ライフサイエンスコーパス: wastewater

1 tivate bacterial and viral microorganisms in wastewater.

2 ost approach to disinfect drinking water and wastewater.

3 sorbents for ammonium removal from domestic wastewater.

4 fter 10 min of contact time in real domestic wastewater.

5 scharges from flue gas desulfurization (FGD) wastewater.

6 tromethane is unlikely to occur naturally in wastewater.

7 ng energy and carbon from dilute organics in wastewater.

8 mits its application in treating hypersaline wastewater.

9 could enable ammonium recovery from domestic wastewater.

10 spinach, infant milk substitute) and battery wastewater.

11 of contaminants and microbial pollutants in wastewater.

12 ed by organic constituents found in domestic wastewater.

13 anic wastes such as pomace, seeds, peels and wastewater.

14 fold, despite pretreatment of the industrial wastewater.

15 biofilm communities for the treatment of dye wastewater.

16 h wastewater, with a focus on slaughterhouse wastewater.

17 s from laboratory-disinfected gas extraction wastewater.

18 est in interventions focused on capture from wastewater.

19 , allowing a quantitative analysis of CIP in wastewater.

20 e electron beam treatment (ELT) of water and wastewater.

21 kg y(-1) of lens dry mass discharged into US wastewater.

22 omise for the n-DAMO application in domestic wastewater.

23 hout matrix effect in drinking, surface, and wastewater.

24 cessed, roughly 80 kg of oil is produced and wastewater accounted for the highest proportion (500 kg)

25 eria (NFB) in reactors fed with low nitrogen wastewater, analogous to those usually found in certain

26 As routine industrial wastewater analyses monitor the occurrence of a limited

27 nstrates >90% removal efficiencies with real wastewater and concentrations of arsenic as low as 10 pp

28 strong positive correlation was found among wastewater and crop's toxic metals (r(2) values in Cu, Z

29 tify, and characterize microplastics in both wastewater and drinking water.

30 e a promising method for treating industrial wastewater and producing clean energy.

31 NP behavior in synthetic wastewater and seawater was characterized during aging a

32 shows that micropollutants in both municipal wastewater and stormwater can be relevant sources of con

33 milar behavior was observed for a mixture of wastewater and surface water (volume ratio 1:1).

34 o tap water, well water, lake water, medical wastewater and tea samples.

35 dium priority (steam, circulating water, and wastewater), and low priority (fresh water, demineralize

36 total processed API quantity was lost to the wastewater, and despite the small percentage (<5%) of FP

37 irect air emissions, bitumen froth, residual wastewater, and tailings components, ultimately enabling

38 t would impact the operation of MESe in real wastewater applications.

39 hate buffer and municipal secondary effluent wastewater, are reported for the first time.

40 H(n)PO(4)(n-3) present in a natural poultry wastewater as mainly struvite.

41 Publicly available toxicological studies on wastewaters associated with unconventional oil and gas (

42 antidepressant fluoxetine spiked into urban wastewater at near-neutral pH after 60 min at 50 mA with

43 imate the trace element concentration of FGD wastewater at the plant level.

44 Avocado wastewater (AWW) was spray dried into powder at differen

45 study, we monitored culturable and resistant wastewater bacteria and cross-resistance to clinically r

46 care biosensor system with mobile health for wastewater-based epidemiology (iBMW) for early warning o

47 Wastewater-based epidemiology (WBE) can provide a compre

48 Wastewater-based epidemiology may be useful for informin

49 for the development of advanced sensors for wastewater-based epidemiology that provide an early warn

50 ch toward the comprehensive investigation of wastewater-borne MNMs.

51 s study are not only suitable for industrial wastewater but also could be efficiently employed for ti

52 milar order of magnitude to that released to wastewater by laundering.

53 ibiotic that is not efficiently removed from wastewater by routine treatment and therefore can be det

54 ation in trace element concentrations in FGD wastewater can span several orders of magnitude and is a

55 microbiome, as antibiotics and pathogens in wastewater can track with clinically relevant parameters

56 e between each participating household and a wastewater canal was measured using GPS coordinates.

