ライフサイエンスコーパス: wastewater

1 get 6.3: halving the proportion of untreated wastewater).

2 uantification limits were at 0.5-120 ng/L in wastewater.

3 que for degradation of organic pollutants in wastewater.

4 s within communities through the analysis of wastewater.

5 as well as the enhanced removal of PFOS from wastewater.

6 s produce an estimated 680 GL/yr of alkaline wastewater.

7 rated the efficiency of this system for real wastewater.

8 ic health status using biomarker analysis in wastewater.

9 plant material after irrigation with treated wastewater.

10 analysis of nine pharmaceuticals in treated wastewater.

11 al biotechnologies for nitrogen removal from wastewater.

12 e is known about the toxicity of the treated wastewater.

13 s for energy-efficient nitrogen removal from wastewater.

14 ) verification of stability of biomarkers in wastewater.

15 hich relies on the analysis of biomarkers in wastewater.

16 em can also be helpful for controlling urban wastewater.

17 f vegetable irrigated with treated municipal wastewater.

18 upply of chemicals, and potentially to treat wastewater.

19 iding a method to monitor public health from wastewater.

20 ing biological nitrogen removal processes in wastewater.

21 were measured for the first time in influent wastewater.

22 en removal from the main stream of municipal wastewater.

23 hat could be used to purify dye-contaminated wastewater.

24 nt trains for the potable reuse of municipal wastewater.

25 omarker due to its high stability profile in wastewater.

26 rom -0.80 to 4.05) from textiles, urine, and wastewater.

27 able water supplies by irrigating crops with wastewater.

28 ctive waste treatment is needed for hospital wastewaters.

29 ight separate substrates and three different wastewaters.

30 e commonly found in industrial and municipal wastewaters.

31 the bench-scale DCMD treatment of synthetic wastewaters.

32 ty in mammalian cells exposed to disinfected wastewaters.

33 d often ceases completely in slightly acidic wastewaters.

34 2O2) compared to previous studies using real wastewaters.

35 n (EU) (30 mg kg(-1)) and those in urine and wastewater (0.004-1.5 mug L(-1)) were at the level usual

36 ions were remarkably similar between the two wastewaters across O3/BAC conditions.

37 ffluent suitable for anammox, real municipal wastewater after anaerobic pretreatment was treated by e

38 ination of E. coli that may remain viable in wastewater after solar irradiation.

39 otic-resistant strain that was isolated from wastewater and carries the emerging NDM-1 antibiotic res

40 uated because stormwater systems differ from wastewater and drinking water systems to which LCA is mo

41 metabolite, sulfated PCMC, was confirmed in wastewater and in urine.

42 display huge potential for treating textile wastewater and other impaired effluents because of their

43 agulant was then reused for treating primary wastewater and overall coagulation efficiency was determ

44 droxypregnanolone, while mixtures that mimic wastewater and river water composition affected embryo d

45 lower bound of PFAS emissions estimates from wastewater and rivers may provide the best estimate of i

46 was used to detect beta-lactam resistance in wastewater and sewage and identified resistance in indiv

47 rimental data on virus inactivation rates in wastewater and similar matrices, we extracted data to co

48 s) derived from industry, landfill, domestic wastewater and stormwater.

49 ause algae aid phosphorus sequestration from wastewater and the thus enriched biomass may serve as or

50 Nitrate is a constituent of different wastewaters and can act as a competing electron acceptor

51 ystems (to halve the proportion of untreated wastewater), and existing system replacement, while also

52 roduction with combined N and P removal from wastewater, and it further suggests a putative denitrify

53 fully applied to hospital residues and urban wastewater, and the attained recoveries were between 90%

54 incorporating the potable reuse of municipal wastewater are interested in converting from the UV/H2O2

55 tobacco-related toxicants and carcinogens in wastewater are not available.

56 s the monitoring of phthalate metabolites in wastewater as a nonintrusive and economic alternative to

57 Target analytes were stable in wastewater at 4 and 20 degrees C over 24 h.

58 lations of the shredder Gammarus fossarum to wastewater at three field-relevant dilution levels (i.e.

