ライフサイエンスコーパス: biosolid

1 a land application of treated sewage sludge (biosolids).

2 nanomaterials pose from land application of biosolids.

3 en being reported here for the first time in biosolids.

4 her rate in the presence of a plant and WWTP biosolids.

5 mpacts of nonregulated contaminants found in biosolids.

6 O2 introduced was observed to associate with biosolids.

7 exposure and risk assessment of land-applied biosolids.

8 from biosolids, or more specifically lagoon biosolids.

9 nments through the land application of these biosolids.

10 ng land application of sewage sludge-derived biosolids.

11 nderstanding the pathogen content of class B biosolids.

12 pharmaceuticals in wastewater effluents and biosolids.

13 pharmaceuticals in complex matrices such as biosolids.

14 r flow, and land application of contaminated biosolids.

15 scharges to the environment via effluent and biosolids.

16 cy across chain lengths in water, blood, and biosolids.

17 stion had only 1% of the initial QACs in the biosolids.

18 c fertilizers with organic alternatives like biosolids.

19 tment plants generate a solid waste known as biosolids.

20 abundant organic micropollutants detected in biosolids.

21 wastewater effluent and prevents transfer to biosolids.

22 ge and runoff following land applications of biosolids.

23 n environment between ENM and bulk/dissolved biosolids.

24 indicating significant metal accumulation in biosolids.

25 h have been detected in WWTP and paper fiber biosolids.

26 t to 75% (range: 12-96%) of the total TEQ in biosolids.

27 , and be discharged with treated effluent or biosolids.

28 concentration that has been detected in U.S. biosolids.

29 on the redox state and water content of the biosolids.

30 llutants associated with land-application of biosolids.

31 centration of 504 +/- 417 ng/g dry weight of biosolids.

32 umulation of endogenous PFCAs present in the biosolids (0.1-138 ng/g wet weight (ww)) and those produ

33 ion (0.198 kWh) and incineration of residual biosolids (0.153 kWh); and also achieved a negative carb

34 introduced into the influent wastewater (ENM biosolids), (2) AgNO3, Zn(SO4)2, and micron-sized TiO2 (

35 ng from the background concentration of seed biosolids (30 mg/kg) to toxic concentrations of 850 mg/k

36 from pastures fertilized with sewage sludge (biosolids): a common global agricultural practice.

37 mended with a Class B anaerobically digested biosolid (ADB), an exceptional quality composted biosoli

38 cular formulas unique to these biosolids and biosolid amended soils.

39 Comparison of metal adsorption edges on the biosolid-amended soil and the soil sample showed that Cu

40 cation will increase metals retention in the biosolid-amended soil by providing reactive organic matt

41 Biosolid-amended soil exhibited increased concentrations

42 r plays a dominant role in Ni binding in the biosolid-amended soil, it was of lesser importance for C

43 e speciation of copper, nickel and zinc in a biosolid-amended soil.

44 concentrations were significantly higher in biosolid-amended soils (average of 1137 MPs/kg) than in

45 an environmentally relevant concentration in biosolid-amended soils.

46 trol of the long-term stability of metals in biosolid-amended soils.

47 ate that rainfall can mobilize hormones from biosolids-amended agricultural fields, directly to surfa

48 presence of perfluoroalkyl acids (PFAAs) in biosolids-amended and aqueous film-forming foam (AFFF)-i

49 soil were collected from several full-scale biosolids-amended farm fields.

50 compartments of crops grown in the municipal biosolids-amended soil and in the control soil were less

51 uptake of perfluoroalkyl acids (PFAAs) from biosolids-amended soil has been identified as a potentia

52 lity of Dynamic Plant Uptake (DPU) model and Biosolids-amended Soil Level IV (BASL4) model to predict

53 eight PPCPs in the tissue of plants grown in biosolids-amended soil under a number of exposure scenar

54 persicum ) grown in an industrially impacted biosolids-amended soil, a municipal biosolids-amended so

55 As (a control soil, an industrially impacted biosolids-amended soil, a municipal biosolids-amended so

56 . macrocarpon) from an industrially impacted biosolids-amended soil, a municipal biosolids-amended so

57 impacted biosolids-amended soil, a municipal biosolids-amended soil, and a control soil was measured.

58 impacted biosolids-amended soil, a municipal biosolids-amended soil, and a control soil.