57 nd despite the small percentage (<5%) of FPI wastewater compared to the total wastewater flow.

58 demonstrated the large mineralization of all wastewater components at 6 h, which was accompanied by a

59 aggregation observed between Ag, Ti NPs, and wastewater components.

60 tration, trace element partitioning, and FGD wastewater composition.

61 d, which are clearly above typical municipal wastewater concentrations; and (iii) a pharmaceutical no

62 -efficient water treatment technology toward wastewater containing complex contaminants.

63 rochemical manufacturing facility discharged wastewater containing poorly understood per- and polyflu

64 Without treatment, however, wastewater contains harmful pathogens and chemicals.

65 se) were used to annotate trends of relevant wastewater contaminants.

66 used as a biofertilizer and that the treated wastewater could be released to the environment with ver

67 uarine environment lowered the risks of most wastewater-derived CECs, but dilution alone is insuffici

68 cts, in addition to the expected pesticides, wastewater-derived chemicals and chemicals typical for s

69 solved nitrogen, specific conductance, and a wastewater-derived fluorescent organic matter component)

70 (TK) model to predict the concentrations of wastewater-derived micropollutants in freshwater inverte

71 Although the exposure assessment of wastewater-derived micropollutants via chemical, bioanal

72 Evaluation of struvite-based wastewater-derived sorbents, comparison with commonly us

73 For wastewater-derived sorbents, S solids heated to 150 degr

74 Biological treatment of wastewater did not result in a measurable loss of plasti

75 PFO5DoA to 65% for PFO4DA in 6 months due to wastewater discharge control.

76 ce tidal creek to investigate the impacts of wastewater discharge from a poultry processing plant on

77 y demonstrates denitrification inhibition by wastewater discharge from a poultry processing plant wit

78 d in the impacted creek, especially near the wastewater discharge, and denitrification inhibition by

79 tants reaching the marine environment though wastewater discharges from coastal sources remain largel

80 important information in designing an Fe(VI) wastewater disinfection process.

81 , the most efficient photosensitizer was the wastewater DOM isolated from the influent of the wetland

82 lated to high organic matter found in Arctic wastewater due to lower consumption of potable water lea

83 Reverse osmosis (RO) treatment of municipal wastewater effluent is becoming more common as water reu

84 calculations demonstrated the prevalence of wastewater effluent to nearshore marine environments, th

85 Ozonation of wastewater effluent was shown to form abundant nitrometh

86 GEM suitable for treating stormwater runoff, wastewater effluent, and agricultural discharge via vary

87 m open-water wetlands that treated municipal wastewater effluent.

88 bove 7 muM) were observed after ozonation of wastewater effluent.

89 noparticles through municipal and industrial wastewater-effluent discharges and agricultural nonpoint

90 llowing: (1) reported concentrations in both wastewater effluents and drinking water, (2) microplasti

91 conditions of base flow dominated by treated wastewater effluents and flood events transporting rural

92 The discharge of wastewater effluents to a stream that is subsequently us

93 e in transforming effluent organic matter as wastewater effluents travel downstream, but the correspo

94 ively, in clean water and secondary/tertiary wastewater effluents when the same amounts of PAA and UV

95 ously producing struvite and dihydrogen from wastewater effluents with no energy input in a green and

96 ce health risks for entire communities where wastewater exposure occurs.

97 , and polyomavirus in sewage samples from 49 wastewater facilities across the contiguous United State

98 ams as well as discharge from more than 7500 wastewater facilities.

99 <5%) of FPI wastewater compared to the total wastewater flow.

100 e treatment of simulated methylene blue (MB) wastewater for 9 weeks under aerobic conditions. The COD

101 Reusing wastewater for irrigation is a longstanding practice tha

102 ing and to monitor ambient water sources and wastewater for pharmaceutical pollutants.