59 treating wet flue gas desulfurization (FGD) wastewater at US CFPPs using the two best available trea

60 of daily drug consumption in urban areas in wastewater-based epidemiological assessments.

61 This can be achieved by wastewater-based epidemiology (WBE), which relies on the

62 d management, increasing water productivity, wastewater-based epidemiology and on-site water and wast

63 Wastewater-based epidemiology is an established approach

64 Wastewater-based epidemiology is an innovative approach

65 A key uncertainty of wastewater-based epidemiology is the size of the populat

66 prominent example for the emerging field of wastewater-based epidemiology.

67 The metals contained in wastewater biosolids played an important role in upgradi

68 Wastewater biosolids pyrolysis is a promising technology

69 A novel pyrolysis process using wastewater biosolids-derived biochar (WB-biochar) as a c

70 Agricultural use of treated wastewater, biosolids, and animal wastes introduces a mu

71 In wastewater, both E. coli strains decayed slower than the

72 l effectiveness of PAA and monochloramine in wastewater, but limited information is available for vir

73 roids occurred in hospital and raw municipal wastewater, but they were low (lower than 1 ng/L) or bel

74 Surface water discharges of O&G wastewater by centralized waste treatment (CWT) plants p

75 utralization and element removal in alkaline wastewaters by fermentation of organic carbon, using bau

76 A new compound detected in wastewater can be a potential biomarker of an emerging t

77 Harvesting energy from wastewater carbonaceous substrates can offset energy dem

78 ve evaluated their ability to remove organic wastewater compounds (OWCs) such as pharmaceuticals, hor

79 Millions of tons of wastewater containing both inorganic and organic polluta

80 antibiotic use, overcrowding, and inadequate wastewater containment.

81 Unfortunately, wastewater contains biologically active, long-lived phar

82 6000 ppm) chosen to simulate high industrial wastewater contamination.

83 The economic cleanup of wastewater continues to be an active area of research.

84 f selected biomarkers of exposure to PFRs in wastewater could be a simple and complementary approach

85 alth, microbial culturing found 18 to 41% of wastewater CRE isolates (n = 1447) were on the WHO "crit

86 ondary wastewaters (SW), as well as centrate wastewater (CW) diluted to less than 20%.

87 d knowledge regarding the adverse effects of wastewater-derived microplastics, particularly fibers, o

88 s (EOCs) in two catchment basins impacted by wastewater discharges.

89 feine, anthropogenic indicators of untreated wastewater discharges.

90 rs corresponding to the years of maximum O&G wastewater disposal contained higher concentrations of s

91 be used to assess future water sourcing and wastewater disposal or reuse, and to inform policy discu

92 for analytes to identify unconventional O&G wastewater disposal.

93 developed passive samplers were deployed in wastewater-dominated reaches of the Grand River (Kitchen

94 of DSi loading (3.6 Gmol SiO2 year(-1)) from wastewater effluent across the US.

95 y (CHO) cells induced by municipal secondary wastewater effluent amended with elevated Br(-) and I(-)

96 introduced into freshwater wetlands through wastewater effluent and agricultural runoff.

97 uperior estuary were primarily attributed to wastewater effluent and, to a lesser extent, geese and g

98 Disinfected wastewater effluent contains a complex mixture of biomol

99 er sources are located downstream of treated wastewater effluent discharges.

100 ing the pilot-scale ozonation of a secondary wastewater effluent from a major city in Germany.

101 t hydraulically downgradient former domestic wastewater effluent infiltration beds both act as contin

102 Nitrogen standards for discharge of wastewater effluent into aquatic bodies are becoming mor

103 Wastewater effluent is a recognized source of N and P to

104 DOM from surface waters, wastewater effluent, and 1 kDa size fractions were adsor

105 to peak A, whereas the reverse was found in wastewater effluent, indicating that humic-like fluoresc

106 application in constructed wetlands to clean wastewater effluents containing IBP and possibly also ot

107 to identify aromatic amines in six mutagenic wastewater effluents from a chemical-industrial area in

108 Worldwide, ozonation of secondary wastewater effluents is increasingly considered in order

109 and emitted to aquatic environments through wastewater effluents, and their bioaccumulation potentia

110 y-scale O3/BAC system treating two nitrified wastewater effluents, this study characterized the effec

111 ans, and this drug is prevalent in municipal wastewater effluents.

