million people, or most of the annual municipal and industrial needs of Pakistan, Tajikistan,

14 Reuse of municipal and industrial wastewater treatment plant (WWT

15 exposed to engineered nanoparticles through municipal and industrial wastewater-effluent discharges

16 otal influenza incidence are produced at the municipal and state level in the United States.

17 semiarid climate with competing agriculture, municipal, and industrial water demands was one of the f

18 ed avoidance of certain route types (county, municipal, and US routes).

19 outbreak occurred in cats in New York City's municipal animal shelters.

20 In 2004, municipal authorities in Medellin, Colombia, built a pub

21 in edible compartments of crops grown in the municipal biosolids-amended soil and in the control soil

22 ustrially impacted biosolids-amended soil, a municipal biosolids-amended soil, and a control soil was

23 ustrially impacted biosolids-amended soil, a municipal biosolids-amended soil, and a control soil.

24 ustrially impacted biosolids-amended soil, a municipal biosolids-amended soil, and two AFFF-impacted

25 Analysis of effluent samples from a range of municipal BNR plants (total DON concentrations ranging f

26 We observed larger reductions in municipal childhood pneumonia mortality in all three age

27 tions: how much farmland can be applied with municipal compost and what percentage of the diverted or

28 coli inactivation by peracetic acid (PAA) in municipal contact tanks fed by secondary settled wastewa

29 n (BCPE) aimed to achieve 90-90-90 in Bukoba Municipal Council, Tanzania, by scaling up new HIV testi

30 genetic analyses performed on a local level (municipal, county, or state), with results communicated

31 er (surface/groundwater) losses, compared to municipal drinking water and well water.

32 e collected recent annual mean THM levels in municipal drinking water in 28 European countries (EU28)

33 stribution distance and no pump) outperforms municipal drinking water in all environmental impact cat

34 The two municipal drinking water systems of New Orleans, LA, U.S

35 Municipal effluent discharged from wastewater treatment

36 ical chemicals can represent constituents of municipal effluent outflows that are dispersed into aqua

37 2 efficiently degrade EE2 in pure lab water, municipal effluents and EE2-spiked synthetic urine.

38 inants of emerging concern (CECs) in treated municipal effluents have the potential to adversely impa

39 een truth-telling and reelection in the next municipal elections, which suggests that dishonesty migh

40 d in the Finnish Longitudinal Study on Aging Municipal Employees (FLAME) in 1981 and were followed up

41 es, and leaks and spills from industrial and municipal facilities.

42 o reuse increased for 17 of the 25 DWTPs, as municipal flows upstream of the sites increased by 68%.

43 of organized trash collection and high-level municipal functioning on a city-wide scale.

44 his case study demonstrate the potential for municipal government to use a combination of cooperative

45 the association of AOD to PM2.5 daily using municipal ground monitors, land use, and meteorological

46 al Science Foundation of China, and Shanghai Municipal Health and Family Planning Commission.

47 ective cohort study of 434,646 patients in a municipal health care system.

48 in 72 baranguays (villages) serviced by six municipal health centres in a schistosomiasis endemic re

49 der, age, distance to the hospital and local municipal health structure were evaluated as possible ba

50 741 images from 154 patients; and the Weihai Municipal Hospital, Shandong, 11 039 images from 1420 pa

51 a (CML) patients has migrated extensively to municipal hospitals (MHs) and office-based physicians (O

52 ics from different wastewater sources (e.g., municipal, hospitals, animal production, and pharmaceuti

53 ricultural use and "heavy" (i.e., commercial/municipal/industrial) use.

54 ir breakdown between household subsidies and municipal infrastructure varied greatly between sanitati

55 nsit-oriented development was accompanied by municipal investment in neighborhood infrastructure.

56 tored over 5 months (February-June, 2010) in municipal landfill leachate.

57 Sediments were collected from the Dover Municipal Landfill Superfund site.

58 t and selection of heating systems or at the municipal level for designing district heating networks.

59 credit created cross-party alliances at the municipal level.