59 impacted biosolids-amended soil, a municipal biosolids-amended soil, and two AFFF-impacted soils) was

60 firms that the bioaccumulation of PFAAs from biosolids-amended soils depends strongly on PFAA concent

61 o the occurrence and fate of nitrosamines in biosolids-amended soils in the context of crop and drink

62 igated with reclaimed wastewater or grown in biosolids-amended soils may take up pharmaceuticals and

63 ved the uptake of PPCPs into plants grown in biosolids-amended soils.

64 6.7% vs ~1%) and higher bioavailability than biosolids-amended soils.

65 ula A17 were monitored following exposure to biosolids-amended soils.

66 om Florida pastures with differing levels of biosolid amendment and an adjacent control site.

67 Experiments consisted of six biosolid amendment treatments, including Mizzou Doo comp

68 Among the six biosolid amendments examined, SMC and MD treatments were

69 to stabilize Pb using phosphate (P)-enriched biosolid amendments in the contaminated mining wastes) l

70 isk reduction in mining wastes by P-enriched biosolid amendments was long-term and environmental-soun

71 nd their distinctive variations in different biosolid amendments.

72 The increasing application of biosolids and agrochemicals containing silver nanopartic

73 s through land application of nanocontaining biosolids and agrochemicals.

74 297 molecular formulas were present only in biosolids and amended soil leachates (i.e., not present

75 dentified molecular formulas unique to these biosolids and biosolid amended soils.

76 Historical municipal biosolids and composts were dominated by perfluorooctane

77 le that could be in contact with NPs through biosolids and direct agrichemical application.

78 or dissolved in agricultural lands receiving biosolids and in freshwater or marine sediments.

79 Based on the measured concentrations in biosolids and predicted mass in wastewater, it was estim

80 r treatment process and likely accumulate in biosolids and sludge.

81 el tracers of biosolids, characterization of biosolids and their impacts on OM composition in recipie

82 ence of carbamazepine and its metabolites in biosolids and underscore the importance of optimizing sl

83 served in the environment (e.g., wastewater, biosolids) and in human blood using high-throughput in v

84 compounds is retained in the sewage sludge (biosolids), and due to its high content of nutrients, sl

85 Agricultural use of treated wastewater, biosolids, and animal wastes introduces a multitude of c

86 d PBAT were commonly detected in wastewater, biosolids, and sediment samples at concentrations betwee

87 patial trend between EPFAS and distance from biosolid application or well characteristics.

88 mponents (clay minerals and organic matter), biosolid application will increase metals retention in t

89 plied via a likely route of exposure, sewage biosolid application.

90 eiving CBZ through wastewater irrigation and biosolid application.

91 Runoff samples collected prior to biosolids application had low concentrations of two horm

92 ristics, and transport of MPs resulting from biosolids application in two Queensland agricultural sit

93 Biosolids application on agricultural fields increased P

94 the development of guidelines for acceptable biosolids application rates.

95 runoff samples taken 1, 8, and 35 days after biosolids application.

96 me, time since application, and frequency of biosolids application.

97 strels) consumers, after repeated, long-term biosolids application.

98 tion of wastewater treatment residual (i.e., biosolid) applications to watersheds can alter the amoun

99 ted effluent discharged to surface waters or biosolids applied to agricultural land, incinerated wast

100 Hierarchical cluster analysis identified biosolid-applied fields, WTTPs, and industrial discharge

101 Biosolids are a byproduct of wastewater treatment that c

102 rticles (Ag2S-NPs) when wastewater treatment biosolids are applied as fertilizer to agricultural soil

103 The resulting biosolids are either used as fertilizer or incinerated.

104 Biosolids are nutrient-rich and inexpensive soil amendme

105 optimization and may also be beneficial when biosolids are used for contaminated site remediation.

106 When treated wastewater and biosolids are used in agriculture, CECs and their transf

107 s the practice of applying treated sludge or biosolids as a potential source of these chemicals onto

108 armaceuticals in the environment, the use of biosolids as fertilizer is a potential route for antidep

109 environment and establishing wastewater and biosolids as vectors for MP transport and delivery.

110 detection, evaluation, and prioritization of biosolid-associated organic contaminants (BOCs).

111 e; perhaps due to low bioavailability of the biosolids-associated flame retardants.

