ライフサイエンスコーパス: sewage

1 ed as the SBT of the low-carbon CEPT settled sewage.

2 evaluated against measured concentrations in sewage.

3 eactive N-nitrosamine precursors to domestic sewage.

4 ers through the discharge of treated and raw sewage.

5 nto consumer products that are disposed into sewage.

6 a good stability of the target biomarkers in sewage.

7 , ranging from unpolluted river water to raw sewage.

8 C), and, as such, they have been detected in sewage.

9 t numerous populations to be associated with sewage.

10 ic strengths than those commonly observed in sewage.

11 ncentrations of human enteric viruses in raw sewage.

12 of both surface and groundwaters by domestic sewage.

13 ce to colistin, carbapenem and amikacin from sewage.

14 ly removed the pollutants from the synthetic sewage.

15 sence of only suspended biomass in untreated sewage.

16 93 isolates), faeces (128 [36%] of 360), and sewage (14 [22%] of 65) with STs 38 and 648 also widespr

17 f (12%), groundwater infiltration (39%), and sewage (49%).

18 r was found to be comparable to that in real sewage (71% vs 69%, respectively), suggesting that the s

19 stimates varied across different mixture and sewage age scenarios.

20 nome amplification (WGA) of RNA and DNA from sewage and animal (avian, cattle, poultry, and swine) fe

21 percentage true positives) of MST results in sewage and animal waste samples (21-33%) was lower than

22 m two sources concentrated in urban systems, sewage and atmospheric deposition.

23 With stressors linked to untreated sewage and catchment development also now impacting the

24 Virus serotypes detected in sewage and groundwater were temporally correlated, sugge

25 32% of the microbes represented terrestrial, sewage and human inputs (allochthonous).

26 ect beta-lactam resistance in wastewater and sewage and identified resistance in individual bacterial

27 s of total fipronil related compounds in raw sewage and in plant effluent after chlorination were sta

28 ects poliovirus circulation in environmental sewage and is used to monitor transmission in communitie

29 ESBL-E coli also were frequent in sewage and retail chicken (104 [65%] of 159 meat samples

30 genetic markers were highly abundant in raw sewage and sewage-impacted water samples.

31 essfully for the determination of ammonia in sewage and soil water samples.

32 (CSOs) occur in combined sewer systems when sewage and stormwater runoff are released into water bod

33 to evaluate stability of drug biomarkers in sewage and the uncertainty related to back-calculation o

34 rting reactive nitrogen to dinitrogen gas in sewage and waste treatment plants.

35 nsmission of enteric fever organisms through sewage and water, discuss recent advances in the molecul

36 was isolated from cattle, poultry, hospital sewage, and 12/20 wastewater treatment plants.

37 eatment plant (raw sewage, secondary-treated sewage, and final effluent) monthly for a 13-month perio

38 blished the specificity of the microarray in sewage, and fluorescence decrease of positive probes ove

39 23 were represented in bloodstream, hospital sewage, and municipal wastewater isolates.

40 e most abundant groups of faecal bacteria in sewage, and several Lachnospiraceae high-abundance sewag

41 When conservative estimates of DIN from sewage are included in input calculations, DIN retention

42 species and hosts, and the potential role of sewage as a conduit for the spread of AMR.

43 We propose metagenomic analysis of sewage as an ethically acceptable and economically feasi

44 We also sampled a local lake and untreated sewage as potential virus sources.

45 ybrid system operating continuously with raw sewage as the feed at water recovery up to 80%.

46 nts were elevated, and deltaN(15) implicates sewage as the source, demonstrating transported nutrient

47 d water sources through latrine overflow and sewage, as well as by the periodicity of human activitie

48 terica, and Giardia lamblia were detected in sewage, as well as MST markers and resistance genes to a

49 be useful in predicting samples enriched in sewage-associated and pathogen-like bacteria in tropical

50 asured levels of FIB and the distribution of sewage-associated bacteria, including potential pathogen

51 l water quality parameters, conventional and sewage-associated microbial indicators, and human pathog

52 icated that the proportion of sequences from sewage-associated taxa (SAT) or pathogen-like sequences

53 nd SR14 bacteriophages were present in human sewage at 2-4 orders of magnitude.

