ライフサイエンスコーパス: biosolid

1 O2 introduced was observed to associate with biosolids.

2 exposure and risk assessment of land-applied biosolids.

3 from biosolids, or more specifically lagoon biosolids.

4 nments through the land application of these biosolids.

5 ng land application of sewage sludge-derived biosolids.

6 nderstanding the pathogen content of class B biosolids.

7 abundant organic micropollutants detected in biosolids.

8 pharmaceuticals in wastewater effluents and biosolids.

9 pharmaceuticals in complex matrices such as biosolids.

10 wastewater effluent and prevents transfer to biosolids.

11 ge and runoff following land applications of biosolids.

12 n environment between ENM and bulk/dissolved biosolids.

13 indicating significant metal accumulation in biosolids.

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

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

16 , and be discharged with treated effluent or biosolids.

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

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

19 llutants associated with land-application of biosolids.

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

21 nanomaterials pose from land application of biosolids.

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

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

24 mpacts of nonregulated contaminants found in biosolids.

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

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

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

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

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

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

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

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

33 Biosolid-amended soil exhibited increased concentrations

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

55 s through land application of nanocontaining biosolids and agrochemicals.

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

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

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

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

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

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

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

63 eiving CBZ through wastewater irrigation and biosolid application.

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

65 Biosolids application on agricultural fields increased P

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

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

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

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

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

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

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

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

74 Biosolids-associated PBDE bioavailability was lower than

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

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

77 Biosolids biochar had the worst relative environmental p

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

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

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

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

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

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

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

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

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

87 Biosolids contain a variety of pharmaceuticals and perso

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

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

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

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

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

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

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

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

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

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

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

99 termination of antidepressants in the lagoon biosolid extracts.

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

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

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

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

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

105 Amendment of biosolids further suppressed mineralization.

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

107 ther carbon sequestration opportunity during biosolids handling.

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

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

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

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

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

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

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

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

116 soils through reclaimed water irrigation and biosolid land applications.

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

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

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

120 cording to physicochemical properties of the biosolids microstructure.

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

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

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

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

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

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

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

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

129 Treatments included biosolids produced using a pilot wastewater treatment pl

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

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

132 Wastewater biosolids pyrolysis is a promising technology that could

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

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

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

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

137 Biosolid samples were analyzed following the dilution of

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

139 sant and degradation product detected in the biosolid samples.

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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