112 nents of these SMPs to understand what is in wastewater effluents.

113 MS) are emitted to aquatic environments with wastewater effluents.

114 s N 23 degrees E), experiencing intermittent wastewater emissions and high latitude environmental con

115 ouse dust, aquatic biota, surface water, and wastewater environments.

116 actical utility of our approach, a simulated wastewater experiment was conducted using water from the

117 (2) in vivo pooled urine assay, (3) in vivo wastewater fingerprinting assay, (4) analysis with HR-MS

118 Many countries are utilizing reclaimed wastewater for agriculture because drought, rising tempe

119 Our results suggest that use of reclaimed wastewater for irrigation of crops can affect the develo

120 the impact of surface water disposal of O&G wastewater from CWT plants upstream of the Conemaugh Riv

121 In addition, wastewater from different treatment steps of two WTPs wi

122 n, may indicate discharges of poorly treated wastewater from failing or outdated septic systems.

123 uiring remediation in gold mine tailings and wastewaters globally.

124 Hospital wastewaters had up to 9 orders of magnitude greater conc

125 s, the framework for comparison of water and wastewater impacts of various buildings can be applied d

126 Wastewaters in coastal regions may contain elevated leve

127 s, carcinogens, and their metabolites in raw wastewater, including anabasine (ANABA), anatabine (ANAT

128 ition near the water table below the FTA and wastewater-infiltration beds.

129 t finding considering the tremendous cost of wastewater infrastructure.

130 translocation by maize when they co-exist at wastewater irrigation sites.

131 ls to maize at the farmlands with industrial wastewater irrigation, this study revealed the effects o

132 organic micropollutants (MPs) from water and wastewater is challenging.

133 Disinfection of such wastewater is essential to prevent the spread of pathoge

134 ally in arid regions where treated municipal wastewater is extensively reused.

135 Remediation of industrial wastewater is important for preventing environmental con

136 c constituents in these hydraulic fracturing wastewaters is limited to hydrocarbons and a fraction of

137 ners in surface water, treated and untreated wastewater, landfill leachate, and biosolids (NY CARP da

138 ermination of eight phthalate metabolites in wastewater (limits of quantification between 0.5 and 32

139 cture was quantified to approximate need for wastewater management and downstream treatment.

140 oxazole and carbamazepine, which are typical wastewater markers in river water.

141 The O3/BAC-treated wastewaters met regulatory levels for trihalomethanes (T

142 Typical wastewater microorganisms like Pseudomonas sp. were chos

143 (MABRs) can make treatment of ammonium-rich wastewaters more energy-efficient, especially within the

144 long been used for disinfection of municipal wastewater (MWW) effluent while the use peracetic acid (

145 d and validated to monitor the occurrence in wastewater of human exposure biomarkers of 2-ethylhexyld

146 l predicting the transformation in untreated wastewater of six biomarkers, excreted following human m

147 Unfortunately, wastewater often contains biologically active, pseudoper

148 fects of agronomic application of olive mill wastewater (OMW) with rock phosphate (RP) in a field of

149 vinegar production from olive oil press-mill wastewaters (OMW) is presented.

150 resistant bacteria and genes in 12 hospital wastewater outfalls and five background sewer drains acr

151 Experiments treating authentic latrine wastewater over variable treatment times, current densit

152 owever, have examined the Si load of a large wastewater plant's effluent or the molar ratios of Si/N

153 iments on the desorption kinetics of typical wastewater pollutants (phenanthrene, tonalide, and benzo

154 The efficient handling of wastewater pollutants is a must, since they are continuo

155 It is assumed that wastewater pre-exposure alters animals' sensitivity to p

156 monstrate that press disturbance as posed by wastewater pre-exposure can enhance susceptibility of ke

157 Moreover, both wastewater pre-exposure scenarios increased animals' sen

158 Chlorination of wastewaters produced CHO cell genotoxicity comparable to

159 the United States; accompanied by increased wastewater production.