60 to pre-ESF trends and the inclusion of other municipal-level factors that could be associated with co

61 address these gaps in knowledge by combining municipal-level panel data on diseases, public health se

62 Technological developments in municipal lighting are altering the spectral characteris

63 We identified 41 unique businesses and municipal location types with >/=20 locations in Toronto

64 We identified and ranked businesses and municipal locations by spatiotemporal OHCA risk in their

65 We aim to identify specific businesses and municipal locations that maximize OHCA coverage on the b

66 The businesses and municipal locations were then ranked by spatiotemporal O

67 ow if radon concentration is associated with municipal mortality due to brain cancer in Galicia, Spai

68 We correlated radon concentrations with municipal mortality due to these malignant tumors during

69 oundwater was sampled from private (n = 81), municipal (n = 34), and observation (n = 15) wells betwe

70 ning and received either bottled (n = 90) or municipal (n = 86) drinking water based on residence in

71 eplacement cost methodology and allocated by municipal nitrogen source.

72 We present a new municipal open waste burning emission inventory from Ind

73 hat brining is a highly viable BMP for local municipal operations.

74 m that aims at recovering nutrients from the municipal organic waste generated in the Spanish region

75 degree capable of compensating for delays in municipal policy making.

76 farm by immunoglobulin M seroprevalence in a municipal population sample.

77 The WWTPs sampled included two municipal, publicly owned treatment works and a commerci

78 ume changes to agricultural, industrial, and municipal pumping within the Tulare basin.

79 ore river water started to infiltrate due to municipal pumping.

80 municipality and correlated this value with municipal radon concentration using Spearman's Rho.

81 35 883 households were selected from municipal rolls using two-stage random sampling stratifi

82 far exceed regulatory limits for disposal in municipal sanitary landfills and require careful monitor

83 suggest that observation and forecast at sub-municipal scales within New York City provides richer, m

84 ovirus (MNV) by PFA, in phosphate buffer and municipal secondary effluent wastewater, are reported fo

85 Chinese hamster ovary (CHO) cells induced by municipal secondary wastewater effluent amended with ele

86 n roof, and permeable pavement) versus gray (municipal separate stormwater sewer systems, MS4) altern

87 We explore the use of municipal service requests (also known as "311" requests

88 id oil and gas development with overburdened municipal services, upended social and cultural patterns

89 alpha-ethinylestradiol (EE2), are present in municipal sewage discharges.

90 ., pyrolysis) and hydrothermal treatments of municipal sewage sludge using complementary chemical ext

91 Thermo-chemically treated municipal sewage sludge, as well as diatomaceous earth,

92 hates, biochar, ash, diatomaceous earth, and municipal sewage sludge.

93 nal policy to reduce MPs in the effluents of municipal sewage treatment plants (STPs).

94 er nanoparticles (Ag-NP) discharged into the municipal sewer system largely accumulate in the sewage

95 At the municipal sexually transmitted disease clinic in Seattle

96 ed from symptomatic males at San Francisco's municipal sexually transmitted disease clinic, a partici

97 actions between unemployment and terciles of municipal social protection and health-care expenditure

98 ments taken at additional time points in the municipal soil were used to model the kinetics of uptake

99 tory-scale anaerobic bioreactors filled with municipal solid waste (MSW) and operated over 273 days.

100 Dry anaerobic digestion (AD) of organic municipal solid waste (MSW) followed by composting of th

101 Open-burning of municipal solid waste (MSW) is a major source of PM emis

102 Up to 30% of the municipal solid waste (MSW) that is incinerated for ener

103 d the production of saleable byproducts from municipal solid waste (MSW).

104 used as substrates: the organic fraction of municipal solid waste (OFMSW) and supermarket food waste

105 ic pollution, we modeled stocks and flows of municipal solid waste and four sources of microplastics

106 SWNT transport through a packed-bed of mixed municipal solid waste collectors.

107 cade decrease in Hg emissions primarily from municipal solid waste combustors and, secondarily, from

108 uncertainty in gas collection efficiency and municipal solid waste fraction on optimal k values and c

109 e aggregate proportion of food waste in U.S. municipal solid waste from 1995 to 2013 was found to be

110 nterest in diverting the organic fraction of municipal solid waste from landfills to biological treat

111 Food waste makes up approximately 15% of municipal solid waste generated in the United States, an

112 sed as the primary means for the disposal of municipal solid waste in Canada.