54 poser and flushing for management with other sewage at a wastewater treatment plant emits 0.10 kg of

55 xtend the QMRA approach to model mixtures of sewage at different ages using genetic marker concentrat

56 tment and low carbon-to-nitrogen (C/N) ratio sewage at the secondary biological treatment (SBT) has n

57 ere coordinated with the municipal water and sewage authority established to improve chlorination at

58 al analysis, stability of drug biomarkers in sewage, back-calculation of drug use (specific case of c

59 bic and aerobic microbial communities during sewage biological treatment.

60 Mn and Fe in Fe3O4@OMS-2@CTS changed during sewage biological treatment.

61 consumption through the chemical analysis of sewage biomarkers of illicit drugs.

62 oil) applied via a likely route of exposure, sewage biosolid application.

63 f environmental and human samples, including sewage, blood, and urine.

64 an populations are potentially excreted into sewage collection systems and concentrated in sewage slu

65 ectively account for nearly 35% of the total sewage community.

66 cetamiprid, and clothianidin as recalcitrant sewage constituents that persist through wastewater trea

67 to ZIKV infection when breeding in urine or sewage containing low concentrations of ZIKV.

68 or was calibrated and tested with tap water, sewage contaminated water, marine water, long lived sea

69 There are many "prehygiene" communities with sewage-contaminated water supplies, helminth infestation

70 he sterol ratios indicated a higher level of sewage contamination in the Santos Estuary.

71 This outbreak of HEV was likely caused by sewage contamination of the municipal water system.

72 rs may not be effective indicators when aged sewage contributes the majority of pathogens, relative t

73 ation) and TCS (methylation) occurred during sewage conveyance and treatment.

74 and previous studies suggest that sulfide in sewage could alter the activity of heterotrophic denitri

75 crobial risks, compared to NoV data from raw sewage coupled with wastewater treatment reduction estim

76 trometry (HRMS), we have identified over 500 sewage-derived contaminants occurring in the ocean.

77 enylacetate decarboxylase from an anaerobic, sewage-derived enrichment culture that quantitatively pr

78 to total event-based nitrate loads, although sewage-derived nitrate remained the dominant source (66%

79 ctionations into mixing models; up to 19% of sewage-derived samples showed the isotopic effects of de

80 ed was constructed, ultimately inverted, and sewage DIN inputs constrained using Monte Carlo simulati

81 The mean concentration from the expected sewage discharge scenario indicated that 12% by length o

82 inner part of the bay, directly affected by sewage discharges and where water circulation is more re

83 nylestradiol (EE2), are present in municipal sewage discharges.

84 uncertainties are related to the analysis of sewage drug biomarkers (uncertainty as relative standard

85 he RT-qPCR assays against RNA extracted from sewage effluent (n = 14), surface water (n = 30), and tr

86 ural) progestins have so far been studied in sewage effluent and surface waters.

87 emoval rates, were used to derive per capita sewage effluent values for the European countries .

88 e strongly indicative of denitrification and sewage effluent, corroborating a previously suggested li

89 om water pollution control plants (WPCPs) in sewage effluent.

90 d a complex environmental isolate of primary sewage effluent.

91 armaceuticals are active substances found in sewage effluents and can negatively impact aquatic syste

92 uggest that widespread discharge of domestic sewage entered directly into the estuary, preventing rem

93 nient biomarkers for NIC tracing through the sewage epidemiology approach at the local scale.

94 Sewage epidemiology is a rapidly expanding field that ca

95 stewater analysis (sometimes referred to as "sewage epidemiology") relates to the size and variabilit

96 od was used to collect 1.75 L of raw flowing sewage every 2-4 weeks.

97 es, and prospectively collected samples from sewage, farm slurry, and retail foodstuffs in London, Ea

98 m wastewater treatment plant (WWTP) influent sewage from 12 cities geographically distributed across

99 ound to effectively reduce sulfide levels in sewage from 12.7 +/- 0.3 to 0.2 +/- 0.0 mg S/L at a sulf

100 URA-protected areas, but also receives urban sewage from a large city through a manmade ditch.

101 acking sanitation infrastructure to separate sewage from drinking water.