160 the need for vigilant monitoring of treated wastewater quality and disinfection effectiveness prior

161 Wastewater releases from New Delhi hospitals may pose a

162 Wastewater resource recovery has been advocated for deca

163 hnical socio-political barriers to realizing wastewater resource recovery.

164 r = 0.913, p = 0.010) levels across hospital wastewaters, respectively, implying that elevated CRE an

165 t plant, ozonation of conventionally treated wastewater resulted in the removal of micropollutants an

166 such as seawater desalination or industrial wastewater reuse may be limited by low rejection of vola

167 s-free advanced treatment trains for potable wastewater reuse.

168 progestins, and glucocorticoids, in hospital wastewaters, river water, and municipal wastewater treat

169 the population which contributed to a given wastewater sample.

170 etermination of DNZ in soil, river water and wastewater samples and satisfactory recoveries were obta

171 erference study for determination of H2O2 in wastewater samples demonstrated the selectivity of the m

172 The developed method was applied to wastewater samples from two Belgian cities.

173 this study, we analyzed hydraulic fracturing wastewater samples using ultrahigh resolution Fourier tr

174 for detection of hydrogen peroxide (H2O2) in wastewater samples.

175 f the concentrations of CN(-) in complicated wastewater samples.

176 ty with biological proteins (glutathione) of wastewater samples.

177 cherry juice, mineral water, well water and wastewater samples.

178 mitochondrial DNA (mtDNA) from raw untreated wastewater samples.

179 was obtained with the MNC-TFC membranes with wastewater samples.

180 enhance integrated resource recovery in the wastewater sector through the creation of a national tes

181 developments, to provide a strategy for the wastewater sector to accelerate a path forward that lead

182 or (FPA)-based micro-FTIR analyses of water, wastewater, sediment, biota, and food samples.

183 Analysis of the postdisinfected treated wastewater showed the presence of clinically relevant sl

184 Residual wastewater solids are a significant reservoir of antibio

185 o that of the control microcosms to which no wastewater solids had been applied.

186 These results demonstrate that wastewater solids treatment technologies can be used to

187 chnologies can reduce ARG levels in residual wastewater solids, the effects of these technologies on

188 on the fate of ARGs and class 1 integrons in wastewater solids-amended soil microcosms.

189 establish mathematical relationships between wastewater/solution characteristics, biofilm communities

190 in drainfields varied widely and depended on wastewater sources and compound-specific removal process

191 ndicating large anthropogenic inputs via the wastewater stream.

192 lecules which nanoparticles may encounter in wastewater streams, stabilizes silver colloids from aggl

193 mpounds in flowback fluids rather than older wastewaters suggested that the observed molecular ions m

194 ng chemical chlorination and electrolysis of wastewater, suggesting that organic byproducts are forme

195 y relevant mycobacteria in treated municipal wastewater, suggesting the need for vigilant monitoring

196 inum grew well on primary (PW) and secondary wastewaters (SW), as well as centrate wastewater (CW) di

197 o achieve universal coverage), newly treated wastewater systems (to halve the proportion of untreated

198 Integrated real-time control (RTC) of urban wastewater systems is increasingly presented as a promis

199 ogates to be aerosolized from three types of wastewater systems: toilets, a lab-scale model of an aer

200 Acid rock drainage (ARD) is a metal-rich wastewater that forms upon oxidation of sulfidic mineral

201 leads to the production of more recalcitrant wastewaters that are difficult to dispose or recycle on-

202 ations of Ra and Sr were likely sourced from wastewaters that originated from the Marcellus Shale for

203 morpha linum in different types of municipal wastewaters, their ability to remove nutrient and their

204 onal criteria: (3) negligible degradation in wastewater to ensure the stability of chemicals during c

205 he air emissions associated with natural gas wastewater transport as a case study.