103 The tapping of municipal wastewater for potable reuse significantly enhances drin

104 utility of viral RNA monitoring in municipal wastewater for SARS-CoV-2 infection surveillance at a po

105 At the WWTP receiving wastewater from a pharmaceutical manufacturing site, (i)

106 At two municipal WWTPs, both receiving wastewater from several FPIs, two months' daily effluent

107 NBFRs) were determined in lagoons processing wastewater from two high-Arctic and two sub-Arctic of Ca

108 n based on reduction of bacterial community (wastewater) growth.

109 Reuse of untreated wastewater has been shown to be harmful to the health of

110 Direct sampling of building wastewater has the potential to enable "precision public

111 -bearing solids from swine (S) and dairy (D) wastewater, heat-treated to 150-300 degrees C, were eval

112 mpared to the WWTP receiving purely domestic wastewater; (ii) for 11 pharmaceuticals peak concentrati

113 a group of toxic disinfection byproducts, in wastewater-impacted surface water have not been thorough

114 Technologies to treat wastewater in decentralized systems are critical for sus

115 Disinfection of wastewaters increased mammalian cytotoxicity several ord

116 We quantified SARS-CoV-2 RNA in wastewater influent and primary settled solids in two wa

117 a resistant to TCS and BC were isolated from wastewater influent over 21 months, and cross-resistance

118 can alleviate large water fluxes into aging wastewater infrastructure.

119 In secondary effluent wastewater (initial NH(4)(+)-N of 0.7 meq NH(4)(+)-N/L),

120 he environment and health risk assessment of wastewater irrigated soil and crops in a semi-arid regio

121 Crop irrigation by wastewater irrigation is a prominent alternative option

122 ironmental samples including drinking water, wastewater, irrigation water, and surface waters.

123 Wastewater is a common pathway for the spread of antibio

124 Potable reuse of wastewater is expanding, and ozonation for water reuse i

125 ocess for ammonium (NH(4)(+)-N) removal from wastewater is limited due to the lack of suppliers of en

126 hin the same hospital group and in human and wastewater isolates from 3 hospitals elsewhere in the Un

127 ng correlation was also found among soil and wastewater lead (r(2) = 0.639).

128 ied broadly as a strategy for both improving wastewater management and decarbonization.

129 rd shows that the implementation of improved wastewater management policies succeeded in bringing dow

130 ne can enable nutrient recycling, facilitate wastewater management, and conserve water.

131 t nitro-STG was formed as the main TP in the wastewater matrix.

132 However, industrial wastewater may contain growth inhibitory compounds precl

133 Antimicrobial-resistant bacteria within wastewater may reflect the resistance burden within the

134 ity of extracellular peptidases derived from wastewater microbial communities, which is a major imped

135 enzyme pools derived from three independent wastewater microbial communities.

136 s of cross-resistance patterns among diverse wastewater microorganisms, which could reflect the varie

137 in several fields, including biotechnology, wastewater monitoring, and nanobubble preparations.

138 , demonstrating a robust system for treating wastewater of varying strengths.

139 Introduction of oil and gas extraction wastewaters (OGWs) to surface water leads to elevated ha

140 for the adsorption of metal ions in tannery wastewater onto the nano-adsorbents was examined using W

141 ects in many samples indicated the impact by wastewater or overflow of combined sewer systems.

142 We hypothesized that wastewater ozonation forms nitromethane, which would be

143 e the specificity of dissolved extracellular wastewater peptidases.

144 -based antibiotics that can be hydrolyzed by wastewater peptidases.

145 monly used peracid disinfectant of municipal wastewater, peracetic acid (PAA), the ICT requirements d

146 The report by Kang and colleagues adds wastewater plumbing systems to the catalogue of potentia

147 ut facilities due to the connected system of wastewater plumbing.

148 Olive oil mill wastewater polyphenol powders (OMWP) were added to gluco

149 n-the-loop corrective management actions for wastewater processing.

150 to find an alternative application for this wastewater rather than its direct disposal into landfill

151 ch reactor, anaerobic ammonia oxidation in a wastewater reactor and aerobic pyrite oxidation in acid

152 les (NPs), individually and as a mixture, in wastewater relative to their pristine counterparts on th

153 Ozonation of drinking and wastewater relies on ozone (O(3)) and hydroxyl radical (

154 +/- 0.022 L/(mg.min) in phosphate buffer and wastewater, respectively, at pH 7.2.