112 Biosolids-associated PBDE bioavailability was lower than

113 il amended with only a single application of biosolids (at an agronomic rate for nitrogen) were predo

114 Our findings revealed that EBPR biosolid augmentation promoted the best maize shoot grow

115 Biosolid augmentation significantly impacted the rhizomi

116 Results suggest that HUDF and biosolid-based fertilizers are equally preferred and mor

117 oncentration ranges observed are as follows: biosolid-based products (9.0-199 mug/kg) > food and yard

118 ealed the presence of PFAA precursors in the biosolid-based products at much higher levels, when the

119 olids, while sales in commercially available biosolid-based products used as soil amendments are also

120 (PFAAs) present in 13 commercially available biosolid-based products, six organic composts (manure, m

121 epresentative samples and the amount of U.S. biosolids being applied on land as soil amendment, this

122 Biosolids biochar had the worst relative environmental p

123 from the production and use of wood biochar, biosolids biochar, and coal-derived PAC to remove sulfam

124 Among all known DLCs determined in biosolids, brominated analogs contributed 370% more TEQ

125 kyl substances (PFAS) are well documented in biosolids, but limited information is available on how b

126 Zn3(PO4)2 persisted in sludge and biosolids, but the ratio of ZnS and Zn associated with F

127 Phosphorus (P) recovery from biosolids can play an important role in a circular econo

128 cation of stabilized sewage sludge (known as biosolids) can contribute PBDEs to terrestrial systems.

129 olid (ADB), an exceptional quality composted biosolid (CB), PBDE-containing polyurethane foam (PUF) m

130 To identify novel tracers of biosolids, characterization of biosolids and their impac

131 An acidic pH reduced the biosolids charge while simultaneously increasing the dew

132 ive of this study was to quantify 92 PFAS in biosolids collected from eight biosolids treatment facil

133 ne, and two of their selected metabolites in biosolids collected from four wastewater treatment plant

134 ing from 83.6 to 2490 ng/g dw, were found in biosolids collected from the northeastern United States.

135 Ni, and Zn can be retained by both soil and biosolid components such as amorphous iron phases, organ

136 wo PBDDs and five PBDFs were detected in the biosolids composites at varying frequencies (40-100%) wi

137 Median biosolid concentrations were substantial (26-430 mg QAC/

138 Biosolids contain a variety of pharmaceuticals and perso

139 inexpensive soil amendments, however, if the biosolids contain PFAS which are known to be toxic, mobi

140 s of applications of soil amendments such as biosolids containing NPs or nano-enabled formulations us

141 Monitoring sludge/biosolids contaminant burdens may be valuable in reveali

142 articulate Ag from a field soil amended with biosolids contaminated with engineered silver nanopartic

143 neered processes (e.g., anaerobic digestion, biosolids decomposition in soils) that result in cellula

144 A novel pyrolysis process using wastewater biosolids-derived biochar (WB-biochar) as a catalyst was

145 ntrol Act, in determining the ecotoxicity of biosolids-derived emerging contaminants.

146 This study demonstrates that biosolids-derived TCC and TCS are present throughout the

147 The method was applied to biosolids destined for land application.

148 presence of perfluoroalkyl acids (PFAAs) in biosolids destined for use in agriculture has raised con

149 aminant metals (copper, zinc and cadmium) in biosolids destined for use in agriculture.

150 Composting all biosolids dramatically reduced the GWP relative to the b

151 ironmental performance due to energy use for biosolids drying and the need for supplemental adsorbent

152 The production of sludge (biosolids) during wastewater treatment is a major issue

153 ased into the Australian environment through biosolids end-use each year, equating to approximately 2

154 d emission estimate of plastic types through biosolids end-use.

155 The biosolid endmember was further constrained by extracting

156 termination of antidepressants in the lagoon biosolid extracts.

157 cumulate in soils through the application of biosolid fertilizers.

158 taining the test plots had been applied with biosolids for the first time immediately prior to this s

159 verius) at an experimental site amended with biosolids for the previous 7 years.

160 the same types of samples from a reference (biosolids-free) agricultural site.

161 In archived Chicago area sludges/biosolids from 1975 to 2008, penta-BDE concentrations in

162 ence of eight carcinogenic N-nitrosamines in biosolids from 74 wastewater treatment plants (WWTPs) in

163 Amendment of biosolids further suppressed mineralization.

164 Treatments consisted of soils amended with biosolids generated with (1) Ag, ZnO, and TiO2 ENMs intr

165 ther carbon sequestration opportunity during biosolids handling.