113 uring ENM agglomeration and sedimentation in municipal solid waste incineration landfill leachates ov

114 ompeting management alternatives for organic municipal solid waste including landfilling, composting,

115 Mixed color waste glass extracted from municipal solid waste is either not recycled, in which c

116 ces (PFAS)-contaminated wastewaters, such as municipal solid waste landfill leachates, pose a challen

117 the largest domestic CH4 emissions sources: municipal solid waste landfills, oil and natural gas, co

118 to estimate the global warming impacts from municipal solid waste landfills.

119 their useful life, they will be discarded in municipal solid waste landfills.

120 of butanol and ethanol production from mixed municipal solid waste to demonstrate the challenges in u

121 nt feedstocks (dairy manure, food waste, and municipal solid waste).

122 st plastic and is the largest contributor to municipal solid waste.

123 noparticles (PVP-AgNPs) on the composting of municipal solid waste.

124 Food waste is a major constituent in municipal solid wastes and its accumulation or disposal

125 ge dominates shallow groundwater inputs with municipal sources contributing only 13-29% of discharge.

126 augmentation were isolated from full-scale, municipal SSFs so as to optimize survival in the laborat

127 rent population living on endangered land at municipal, state, and national levels within the United

128 gs may not be cost-effective compared to the municipal supplies over their lifetime, except in Seattl

129 cation, relies heavily on imported water for municipal supply, and has come under regulatory scrutiny

130 , were also noted as well as the use of more municipal support, sick leave benefits, and disability p

131 1.9-2.2), suicidal behaviors, mortality, and municipal support.

132 ped to evaluate alternatives for residential municipal SWM, which included combinations of a mixed wa

133 Clinicians should be aware of municipal tap water as a potential cause of methemoglobi

134 s were collected from 3 urban source waters (municipal tap water, streamwater, and wastewater treatme

135 sed the risk of CHIKV infection, whereas >=4 municipal trash collections/week (aRR, 0.38) and having

136 Treated and untreated wastewater from 20 municipal treatment plants in the East of England, Unite

137 ations by the Oita University and the Nagoya Municipal University in Japan, which focused on the rese

138 times the yearly energy needs of the city's municipal vehicle fleet.

139 arge high pressure (HP) boilers operating in municipal waste and recycling facilities to prevent corr

140 Results show that municipal waste biogas contained elevated levels of chem

141 by mechanical-biological treatment (MBT) of municipal waste can replace fossil fuels, being a CO(2)-

142 The boiler exit flue gas of a municipal waste combustor was sampled to evaluate an onl

143 Municipal Waste Incineration (MWI) is regulated through

144 s rivers revealed that chemical industry and municipal waste incinerators are the most important brom

145 n WWTPs with specific bromide sources (e.g., municipal waste incinerators, landfill leachate, and che

146 es and (ii) the amounts needed to expand the municipal waste management infrastructure for unserved p

147 ss beads and was then applied to a composted municipal waste sample with spike recoveries ranging fro

148 The results from municipal waste samples and soil samples collected from

149 Chemical analyses showed that for the municipal waste samples Ca and Al were present in higher

150 e the first known estimate of available U.S. municipal waste stocks (8.5 billion tonnes) and go on to

151 dder light fraction, which is incinerated in municipal waste treatment plants mainly in Switzerland;

152 WIPs) with different input materials such as municipal waste, wood and sewage sludge.

153 ation has long been used for disinfection of municipal wastewater (MWW) effluent while the use perace

154 on processes (AOPs) in advanced treatment of municipal wastewater (WW) to be reused for crop irrigati

155 icant fraction is eventually discharged with municipal wastewater (WW).