102 iruses in the wells was leakage of untreated sewage from sanitary sewer pipes.

103 We quantified NoV and Escherichia coli in sewage from storm tank discharges and treated effluent p

104 3) The input of the newly increased sanitary sewage had a dominant influence on the quality and yield

105 on of MS2 to levels regularly encountered in sewage-impacted environments.

106 rkers were highly abundant in raw sewage and sewage-impacted water samples.

107 bacteriophage MS2, a virus often detected in sewage-impacted water supplies.

108 nify a health risk from enteric pathogens in sewage-impacted waters.

109 he risk cleaning products pose to health and sewage in Merida, a city in the Yucatan peninsula of Mex

110 hat multiple pathogens have been detected in sewage, including SARS-CoV-2, providing significant oppo

111 e and Ruminococcaceae for their potential as sewage indicators.

112 than the measured fluxes indicating that the sewage infrastructure of Boston diverts watershed DSi to

113 In contrast, fecal- and sewage infrastructure-derived microbes progressively dec

114 ecreased water flow months were dominated by sewage inputs and soil-related organisms.

115 Sewage inputs significantly contributed to the higher ab

116 Further, they highlight the importance of sewage inputs to DIN budgets in urban streams, particula

117 sewer overflows (SSOs) occur when untreated sewage is discharged into water sources before reaching

118 ethyl-mono-(di;tri) sulfide are important in sewage-like odors of pit latrines under anaerobic condit

119 The use of some of these chemicals as sewage molecular markers was also investigated.

120 ficult in low-income countries with informal sewage networks.

121 influences of the paved runoff and sanitary sewage on the DOM quality of WWF using excitation-emissi

122 fficient at removing organic pollutants from sewage or so-called grey water.

123 off is redirected to the combined stormwater-sewage overflow system.

124 arded as indicators to identify the types of sewage overflows and the illicit connection status of dr

125 st a potential health impact associated with sewage overflows.

126 Nigeria during June 2018-May 2019, including sewage physicochemical properties, using a water-quality

127 rated in local tap water and in effluents of sewage plants.

128 are recovering from industrial, mining, and sewage pollution during the 20th century.

129 to surface water DOM and characteristic of a sewage pollution influence.

130 common and frequently high impact sources of sewage pollution worldwide.

131 wed fipronil occurrence at 12-31 ng/L in raw sewage, primary effluent, secondary effluent, chlorinate

132 Simple measurement of sewage properties and catchment population estimation co

133 , and several Lachnospiraceae high-abundance sewage pyrotags occurred in at least 46 of 48 human faec

134 ts reveal substantial DIN contributions from sewage ranging from 6 to 14 kg ha-1 yr-1.

135 ctive when aged sewage was present, and aged sewage RBT estimates often fell below the marker lower l

136 Fresh sewage RBT estimates were not always protective when age

137 ormation, excretion, national water use, and sewage removal rates, were used to derive per capita sew

138 then applied to determination of PPCPs in a sewage sample and ASA and FP in drug preparations.

139 in 3 other major cities in 2011-2013); b. in sewage samples (27 from metropolitan Tel-Aviv, 14 from t

140 rences were observed for composite fecal and sewage samples (n = 147) by the LinRegPCR approach, corr

141 ociated markers were detected in 100% of the sewage samples analyzed.

142 uencing data obtained for viruses present in sewage samples and successfully detected multiple sub-po

143 The application of the method to composite sewage samples collected during 1 week in three differen

144 Stool specimens of AFP patients and sewage samples collected from 60 active environmental si

145 ients with acute flaccid paralysis (AFP) and sewage samples collected from 60 environmental sites wer

146 ting Clostridium coccoides (C. coccoides) in sewage samples demonstrated that Lachnospiraceae-annotat

147 phage, Bacteroides spp., and polyomavirus in sewage samples from 49 wastewater facilities across the

148 Sewage samples were all extremely high in virus concentr

149 Rates and types of polioviruses found in sewage samples were analyzed, and all poliovirus isolate

150 Sewage samples were collected from 27 environmental samp

151 Serial sewage samples were collected in 4 towns of Mexico befor

152 of 24 illicit drugs and metabolites in urban sewage samples.