166 While the use of TWW and biosolids has many societal benefits, introduction of PP

167 evaluated within a test plot at a site where biosolids have been historically land-applied.

168 steroid hormones in runoff from sites where biosolids have been used as agricultural fertilizers is

169 At biosolids-impacted sites, the presence of active ingredi

170 urface water relative to land application of biosolids in a tile-drained agriculture-dominated waters

171 The use of sludge (biosolids) in land application may contribute to the spr

172 um of mean concentrations of nitrosamines in biosolids increased with the treatment capacity of WWTPs

173 ion of BADGE, NOGE, and their derivatives in biosolids increased with the treatment capacity of WWTPs

174 ation among NP-dosed, ion-dosed, and control biosolids indicate that these nanoparticles are transfor

175 S. regulations limit metals and pathogens in biosolids intended for land applications, no organic con

176 treated wastewater (TWW) and application of biosolids introduce numerous pharmaceutical and personal

177 and micron-sized TiO2 (dissolved/bulk metal biosolids) introduced into the influent wastewater strea

178 ence of pharmaceutical residues in municipal biosolids is an emerging environmental concern due to th

179 The most common management option for biosolids is to beneficially reuse them as an agricultur

180 ary fate of processed sewage sludge (class B biosolids) is application to agricultural land as a soil

181 d States, most of the treated sewage sludge (biosolids) is applied to farmland as a soil amendment.

182 soils through reclaimed water irrigation and biosolid land applications.

183 ed groundwater (AFFF-GW), landfill leachate, biosolids leachate, municipal wastewater treatment plant

184 oam-impacted groundwater, landfill leachate, biosolids leachate, municipal wastewater treatment plant

185 amined the molecular composition of soil and biosolid leachates and identified molecular formulas uni

186 Biosolids leachates were best classified along with land

187 Overall, biosolids leachates were enriched in aliphatic (+16.3% r

188 from 2006 to 2007 revealed highest penta-BDE biosolids levels from western and lowest from northeaste

189 nefits of sidestream nutrient management and biosolid management strategies following digestion of se

190 This study focused on the evaluation of biosolids management systems (BMS) from a natural resour

191 prior to making decisions in sidestream and biosolids management.

192 TCC concentrations of biosolids measured by the ELISA were similar to those de

193 cording to physicochemical properties of the biosolids microstructure.

194 s a key step in identifying novel tracers of biosolids movement through impacted watersheds.

195 prioritize BOCs present in U.S. and Canadian biosolids (n = 16).

196 untreated wastewater, landfill leachate, and biosolids (NY CARP data set) to determine whether peri a

197 s, and 770 tons were estimated to leave with biosolids, of which 640 tons are land applied or landfil

198 s study, we investigated the impacts of EBPR biosolids on crops growth and rhizomicrobiome in compari

199 eed to assess the long-term impact of MPs in biosolids on soil health and food safety.

200 did not differ between treatments receiving biosolids, one plant species, Microstegium vimeneum, had

201 lly reduced the GWP relative to the baseline biosolid option but had slightly higher eutrophication p

202 (PBDEs) and chlorinated paraffins (CPs) from biosolids or effluent.

203 late in organisms ingesting soils containing biosolids or waste plastics.

204 ntidepressants and degradation products from biosolids, or more specifically lagoon biosolids.

205 able rural wells based on their proximity to biosolid-permitted land and location with respect to gro

206 WWTPs and were significantly correlated with biosolid pH, organic carbon content, and oxidation-reduc

207 The metals contained in wastewater biosolids played an important role in upgrading pyrolysi

208 her studied by adding acid/base solutions to biosolids prior to ED.

209 logy to reduce the overall costs of residual biosolids processing, transport, and disposal.

210 e examined the effects of amending soil with biosolids produced from a pilot-scale wastewater treatme

211 Treatments included biosolids produced using a pilot wastewater treatment pl

212 Sewage sludge and biosolids production and management are a central compon

213 her it can be exploited to produce optimized biosolids products through the addition of chemical addi

214 Wastewater biosolids pyrolysis is a promising technology that could

215 micro-bioplastics in environmental samples (biosolids) ranged from 74 to 116%.

216 the postdigestion fossil carbon remained in biosolids rather than in biogas, offering yet another ca

217 ed, data on their transformation products in biosolids remain limited.

218 ory bodies require pathogen reduction before biosolids reuse.