156 s efforts to identify specific precursors in municipal wastewater accounting for N-nitrosamine format

157 produce effluent suitable for anammox, real municipal wastewater after anaerobic pretreatment was tr

158 tants and shows that micropollutants in both municipal wastewater and stormwater can be relevant sour

159 Utilities incorporating the potable reuse of municipal wastewater are interested in converting from t

160 Although the recycling of municipal wastewater can play an important role in water

161 Municipal wastewater collected in areas with moderate cl

162 quantified, which are clearly above typical municipal wastewater concentrations; and (iii) a pharmac

163 n the United States, and it is possible that municipal wastewater could be a reservoir of this microo

164 are located downstream of poultry farms and municipal wastewater discharge points.

165 Alternatively, municipal wastewater effluent can be used, but this rest

166 in water sources impacted by algae bloom and municipal wastewater effluent discharge.

167 Reverse osmosis (RO) treatment of municipal wastewater effluent is becoming more common as

168 of advanced treatment technologies to treat municipal wastewater effluent to meet existing drinking

169 ed groundwater, simulated surface water, and municipal wastewater effluent) as well as a sodium chlor

170 an antibiotic that is frequently detected in municipal wastewater effluent, nitrate and nitrite-sensi

171 were used to predict contaminant removal in municipal wastewater effluent.

172 an open-water unit process wetland receiving municipal wastewater effluent.

173 pilot-scale wetland cell receiving nitrified municipal wastewater effluent.

174 is to remove trace organic contaminants from municipal wastewater effluent.

175 n data from open-water wetlands that treated municipal wastewater effluent.

176 y contrast media (ICM) have been detected in municipal wastewater effluents at relatively high concen

177 ion is effective in improving the quality of municipal wastewater effluents by eliminating organic mi

178 eated (HTP) or advanced primary-treated (PL) municipal wastewater effluents containing CECs.

179 micropollutants was observed in 10 secondary municipal wastewater effluents spiked with 16 micropollu

180 iency of micropollutants during ozonation of municipal wastewater effluents with varying water qualit

181 idation (MF/RO/AOP) for the potable reuse of municipal wastewater effluents, but their effluent quali

182 tor in humans, and this drug is prevalent in municipal wastewater effluents.

183 samples, 9 stormwater runoff samples, and 12 municipal wastewater effluents.

184 se of the array was also confirmed in spiked municipal wastewater effluents.

185 Autotrophic nitrogen removal from municipal wastewater enables development of energy autar

186 The tapping of municipal wastewater for potable reuse significantly enh

187 show the utility of viral RNA monitoring in municipal wastewater for SARS-CoV-2 infection surveillan

188 F-FOMBR) for direct phosphorus recovery from municipal wastewater in the course of its treatment.

189 t and continuous-flow field tests using real municipal wastewater indicated that the S-ISM nitrogen s

190 examined include different nutrient sources (municipal wastewater influent to the activated sludge pr

191 nt, especially in arid regions where treated municipal wastewater is extensively reused.

192 esented in bloodstream, hospital sewage, and municipal wastewater isolates.

193 of sewage sludge, by irrigation with treated municipal wastewater or by manuring.

194 tewater and reverse osmosis concentrate from municipal wastewater recycling due to the high conductiv

195 Drug concentrations in composite municipal wastewater samples and census-based estimates

196 phorus from iron-phosphorus rich wastes like municipal wastewater sludge.

197 (ARGs) are discharged with treated residual municipal wastewater solids and subsequently applied to

198 uce ARG and intI1 concentrations in residual municipal wastewater solids within timeframes typical of

199 stance gene (ARG) concentrations in residual municipal wastewater solids.

200 hosphorus (P) recovery from agricultural and municipal wastewater streams has intensified.