153 HAV was detected in sewage samples: 16/27(59.2%) from Tel-Aviv; 4/14(28.6%)

154 circulating wild poliovirus (WPV) in Israel, sewage sampling detected WPV type 1 (WPV1) in April 2013

155 e steps at a wastewater treatment plant (raw sewage, secondary-treated sewage, and final effluent) mo

156 e first time, a novel quantitative community sewage sensor (namely DNA-directed immobilization of apt

157 the developed DDIAS can be used as community sewage sensors for rapid and cost-effective evaluation o

158 mmunities degrading BACs were developed from sewage (SEW), activated sludge (AS), soil (SOIL) and sea

159 In the United States, most of the treated sewage sludge (biosolids) is applied to farmland as a so

160 s, including via land application of treated sewage sludge (biosolids).

161 of ECs derived from pastures fertilized with sewage sludge (biosolids): a common global agricultural

162 In the U.S., the primary fate of processed sewage sludge (class B biosolids) is application to agri

163 Land application of stabilized sewage sludge (known as biosolids) can contribute PBDEs

164 To relieve the environmental issues of sewage sludge (SS) disposal and greenhouse gas (GHG) emi

165 late versus dissolved) added to the digested sewage sludge affects the fate of the metals during inci

166 (4-NP), a common nonionic detergent found in sewage sludge amended soils.

167 Sewage sludge and biosolids production and management ar

168 he concentrations of 69 elements in digested sewage sludge and effluent samples from 64 municipal was

169 valuable information for risk assessment of sewage sludge application on agricultural soils.

170 environment either in effluent wastewater or sewage sludge applied to land.

171 Sewage sludge ash (SSA) is a prospective phosphorus sour

172 However, the sewage sludge ash (SSA) is almost completely disposed of

173 in conventional anaerobic digesters treating sewage sludge at wastewater treatment plants globally.

174 trations of parabens also were determined in sewage sludge collected from several wastewater treatmen

175 Sewage sludge drying contributes 25% to emissions, soils

176 o standard ecotoxicity media, and in primary sewage sludge for a period of up to 48 h.

177 (Hydro)thermal treatments of sewage sludge from wastewater treatment process can sign

178 HT pretreatment of sewage sludge had a weak effect on the sulfidation of Fe

179 Resource recovery from sewage sludge has the potential to save natural resource

180 tural residues, animal manure, biowaste, and sewage sludge in 2010 and 2030 was assessed for Europe.

181 a trees, fertilized (or not) with dehydrated sewage sludge in a degraded area.

182 2 (SARS-CoV-2) RNA concentrations in primary sewage sludge in the New Haven, Connecticut, USA, metrop

183 ra, and values as high as 0.8 were found for sewage sludge incinerated at 800 degrees C in a syntheti

184 dress the transformation of Cu and Zn during sewage sludge incineration and evaluate whether the form

185 Thus, the behavior of Ag-NP during sewage sludge incineration is essential for a comprehens

186 rapid formation of Ag(0)-NP from Ag2S during sewage sludge incineration, as demonstrated in this stud

187 o address the transformation of Ag-NP during sewage sludge incineration, we spiked metallic Ag(0)-NP

188 environmental performance of wastewater and sewage sludge management is commonly assessed using life

189 currently the most important strategies for sewage sludge management.

190 and sandy clay loam) that were amended with sewage sludge or poultry manure and cropped with lettuce

191 Nutrients from dehydrated sewage sludge play an essential role in the development

192 gh the addition of chemical additives during sewage sludge processing.

193 The amount of sewage sludge produced worldwide is expected to further

194 eatment of nitrogen removal via nitrite from sewage sludge reject water.

195 shotgun viral metagenomics was applied to 10 sewage sludge samples from 5 wastewater treatment plants

196 eries of the four SCCP, MCCP and LCCP-spiked sewage sludge samples ranged from 86 to 123%.

197 During anaerobic digestion of sewage sludge supplemented with CO added through a hollo

198 onmental Protection Agency Targeted National Sewage Sludge Survey data from 2006 to 2007 revealed hig

199 ental Protection Agency in its 2001 national sewage sludge survey.