155 and the reporting of test results, immediate wastewater results can provide considerable advance noti

156 Intense light attenuation in water/wastewater results in photocatalysts exhibiting a low qu

157 The method was applied in triplicate to wastewater samples from Quebec (Canada), obtaining conce

158 measurements was validated by testing solid wastewater samples randomly obtained from the environmen

159 immunosensor for the determination of CIP in wastewater samples was developed using the properties of

160 Although PFAAs also sorb to solids, the wastewater samples were filtered prior to analysis of PF

161 d differences in the chemical composition of wastewater samples were observed over time to reveal hid

162 a high average recovery of 91% after spiking wastewater samples with CIP at a concentration of 9,100

163 sure to a pure chemical and to environmental wastewater samples.

164 ds, in vitro-derived research materials, and wastewater samples.

165 It is found that, in the context of wastewater sensing, MESe technology has been unable to b

166 as provided roads and electricity, water and wastewater services are still lacking in many colonias.

167 The provision of urban water and wastewater services contributes to greenhouse gas (GHG)

168 n to extend utilities' role beyond water and wastewater services providers.

169 phosphate buffer (PB) and secondary effluent wastewater (SEW).

170 eeks under aerobic conditions. The COD of MB wastewater showed a reduction of 86.48% from 2000 to 270

171 HPC-treated wastewater showed higher copy numbers of intI1 in the ir

172 This release mainly occurs through wastewater since the treatments applied in many wastewat

173 successful in the decentralized treatment of wastewater, steady-state power density must be improved

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

175 however prior testing and treatment of such wastewater streams must be employed to minimize the adve

176 to simultaneously manage two complex energy wastewater streams while reducing freshwater resource co

177 ological nitrogen removal, particularly from wastewater streams with low chemical oxygen demand (COD)

178 Wastewater studies that provide per capita estimates of

179 and fecal indicators indigenously present in wastewater such as fecal coliforms and enterococci showe

180 lyfluoroalkyl substances (PFAS)-contaminated wastewaters, such as municipal solid waste landfill leac

181 umption (influent) or release (effluent) via wastewater systems rely heavily on accurate population d

182 To investigate the effective regulation of wastewater systems with this technology, two permitting

183 editorialist discusses the findings and why wastewater systems, particularly those in high-rise buil

184 Integrated real-time control (RTC) of urban wastewater systems, which can automatically adjust syste

185 Wastewater testing captures the rise and fall of novel c

186 ) treat farm-produced pesticide-contaminated wastewater to reduce surface water pollution.

187 mber of animal processing plants discharging wastewater to water bodies.

188 the environmental impacts (EIs) of different wastewater treatment (WWT) configurations, attempting re

189 ) possess a great potential for simultaneous wastewater treatment and energy recovery.

190 generation has presented great potential for wastewater treatment and seawater desalination with high

191 k suggests that an initial anaerobic step in wastewater treatment can reduce the concentration of SMX

192 In some situations, wastewater treatment chemical requirements were eliminat

193 Wastewater treatment contributed to reduce the abundance

194 seful infectious enteric virus indicators of wastewater treatment efficacy.

195 Our results support that wastewater treatment efficiently removes the hosts of an

196 ized for the analysis of 204 pesticides from wastewater treatment facility (WWTF) process water.

197 plications and can, therefore, be applied in wastewater treatment for removal of heavy metals and oth

198 suggests that the benefits and costs of FGD wastewater treatment for the median plant will poorly de

199 mples collected during the various stages of wastewater treatment from two WWTFs in Southern Ontario.

200 Therefore, wastewater treatment has to become a valuable water reso

201 Determining the effect of wastewater treatment in water resistome is a topic of in

202 parameters, such as the electricity grid and wastewater treatment method.