201 ry in four centralized and two decentralized municipal wastewater systems were compared using life cy

202 Twenty TOrCs were detected in the municipal wastewater that was used as feed to the UFO-MB

203 ed oxidation processes (AOPs) used to purify municipal wastewater to potable quality have difficulty

204 ake water, river water, and effluents from a municipal wastewater treatement plant and a treatment we

205 ch suggests that the design and operation of municipal wastewater treatment facilities with the expli

206 robial fuel cells (MFCs) were installed in a municipal wastewater treatment facility and operated for

207 e monitoring of human pathogenic bacteria in municipal wastewater treatment is important not only for

208 c acid (PAA) is an emerging disinfectant for municipal wastewater treatment owing to good biocidal ef

209 reatment able to degrade micro pollutants in municipal wastewater treatment plant (MWTP) effluents at

210 s, in hospital wastewaters, river water, and municipal wastewater treatment plant (WTP) influents and

211 hormone, 17alpha-ethinylestradiol (EE2), in municipal wastewater treatment plant (WWTP) activated sl

212 discharges from pharmaceutical production in municipal wastewater treatment plant (WWTP) effluents an

213 atural and synthetic organic contaminants in municipal wastewater treatment plant (WWTP) effluents ca

214 dge was sampled from an anoxic selector of a municipal wastewater treatment plant (WWTP), and PHB-con

215 samples collected upstream and downstream of municipal wastewater treatment plant discharges in three

216 Use of reclaimed water-municipal wastewater treatment plant effluent-in nonpota

217 Our model integrates data on power plant and municipal wastewater treatment plant operations into a c

218 was determined in unspiked wastewater from a municipal wastewater treatment plant, but no iopromide a

219 .5 mum) mass in primary effluent (PE) from a municipal wastewater treatment plant.

220 ale plant treating secondary effluent from a municipal wastewater treatment plant.

221 ne sites at varying distances from two major municipal wastewater treatment plants (MWWTPs) (Waterloo

222 pting compound (EDC) removal is desirable in municipal wastewater treatment plants (MWWTPs) although

223 Intersex in fish downstream of municipal wastewater treatment plants (MWWTPs) is a glob

224 Municipal wastewater treatment plants (WWTPs) could be a

225 Integrating microalgae systems (MAS) at municipal wastewater treatment plants (WWTPs) to produce

226 d sewage sludge and effluent samples from 64 municipal wastewater treatment plants as well as in majo

227 tal nitrogen discharged to surface waters by municipal wastewater treatment plants designed for biolo

228 97 meat products, the hospital sewer, and 20 municipal wastewater treatment plants in the East of Eng

229 t coastal waters affected by discharges from municipal wastewater treatment plants.

230 ed to treat the residual solids generated at municipal wastewater treatment plants; there is very lit

231 estic wastewater promotes a more sustainable municipal wastewater treatment system.

232 oxygen (DO) concentrations), two full-scale municipal wastewater treatment systems applying oxidatio

233 iling approach toward nitrogen management in municipal wastewater treatment was to remove ammonium by

234 In contrast to these findings at the municipal wastewater treatment, both parental fipronil a

235 ogically stabilize wasted solids produced in municipal wastewater treatment.

236 acted intakes contained less than 1% treated municipal wastewater under average streamflow conditions

237 ere caught from a lake that receives treated municipal wastewater via a small river.

238 Sixteen urban waterways and municipal wastewater were sampled for fipronil, its envi

239 th parallel bench-scale AS reactors treating municipal wastewater with estrogens at 100-300 ng/L conc

240 ferent steroids occurred in hospital and raw municipal wastewater, but they were low (lower than 1 ng

241 can metabolize various waste streams (e.g., municipal wastewater, carbon dioxide from industrial flu

242 organic matter (EfOM), contained in treated municipal wastewater, differs in composition from natura

243 e of bromide ion, as is often encountered in municipal wastewater, hypobromous acid generated through

244 e most commonly used peracid disinfectant of municipal wastewater, peracetic acid (PAA), the ICT requ

245 ronmentally relevant mycobacteria in treated municipal wastewater, suggesting the need for vigilant m

246 sequencing batch reactor treating synthetic municipal wastewater, we observed stable and near-comple

247 For municipal wastewater-impacted river water, the presence

248 onsumers of vegetable irrigated with treated municipal wastewater.