200 issolved ZnSO(4) into anaerobically digested sewage sludge to reach Cu and Zn concentrations of ~2500

201 apus, and Hordeum vulgare, after exposure to sewage sludge treated with nano-Ag (NM300 K at 1.8 and 7

202 A novel technology for simultaneous sewage sludge treatment and CO biomethanation in an anae

203 Critics suggest that rules regulating sewage sludge treatment and land application may be insu

204 tituent of excess sludge produced by Aerobic Sewage Sludge Treatment plants.

205 This study highlights the potential for sewage sludge treatment processes to affect the risk of

206 is) and hydrothermal treatments of municipal sewage sludge using complementary chemical extraction an

207 , and S during sequential HT-AD treatment of sewage sludge using sequential chemical extraction, X-ra

208 Australian sewage sludge was dominated by MCCPs with concentrations

209 unts of each isomer were added separately to sewage sludge which provided the electron-donating subst

210 in decision making about land application of sewage sludge will strengthen environmental health prote

211 ilabilities of P as a response to manure and sewage sludge with a range of P capture and hygienizatio

212 of infection from exposure to wastewater and sewage sludge, and represent a significant leap forward

213 ped, and the chemicals were analyzed in air, sewage sludge, and sediment.

214 Thermo-chemically treated municipal sewage sludge, as well as diatomaceous earth, did not re

215 sh and carbonized wood shavings, pig manure, sewage sludge, carbon nanotubes, and activated carbon.

216 ourcing digital wearable data and monitoring sewage sludge, might be helpful.

217 gged, and safe) of a complex matrix, such as sewage sludge, regarding their impacts on the chemical s

218 ses were found to accumulate as fragments in sewage sludge, resulting in an estimated accumulation of

219 CPs (SCCPs, MCCPs, and LCCPs) in Australian sewage sludge, we applied and further validated a recent

220 water treatment plants and accumulate in the sewage sludge, which is commonly digested.

221 421 ng/g dw) were detected in the Australian sewage sludge, which were comparable with the LCCPs conc

222 agmentation or following land application of sewage sludge-derived biosolids.

223 utinely measuring SCCPs, MCCPs, and LCCPs in sewage sludge.

224 lvent for obtaining maximum information from sewage sludge.

225 of several organic micropollutants (OMPs) in sewage sludge.

226 st time that CPs were reported in Australian sewage sludge.

227 cipal sewer system largely accumulate in the sewage sludge.

228 ic sludge digestion, and land application of sewage sludge.

229 d manufacturing byproducts of TCC and TCS in sewage sludge.

230 byproducts of TCC and TCS in raw and treated sewage sludge.

231 materials such as municipal waste, wood and sewage sludge.

232 17 RNA) different types of human viruses in sewage sludge.

233 ewage collection systems and concentrated in sewage sludge.

234 gum Bayram, a strain isolated from activated sewage sludge.

235 cation on US agricultural soils contained in sewage sludge.

236 e higher on trees fertilized with dehydrated sewage sludge.

237 chnology for enhanced resource recovery from sewage sludge.

238 char, ash, diatomaceous earth, and municipal sewage sludge.

239 ts in the majority becoming entrained in the sewage sludge.

240 ia argentea trees fertilized with dehydrated sewage sludge; such a better ecological indices in ferti

241 U.S. sewage sludges were analyzed for 58 regulated and nonreg

242 been detected in oceans, rivers, sediments, sewages, soil and even table salts.

243 fety: bacteria are exposed to MNMs in water, sewage, soils, and sediments, wherein they influence MNM

244 ive against Ent. faecalis, it is not for the sewage-source organisms.

245 during baseflow conditions and indicate that sewage-sourced DIN is not limited to sewer overflow even

246 faecalis, but depressed photoinactivation of sewage-sourced enterococci and E. coli after correcting

247 The decay of sewage-sourced Escherichia coli and enterococci was meas

248 4% of nitrate in streamwater originated from sewage sources during baseflow conditions.

249 s with a particular focus on detecting human sewage sources of contamination.

250 sterols originating from human and nonhuman sewage sources.

251 her than nonhost specific RYC2056 phages and sewage-specific KS148 phages (p < 0.05).