203 Our results suggest that wastewater treatment mitigates the environmental dissemi

204 l transformation processes during artificial wastewater treatment of silver (Ag-NPs) and titanium dio

205 have potential opportunities in the areas of wastewater treatment or other activated carbon/carbon na

206 A) is an emerging disinfectant for municipal wastewater treatment owing to good biocidal effects and

207 samples were collected from three steps at a wastewater treatment plant (raw sewage, secondary-treate

208 an rivers sampled upstream and downstream of wastewater treatment plant (WWTP) discharge.

209 from pharmaceutical production in municipal wastewater treatment plant (WWTP) effluents and to estim

210 ion and compared to overall API emissions in wastewater treatment plant (WWTP) effluents.

211 nhance bioenergy recovery and to transform a wastewater treatment plant (WWTP) from an energy consume

212 subtraction, 3303 features were obtained of wastewater treatment plant (WWTP) influent samples.

213 sheds as a function of adjacent land use and wastewater treatment plant (WWTP) input 6 months after H

214 g of the Colorado River near the Moab, Utah, wastewater treatment plant (WWTP) outflow has detected p

215 artificial flumes fed with effluents from a wastewater treatment plant and subjected to four treatme

216 tions by 85%, as the result of upgrading the wastewater treatment plant at one of the sampling sites

217 were repeatedly affected, including ~55% of wastewater treatment plant capacity and swine operations

218 was used to assess general toxicity at four wastewater treatment plant effluents of Biscay (Gorliz,

219 extracted from deployed passive samplers at wastewater treatment plant effluents.

220 from influents and treated effluents from a wastewater treatment plant located in Northern Portugal

221 Using the anaerobic digestate of a pilot wastewater treatment plant spiked with metal-doped plast

222 0s, reflecting intensified human activities, wastewater treatment plant upgrades and regulation in th

223 in a microbial consortium from a biological wastewater treatment plant using integrated meta-omics.

224 nous microbial populations from a biological wastewater treatment plant.

225 ructed wetland and from digester sludge of a wastewater treatment plant.

226 treating secondary effluent from a municipal wastewater treatment plant.

227 the influent and effluent of a typical urban wastewater treatment plant.

228 On-site wastewater treatment plants (OSTs) are usually unattende

229 ties including 5 refineries, 10 landfills, 4 wastewater treatment plants (POTWs), 2 composting operat

230 Biosolids samples collected from 82 wastewater treatment plants (WWTPs) across Australia and

231 release into the environment, especially via wastewater treatment plants (WWTPs), poses a potential t

232 major impact of urbanization are inputs from wastewater treatment plants (WWTPs).

233 ns previously observed in Canadian temperate wastewater treatment plants (WWTPs).

234 f their widespread presence in effluents and wastewater treatment plants (WWTPs).

235 he antidiabetic drug sitagliptin (STG) enter wastewater treatment plants (WWTPs).

236 that NPs are not completely filtered out at wastewater treatment plants and may therefore be continu

237 tewater since the treatments applied in many wastewater treatment plants are not able to completely r

238 wnstream of one upgraded and two nonupgraded wastewater treatment plants before being sampled for ana

239 ers was limited to certain hotspots close to wastewater treatment plants discharge points.

240 ce is primarily attributed to discharge from wastewater treatment plants due to incomplete removal by

241 naerobic digesters treating sewage sludge at wastewater treatment plants globally.

242 Wastewater treatment plants have been identified as impo

243 oducts, the hospital sewer, and 20 municipal wastewater treatment plants in the East of England betwe

244 nic contaminants encountered downstream from wastewater treatment plants is not well understood.

245 r influent and primary settled solids in two wastewater treatment plants to inform the preanalytical

246 , is present in surface waters downstream of wastewater treatment plants.

247 ft from energy-negative to energy-neutral in wastewater treatment plants.

248 rogen cycle in both natural environments and wastewater treatment plants.

249 ection methods commonly used in drinking and wastewater treatment plants.

250 e fertilizers and reducing nutrient loads to wastewater treatment plants.