206 Wastewater transport from wells eligible for 2011 impact

207 ally and temporally distributed impacts from wastewater transport.

208 use and carbon footprint per cubic meter of wastewater treated, varies markedly with the carbon subs

209 26 per cubic meter for zero-liquid discharge wastewater treatment (expected cost-benefit ratios of 1.

210 erage) and those connected to sewers without wastewater treatment (Target 6.3: halving the proportion

211 oalgae C. linum could represent an effective wastewater treatment alternative that could also provide

212 er for chemical precipitation and biological wastewater treatment and $11.26 per cubic meter for zero

213 e an emerging concept for simultaneous water/wastewater treatment and energy recovery.

214 d other merits, such as creating benefits of wastewater treatment and facile preparation and scalabil

215 ntially reduce the costs and energy input of wastewater treatment and facilitate recovery of nitrogen

216 can increase our understanding of industrial wastewater treatment and inform iterative process design

217 cture functionalized polymeric membranes for wastewater treatment and osmotic power generation.

218 applications in the areas of energy storage, wastewater treatment and solar-steam-assisted desalinati

219 Findings of net cost for FGD wastewater treatment are robust to uncertainty in auxili

220 an attractive candidate for energy-positive wastewater treatment as it biologically couples CO2 and

221 r this purpose, the local N2O emissions of a wastewater treatment bioreactor was sampled by a dedicat

222 are an attractive option for onsite latrine wastewater treatment due to their high efficiency and sm

223 er nanoparticles (AgNPs) enter estuaries via wastewater treatment effluents, where they can inhibit m

224 or the analysis of the final effluent of six wastewater treatment facilities.

225 aters (municipal tap water, streamwater, and wastewater treatment facility effluent) under normal-flo

226 ncluding chicken and turkey litter leachate, wastewater treatment facility effluent, and concentrated

227 Wastewater treatment facility effluent, turkey litter le

228 tion concept to assess processes of advanced wastewater treatment including ozonation and GAC by cons

229 omains that are utilizing microorganisms for wastewater treatment or electrosynthesis.

230 ital wastewaters, river water, and municipal wastewater treatment plant (WTP) influents and effluents

231 ) measurements, anthropogenic influence of a wastewater treatment plant (WWTP) discharge was observed

232 o diester metabolites were investigated in a wastewater treatment plant (WWTP) in the Albany area of

233 8 days at three locations near two different wastewater treatment plant discharge sites in the Saint

234 Wastewater treatment plant disinfection practices inform

235 udy, more than 80% of the compounds found in wastewater treatment plant effluent samples possessed a

236 oinvertebrates can be chronically exposed to wastewater treatment plant effluents (i.e., press distur

237 " in complex environmental matrices (such as wastewater treatment plant effluents).

238 ushing for management with other sewage at a wastewater treatment plant emits 0.10 kg of CO2e.

239 Run-off from farms and wastewater treatment plant overflows contribute high con

240 was implemented successfully in a full-scale wastewater treatment plant.

241 he outfall of the Las Palmas de Gran Canaria wastewater treatment plant.

242 nd applied in the influent and effluent of a wastewater treatment plant.

243 al tool for N2O analyses of the off-gas of a wastewater treatment plant.

244 t varying distances from two major municipal wastewater treatment plants (MWWTPs) (Waterloo, Kitchene

245 Intersex in fish downstream of municipal wastewater treatment plants (MWWTPs) is a global concern

246 waters, reducing nitrogen (N) discharge from wastewater treatment plants (WWTPs) by upgrading convent

247 eholds and are common in areas not served by wastewater treatment plants (WWTPs) globally.

248 Niagara River receives PPCPs from different wastewater treatment plants (WWTPs) situated along the r

249 of the SCCPs, MCCPs, and LCCPs in Australia wastewater treatment plants (WWTPs).

250 challenges to the enhanced sustainability of wastewater treatment plants (WWTPs).

251 d in a range of applications today and enter wastewater treatment plants after product utilization.