249 he presence and fate of enveloped viruses in municipal wastewater.

250 roundwater aquifers via the reuse of treated municipal wastewater.

251 ceiving water bodies with a high fraction of municipal wastewater.

252 ure, on the anaerobic digestion of synthetic municipal wastewater.

253 ter in ditches surrounding poultry farms and municipal wastewater.

254 receive measurable contributions of treated municipal wastewater.

255 FP) from a membrane bioreactor used to treat municipal wastewater.

256 umer products are likely to be released into municipal wastewater.

257 d trace organic chemical (TOrC) removal from municipal wastewater.

258 sludge from a pilot-scale facility treating municipal wastewater.

259 hort of its goal to recycle 1,000,000 AFY of municipal wastewater.

260 on, whereas 900 min were required in treated municipal wastewater.

261 ent nitrogen removal from the main stream of municipal wastewater.

262 ed treatment trains for the potable reuse of municipal wastewater.

263 Despite widespread recognition that municipal wastewaters contain natural and synthetic estr

264 hen the EMR was applied for the treatment of municipal wastewaters with real environmental concentrat

265 gae Chaetomorpha linum in different types of municipal wastewaters, their ability to remove nutrient

266 minants are commonly found in industrial and municipal wastewaters.

267 removing EE2 and other pharmaceuticals from municipal wastewaters.

268 dvanced oxidation process for industrial and municipal wastewaters.

269 ir only shared exposures were consumption of municipal water and of ice that was mass-produced at the

270 ater resource in buildings, a combination of municipal water and rainwater is typically required to m

271 reen building following a transition between municipal water and rainwater.

272 These efforts were coordinated with the municipal water and sewage authority established to impr

273 l water treatment systems for industrial and municipal water and wastewater treatment.

274 nce of cryptosporidiosis between bottled and municipal water groups were compared using Poisson survi

275 runoff, groundwater discharge, and damage to municipal water infrastructure.

276 infectant byproducts served as indicators of municipal water remaining in the system since the rainwa

277 rculous mycobacteria (NTM) commonly colonize municipal water supplies and cause healthcare-associated

278 leri in household plumbing served by treated municipal water supplies and the first reports of PAM po

279 bution, and we apply it in the field to test municipal water supplies, demonstrating its potential us

280 water experiments carried out with the same municipal water supply.

281 likely caused by sewage contamination of the municipal water system.

282 extensive literature documents corrosion in municipal water systems, only minimal data is available

283 The efficacy of plastic particle removal by municipal water treatment plants is currently uncertain,

284 sing the air emission implications of common municipal water treatment processes used to comply with

285 ces in source water chemistry, rainwater and municipal water uniquely interacted with building plumbi

286 ndwater-based irrigation, and industrial and municipal water use, respectively.

287 e; population density, basic urban services (municipal water, electricity, and modern cooking-fuels a

288 a time series of virus samples from six deep municipal water-supply wells.

289 s were often three logs higher than those in municipal water.

290 th data from 3 mo to 5 y were collected from municipal well-baby clinics and linked to maternal HMO c

291 In this study, 16 monitoring wells and six municipal wells were repeatedly sampled for human enteri

292 io assumes the per capita water use rate for municipal withdrawals to remain at 2005 levels and the w

293 including fossil CO2, total GHG emission in municipal WRRFs increased 13%, and 23% if an on-site ene

294 esized that since the fossil carbon entering municipal WRRFs is mostly from soaps and detergents as d

295 ocarbon at different treatment points within municipal WRRFs, we verified that the fossil content cou

296 of target micropollutants in samples from a municipal WWTP in Switzerland.

297 lyzing the field-collected samples from nine municipal WWTPs in Germany, is the first to evaluate the

298 Discharges from three municipal WWTPs were primarily responsible for elevated

299 At two municipal WWTPs, both receiving wastewater from several

300 gher in the rural (70.2 +/- 9.8) than in the municipal zone (62.6 +/- 11.1), and was also significant