251 cattle, poultry, hospital sewage, and 12/20 wastewater treatment plants.

252 ificance to Mn-based oxidation reactions and wastewater treatment processes.

253 e to incomplete removal by common biological wastewater treatment processes.

254 gy, to minimize resistance HGT in biological wastewater treatment processes.

255 To investigate the effects of wastewater treatment processing on the ecotoxicology of

256 merase (CapPhaEC) from activated sludge from wastewater treatment that demonstrates a higher capacity

257 Thus, GBs-FBR system can be used for wastewater treatment to solve the current problem of ind

258 Improving onsite wastewater treatment to standards enabling water reuse w

259 e of male fish to estrogenic substances from wastewater treatment works (WwTWs) results in feminizati

260 lications such as drinking water filtration, wastewater treatment, and contaminant remediation.

261 (NPs) are entering soils with biosolids via wastewater treatment, and on-route, undergo changes (e.g

262 biomedical, electroanalysis, energy storage, wastewater treatment, automotive, etc.

263 tainable advances in the fields of biofuels, wastewater treatment, bioremediation, desalination, and

264 y extracellular peptidases during biological wastewater treatment, thereby limiting the emergence and

265 ons in viral levels can be applicable during wastewater treatment.

266 s and enhancing efficiency for self-aerating wastewater treatment.

267 is a widely discussed technique for advanced wastewater treatment.

268 he reduction of human enteric viruses during wastewater treatment.

269 t has a good application potential in saline wastewater treatment.

270 tally restricts practicality of solar-driven wastewater treatment.

271 impacts their properties and performance in wastewater treatment.

272 ld be an excellent complement for industrial wastewater treatment.

273 technology, for example, in applications for wastewater treatment.

274 urrently incurs the highest energy demand in wastewater treatment.

275 of producing oxygen, the key element in OPG wastewater treatment.

276 n cycle and play a major role in sustainable wastewater treatment.

277 In wastewater-treatment reactors, photogranules grow in num

278 (2) O), which can extensively crystallize in wastewater treatments, is a potential source of N and P

279 Urban water supply and wastewater utilities can potentially achieve low-carbon

280 ges of S-150 for NH(3)(g) mitigation include wastewater valorization, minimal synthesis, low heat tre

281 Our results demonstrate that small wastewater volumes from a single industry not only left

282 es, piperazines, indole, and amphetamine) in wastewater was developed and validated.

283 l efficiency of NaPAA hydrogels in synthetic wastewater was found to be comparable to that in real se

284 As proof of concept, industrial wastewater was investigated.

285 The analysis of CIP in wastewater was performed without the use of an organic s

286 end, a five-month time series for industrial wastewaters was utilized, analyzed by liquid chromatogra

287 d nonresidential), roads, and pipe networks (wastewater, water supply, and natural gas).

288 presentative of the mixture found in laundry wastewater were injected into the system to represent a

289 Fe(III), COD, BOD, and chloride from tannery wastewater were investigated.

290 Replicate reactors treating domestic wastewater were operated under stable aerobic (+195 +/-

291 esses generate a large amount of hypersaline wastewater, whose spills or discharges may significantly

292 enide-based semiconductor materials produces wastewater with co-occurring arsenic (As) ions and CeO(2

293 The biosensor was applied to wastewater with different Zn(2+) concentrations and the

294 n (1 kW m(-2) ) at 3.2 kg m(-2) h(-1) out of wastewater with wide degrees of acidity and alkalinity (

295 ing the anaerobic digestion of high strength wastewater, with a focus on slaughterhouse wastewater.

296 is sp., which rapidly grew and flourished in wastewater, with ammonium and phosphate removal efficien

297 ic and nonphototrophic microorganisms, treat wastewater without aeration, which currently incurs the

298 ogen evolution reaction and decomposition of wastewater without light irradiation can be achieved sim

299 tory experiments to determine the effects of wastewater (WW) on microbial communities and organic-mat

300 Wastewater (WW) reuse is expected to be increasingly ind

301 ification inhibition potential of industrial wastewater (WW) samples.