252 Runoff from farms and output from wastewater treatment plants also contribute high concent

253 an antiepileptic drug which is persistent in wastewater treatment plants and the environment.

254 ludge and effluent samples from 64 municipal wastewater treatment plants as well as in major rivers i

255 It includes substances passing biological wastewater treatment plants regulated or proposed to be

256 (NH4(+) --> NO2(-) --> N2) is favorable for wastewater treatment plants without sufficient carbon so

257 espect to the analysis of N2O emissions from wastewater treatment plants.

258 ing dissolved elements are the main goals of wastewater treatment prior to discharge.

259 ry of electricity and chemical inputs to FGD wastewater treatment processes and quantify the marginal

260 ed use and potency of marijuana on water and wastewater treatment processes and the environment shoul

261 ncept has been developed to compare advanced wastewater treatment processes for their efficacy of eli

262 nable the shift from conventional biological wastewater treatment processes to resource recovery syst

263 acteristics can facilitate sustainable water/wastewater treatment processes.

264 ion as anti-biofouling membrane in water and wastewater treatment processes.

265 due to the inherent complexity of biological wastewater treatment processes.

266 g of MPs through the settlement processes of wastewater treatment results in the majority becoming en

267 olved metagenomics to characterize anaerobic wastewater treatment sludge enrichments performing DPO c

268 onal drainfield-based and alternative onsite wastewater treatment systems to characterize concentrati

269 the importance of this process in full-scale wastewater treatment systems, including its relevance fo

270 Onsite wastewater treatment systems, such as septic systems, se

271 use gas emissions from agricultural soils or wastewater treatment systems.

272 activity of different guilds in sediments or wastewater treatment systems.

273 derably improve the performance of classical wastewater treatment technologies, e.g. adsorption, cata

274 ANDO) is a promising emerging bioprocess for wastewater treatment that enables direct energy recovery

275 ng pharmaceuticals, present in discharges of wastewater treatment works (WwTWs) effluents.

276 ed using alternative management costs (e.g., wastewater treatment) as representative, showing ecosyst

277 portant to characterize their persistence in wastewater treatment, especially in arid regions where t

278 ents relevant to MP removal during water and wastewater treatment.

279 s and have potential for use in drinking and wastewater treatment.

280 ter-based epidemiology and on-site water and wastewater treatment.

281 re thus promising for pollutant oxidation in wastewater treatment.

282 ttracted attention for applications in water/wastewater treatment.

283 Moreover, wastewater type and nutrient concentration influenced bi

284 water up to ca. 1.6 mug L(-1) and in treated wastewater up to ca. 1 mug L(-1).

285 in showed that these substances occur in raw wastewater up to ca. 1.6 mug L(-1) and in treated wastew

286 of possible metabolic biomarkers present in wastewater using an in-vivo study; (ii) verification of

287 cate that MD can purify contaminated, acidic wastewater using low-grade heat sources, such as geother

288 Nevertheless, broad wastewater valorization remains elusive.

289 ate collection of urine, which is only 1% of wastewater volume but contains the majority of nitrogen

290 Ozonated wastewater was at least 3 times less genotoxic than the

291 h reactor (SBR) receiving synthetic domestic wastewater was treated in an FA treatment unit at 210 mg

292 g batch reactor treating synthetic municipal wastewater, we observed stable and near-complete N remov

293 Finally, concentrations in wastewater were also used to estimate metabolite concent

294 Concentrations in raw wastewater were converted into levels of exposure to six

295 Proteins present in the alkaline extraction wastewater were recovered at pH 3, 4, 5 and 6, and were

296 matter (SPM) was 56.4% of the total mass in wastewater, which was the highest among the target chemi

297 These results indicate that the ozonation of wastewater with high Br(-) and I(-) levels may yield org

298 tion column, to pretreat methylene blue (MB) wastewater with high concentration ( 100 mg L(-1) or hig

299 All target OPFRs were found in wastewater, with average concentrations that ranged from

300 c acid (PAA) and monochloramine in secondary wastewater (WW) and phosphate buffer (PB) as assessed by