219 e relative potential for economic value from biosolids revealed the identity of the 13 most lucrative

220 Deca-BDE concentrations in biosolids rose from 1995 to 2008, doubling on a 5-year i

221 and BFDGE.2 HCl) were determined in archived biosolid samples collected from 68 wastewater treatment

222 Biosolid samples were analyzed following the dilution of

223 Influent, effluent, and biosolid samples were collected from 12 wastewater treat

224 results from CIC analysis of real blood and biosolid samples were compared to targeted LC-MS/MS resu

225 ants was consistently detected in the lagoon biosolid samples, and thus antidepressants are being int

226 sant and degradation product detected in the biosolid samples.

227 rying detection frequency (DF) in 88% of the biosolids samples (n = 80), with five of the seven being

228 Biosolids samples collected from 82 wastewater treatment

229 A single biosolid sampling campaign was conducted across the four

230 rrestrial food web encompassing land-applied biosolids, soil, earthworms (Lumbricus), deer mice (Pero

231 observed in lettuce grown in a soil amended (biosolids:soil dry weight ratio of 1:10) with PFAA indus

232 strained by extracting water-soluble OM from biosolids sourced from four Florida wastewater treatment

233 roperties (e.g., organic matter and pH), and biosolids sources affected concentrations and types of P

234 bility of contaminant metals in good quality biosolids (suitable for use in agriculture), suggesting

235 Congener patterns in contemporary Chicago biosolids support the contention that BDE-209 can be deh

236 ercentage of the total PFAS concentration in biosolids than previously estimated.

237 ass spectrometry in the composited, archived biosolids that were collected in 32 U.S. states and the

238 ls conventionally amended for nutrients with biosolids (that are not impacted by PFAA industries) are

239 While PFAS precursors were present in biosolids, they were absent in treated soils, likely due

240 stems by applying wastewater treatment plant biosolids to agricultural fields.

241 for legislation governing the application of biosolids to agricultural land.

242 n use in Australia, the transfer of MPs from biosolids to agricultural soils remains largely unknown.

243 provides a novel perspective leveraging EBPR biosolids to facilitate plant growth with agronomic bene

244 ead land application of wastewater treatment biosolids to food crops, these findings forewarn of agri

245 Soils were amended with biosolids to simulate 20 years of metal loading, which r

246 upon application of compost and paper fiber biosolids to two farm fields.

247 gnificantly higher concentrations of PFAS in biosolids-treated (treatment) soils compared to (untreat

248 aising concerns beyond the boundaries of the biosolids-treated farms.

249 fy 92 PFAS in biosolids collected from eight biosolids treatment facilities before and after four pat

250 but limited information is available on how biosolids treatment processes impact PFAS.

251 Results indicated that, in all cases, the biosolid treatments resulted in significant reductions i

252 Ps and PFCAs present in WWTP and paper fiber biosolids upon amendment of these materials with soil th

253 PFAS) contamination in 10 farms treated with biosolids using a paired control-treatment approach.

254 resence of wastewater treatment plant (WWTP) biosolids using a unique FTACP determined to be a homopo

255 re determined in both fresh and 3-month aged biosolids using X-ray absorption spectroscopy (Cu, Zn) a

256 nanoparticles (NPs) are entering soils with biosolids via wastewater treatment, and on-route, underg

257 rmulations, the ratio of PBDD/Fs to PBDEs in biosolids was 55-times higher ( approximately 0.002% vs

258 soils as a result of the land application of biosolids was estimated at 720 g (range: 530-1600 g).

259 The DF of nitrosamines in biosolids was positively correlated with their respectiv

260 te-of-the-art of STH quantification in soil, biosolids, water, produce, and vegetation with regard to

261 eatment on metal speciation in the resulting biosolids were also examined.

262 henyl)methane) antimicrobial agents found in biosolids were analyzed.

263 soil amended with PFAA industrially impacted biosolids were highest for perfluorooctanoate (PFOA; 67

264 For many WWTPs, the mass loadings of QACs in biosolids were of similar magnitude as those in influent

265 near agricultural fields where contaminated biosolids were spread.

266 of 1:10) with PFAA industrially contaminated biosolids were up to 266 and 236 ng/g for perfluorobutan

267 r a community of 1 million people, metals in biosolids were valued at up to US$13 million annually.

268 er- and polyfluoroalkyl substances (PFAS) in biosolids, while sales in commercially available biosoli

269 raction of inorganic contaminants present in biosolids with iron, aluminum, and manganese oxy/hydroxi