252 We developed sewage-specific microbial source tracking (MST) tools us

253 and molecular analysis of polioviruses from sewage specimens monitored the duration of vaccine-relat

254 been declared polio-free in 1988, a routine sewage surveillance program detected polio in 2013.

255 nd are released into the environment via the sewage system.

256 d-off of urban surfaces and emissions to the sewage system.

257 fide is found in many environments including sewage systems, petroleum extraction platforms, kraft pa

258 and heat losses from basements of buildings, sewage systems, subsurface district heating networks, an

259 re, we use metagenomic analysis of untreated sewage to characterize the bacterial resistome from 79 s

260 eational water, ingestion of cross-connected sewage to drinking water, and shower exposures to DBPs.

261 e results highlight the utility of analyzing sewage to monitor shedding of viral pathogens and the hi

262 ssolved inorganic nitrogen (DIN) inputs from sewage to Nine Mile Run (NMR), an urban watershed (1570

263 r pipelines, although primarily designed for sewage transport, can also be considered as bioreactors.

264 l DSi year(-1)) indicate that the process of sewage treatment at DITP likely does not remove DSi.

265 racteristics sampled at the inlet basin of a sewage treatment plant (STP).

266 In some cases, disposal to a sewage treatment plant may be favored, but plant perform

267 The determination of phosphate at a sewage treatment plant was carried out to demonstrate a

268 rations found in proximity to a metropolitan sewage treatment plant, a wood-related industrial area,

269 ective electrode installed at the inlet of a sewage treatment plant, showed a distinctive pattern whi

270 tory and field experiments at a conventional sewage treatment plant, we determined the environmental

271 surface water and wastewater samples from a sewage treatment plant.

272 ion (n = 21), to levels above 600 ng/m(3) at sewage treatment plants (n = 2).

273 products were quantified in influents of ten sewage treatment plants (STP) serving populations rangin

274 cals are not readily removed in conventional sewage treatment plants (STP), additional STP effluent t

275 e raw wastewater samples were collected from sewage treatment plants (STPs) in 17 cities.

276 to reduce MPs in the effluents of municipal sewage treatment plants (STPs).

277 PA sensor was also employed at two different Sewage Treatment Plants in Chennai, Tamilnadu, India, wh

278 affic-related variables but the proximity to sewage treatment plants was present in all models indica

279 We developed an empirical model to estimate sewage treatment prevalence for 47 additional countries.

280 in 2010; of these, 77 had published data on sewage treatment prevalence.

281 is more likely to occur with septic tanks as sewage treatment systems especially in karstic terrains.

282 as a groundwater infiltration tracer within sewage treatment systems, and highlights the underapprec

283 derrepresented compounds (e.g., fragrances), sewage treatment techniques (e.g., septic systems), and

284 to review trends in diversity of compounds, sewage treatment techniques (STTs), and ecosystems inves

285 eroid estrogens in effluents from Australian sewage treatment works and a receiving river were predic

286 During sewage treatment, the lenses were found to accumulate as

287 adopt costly technology, in our case on-site sewage treatment, was up to a degree capable of compensa

288 tandardized questionnaires collected from 19 sewage treatments plants (STPs) and the results of an in

289 hages (536_P1 and 536_P7) were isolated from sewage using strain 536, a highly virulent extraintestin

290 056, respectively, were predicted when fresh sewage was greater (by volume) than aged at the time of

291 timates were not always protective when aged sewage was present, and aged sewage RBT estimates often

292 ewerage as "improved sanitation" only if the sewage was treated before discharge to the environment.

293 eful management of sources from urban input, sewage waste and irrigation runoff.

294 olice samples, biological fluids and hair to sewage water has risen.

295 The concentrations of crAssphage in raw sewage were positively correlated with the concentration

296 from 10 plants in direct receipt of hospital sewage were significantly higher than 10 plants that wer

297 component occurred in the reserved sanitary sewage, while a type of longer emission wavelength (em:

298 as marker genes), we sampled poultry, dogs, sewage, wild birds and flies.

299 f paved runoff and point sources of sanitary sewage within the drainage networks.

300 00% specificity and 90% sensitivity to human sewage without detecting 68 animal manure pooled samples