ライフサイエンスコーパス: municipal

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

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

3 sing the electronic database of the regional municipal administration registrations.

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

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

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

7 e reservoir for these outbreaks is generally municipal and (often separate) hospital water supplies.

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

9 were compared using simulated FOB waste from municipal and commercial sources.

10 others are incredibly hardy, able to grow in municipal and distilled water, thrive at temperatures of

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

12 be found in waste biomass from agricultural, municipal and industrial sources as well as in dedicated

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

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

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

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

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

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

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

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

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

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

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

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

25 yptosporidiosis outbreak was associated with municipal drinking water, despite state-of-the-art water

26 Municipal effluent discharged from wastewater treatment

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

28 s from waters with a high content of treated municipal effluent were observed in both ESI modes and a

29 2 efficiently degrade EE2 in pure lab water, municipal effluents and EE2-spiked synthetic urine.

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

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

32 Civil servants and municipal employees in Israel (n=9734 men; age, >/=42 ye

33 rforming various duties were obtained from a municipal fire department, from 17 large metropolitan fi

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

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

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

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

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

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

40 s infection in the tumor registry at a large municipal hospital in New York City between 1994 to 1997

41 nee OA from the general medicine clinic of a municipal hospital were assigned arbitrarily to conditio

42 ospital charges for patients with AC at this municipal hospital.

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

44 horticulture, in the removal of ammonia from municipal, industrial, and agricultural waste and drinki

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

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

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

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

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

50 for control of Legionnaires' disease at the municipal level or in individual hospitals, and widespre

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

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

53 Technological developments in municipal lighting are altering the spectral characteris

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

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

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

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

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

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

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

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

62 Use of bottled water (vs. municipal or spring/well water) and years of maternal se

63 e screening survey, and 1264 officers from a municipal police department and a state police departmen

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

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

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

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

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

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

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

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

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

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

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

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

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

77 who attended the San Francisco, California, municipal sexually transmitted disease clinic between 19

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

79 1994, and April, 1996, women who attended a municipal sexually transmitted diseases (STDs) clinic in

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

99 as done among female sex workers attending a municipal STD clinic in Mombasa, Kenya.

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

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

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

103 1.9-2.2), suicidal behaviors, mortality, and municipal support.

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

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

106 At our municipal teaching hospital, 418 patients who had out-of

107 all cardiac arrests transported to a single, municipal teaching institution was performed.

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

109 They break down pollutants, municipal waste and ingested food, and they are the prim

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

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

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

113 ioxins and -furans (PCDDs/Fs) emissions from municipal waste combustors (MWCs) and other stationary s

114 Municipal Waste Incineration (MWI) is regulated through

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

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

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

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

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

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

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

122 icultural and forestry residues, portions of municipal waste, and herbaceous and woody crops, is fina

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

124 l full-scale applications for industrial and municipal waste-water treatment.

125 or the environmentally friendly recycling of municipal waste.

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

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

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

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

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

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

132 omposition or bypass biological treatment of municipal wastewater are released into surface waters an

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

134 Municipal wastewater collected in areas with moderate cl

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

176 In particular, many municipal wastewater treatment plant chlorinated effluen

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

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

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

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

181 .5 mum) mass in primary effluent (PE) from a municipal wastewater treatment plant.

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

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

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

185 Municipal wastewater treatment plants (WWTPs) could be a

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

187 blems if the limited management resources of municipal wastewater treatment plants are regarded.

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

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

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

191 ted on chlorinated effluents discharged from municipal wastewater treatment plants.

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

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

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

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

196 ogically stabilize wasted solids produced in municipal wastewater treatment.

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

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

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

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

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

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

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

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

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

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

207 For municipal wastewater-impacted river water, the presence

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

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

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

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

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

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

214 onsumers of vegetable irrigated with treated municipal wastewater.

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

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

217 roundwater aquifers via the reuse of treated municipal wastewater.

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

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

220 ter in ditches surrounding poultry farms and municipal wastewater.

221 receive measurable contributions of treated municipal wastewater.

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

223 es (detected using a low-cost MST method) in municipal wastewaters (MW) and assesses whether they may

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

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

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

227 removing EE2 and other pharmaceuticals from municipal wastewaters.

228 dvanced oxidation process for industrial and municipal wastewaters.

229 minants are commonly found in industrial and municipal wastewaters.

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

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

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

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

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

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

236 th risks from contaminated water or possibly municipal water supplies which, when chlorinated, may pr

237 In March 1993, the municipal water supply in Milwaukee became contaminated

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

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

240 ironment can enter the groundwater supply of municipal water systems, at which point their removal is

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

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

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

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

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

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

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

248 ers, firefighters, construction workers, and municipal workers.

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

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

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

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

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

254 Discharges from three municipal WWTPs were primarily responsible for elevated

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