ライフサイエンスコーパス: polychlorinated biphenyl

1 to 14.3; 50% of the database entries are for polychlorinated biphenyls.

2 um-impacted sediment and factors of 3-10 for polychlorinated biphenyls.

3 studied via the reductive dechlorination of polychlorinated biphenyls.

4 s, such as highly chlorinated pesticides and polychlorinated biphenyls.

5 to -0.8 mm Hg]), maternal concentrations of polychlorinated biphenyl 118 (-1.4 mm Hg [95% CI: -2.6 t

6 effects of diethylhexyl phthalate (DEHP) and polychlorinated biphenyl 153 (PCB153) on DNA fragmentati

7 l A (BPA), mono-n-butyl phthalate (Pht), and polychlorinated biphenyl 153 (PCB153) on the proteome of

8 lorodiphenyl dichloroethene (rho = 0.017) or polychlorinated biphenyl 153 (rho = -0.016), the other m

9 Polychlorinated biphenyl and organochlorine pesticide co

10 the method by revisiting a data set relating polychlorinated biphenyls and 1,1-dichloro-2,2-bis(p-chl

11 Fifteen polyaromatic hydrocarbons, seven polychlorinated biphenyls and eight organochlorine pesti

12 Differences in K(EOM/olive oil) of two polychlorinated biphenyls and four chlorinated benzenes

13 uty creams, dioxin in waste oil in Missouri, polychlorinated biphenyls and multiple other toxic chemi

14 Epidemiological and laboratory studies link polychlorinated biphenyls and their metabolites to adver

15 termine whether early-life exposure to PCBs (polychlorinated biphenyls) and DDE [1,1-dichloro-2,2-bis

16 tty acids, not persistent pollutants such as polychlorinated biphenyls, and none have evaluated Great

17 he reporting back of results regarding lead, polychlorinated biphenyls, and phthalates.

18 orodiphenyltrichloroethanes and chlordanes), polychlorinated biphenyls, and polybrominated diphenyl e

19 Polychlorinated biphenyls are among the most well-studie

20 Although polychlorinated biphenyls are no longer sold as commerci

21 thalates and persistent contaminants such as polychlorinated biphenyls are thought to influence tissu

22 pmental neurotoxicants: lead, methylmercury, polychlorinated biphenyls, arsenic, and toluene.

23 Next, we use benzene and polychlorinated biphenyls as examples to illustrate how

24 The loss rates of vapor phase polychlorinated biphenyls became more rapid between 1995

25 sessed these links by measuring and modeling polychlorinated biphenyl bioaccumulation by four marine

26 nt during a 28 day bioaccumulation test with polychlorinated biphenyls, chlorpyrifos, and four marine

27 s (or features) were compared with the total polychlorinated biphenyl concentration trends.

28 sex, age at TSH measurement, maternal serum polychlorinated biphenyl concentration, or mode of deliv

29 Polychlorinated biphenyl concentrations are decreasing i

30 ssociations of peripubertal serum dioxin and polychlorinated biphenyl concentrations with pubertal ti

31 realistic emission estimates (1930-2100) for polychlorinated biphenyl congener 153 (PCB-153).

32 lip-sil ranged from 13.6 to 40.0 g g(-1) for polychlorinated biphenyl congeners 28-156 (CB28 and CB15

33 Sampling rates are evaluated for polychlorinated biphenyl congeners at a network of Harne

34 e thermodynamic levels of HOCs, for example, polychlorinated biphenyl congeners, dichlorodiphenyltric

35 ted behaviors among children living near the polychlorinated biphenyl-contaminated New Bedford Harbor

36 orinated dibenzofurans (PCDFs), and coplanar polychlorinated biphenyls (CP-PCBs) concentrations and a

37 The analytes of interest were polychlorinated biphenyls, DDTs, chlordanes, dieldrin, a

38 Rhodococcus jostii RHA1, a polychlorinated biphenyl-degrading soil bacterium whose

39 and dibenzofurans (PCDD/Fs) and dioxin like polychlorinated biphenyls (dl-PCB) is evaluated for the

40 inated dibenzofurans (PCDFs) and dioxin-like polychlorinated biphenyls (dl-PCBs) in the Pilica River

41 dioxins and furans (PCDD/Fs) and dioxin-like polychlorinated biphenyls (dl-PCBs) were measured in pla

42 a two end-member mixing model with DDTs and polychlorinated biphenyls enabled source differentiation

43 are serum concentrations of PBDEs, OH-PBDEs, polychlorinated biphenyl ethers (PCBs) (structurally sim

44 a, to build predictive models for cord serum polychlorinated biphenyls (expressed as a sum, [Formula:

45 gher air concentrations, at lower altitudes (polychlorinated biphenyls, gamma-hexachlorocyclohexane),

46 y pollutants in Alpine glaciers, we analyzed polychlorinated biphenyls in an ice core from the temper

47 ated against measured concentrations of five polychlorinated biphenyls in different-size fish depurat

48 nzene (HCB), total chlordane, and SigmaPCBs (polychlorinated biphenyls) in osprey tissues was explain

49 s of contaminants that mainly originate from polychlorinated biphenyl metabolism.

50 Non-dioxin-like polychlorinated biphenyls (NDL-PCBs) contribute to the d

51 e aminated aptamer selected for hydroxylated polychlorinated biphenyl (OH-PCB) was covalently immobil

52 Hydroxylated polychlorinated biphenyls (OH-PCBs) are an important cla

53 Hydroxylated metabolites of polychlorinated biphenyls (OH-PCBs) have been found to b

54 Hydroxylated polychlorinated biphenyls (OH-PCBs) were measured in sur

55 Some POPs, i.e., hydroxylated metabolites of polychlorinated biphenyls (OH-PCBs), pentachlorophenol (

56 We also conducted an indoor calibration for polychlorinated biphenyls on the same type of PAS using

57 espiring bacteria, with substrates including polychlorinated biphenyls or dioxins.

58 Plasma concentrations of summed polychlorinated biphenyls, organochlorine pesticides, an

59 ragrance compounds, methyl triclosan (MTCS), polychlorinated biphenyls, organochlorine pesticides, an

60 We measured polychlorinated biphenyls, organochlorine pesticides, po

61 nd concentrations of dioxins, dibenzofurans, polychlorinated biphenyls, organochlorines, organophosph

62 jor endocrine disruptor classes:bisphenol A, polychlorinated biphenyls, organophosphates, and polybro

63 We evaluated the association of polychlorinated biphenyl (PCB) and dichlorodiphenyldichl

64 nvestigated the association between prenatal polychlorinated biphenyl (PCB) and p,p'-dichlorodiphenyl

65 Here, we examined polychlorinated biphenyl (PCB) and polybrominated diphen

66 Polychlorinated biphenyl (PCB) and polybrominated diphen

67 Physical partitioning of polychlorinated biphenyl (PCB) and polybrominated diphen

68 , in explaining interspecific differences in polychlorinated biphenyl (PCB) body concentrations betwe

69 orted an association between higher maternal polychlorinated biphenyl (PCB) concentrations and smalle

70 one by following the short-term evolution of polychlorinated biphenyl (PCB) concentrations in water a

71 lence in relation to serum concentrations of polychlorinated biphenyl (PCB) congener groups and three

72 excretion (ADME) processes in fish can alter polychlorinated biphenyl (PCB) congener patterns in fish

73 ed with TMFs of several legacy contaminants: polychlorinated biphenyl (PCB) congeners 153 and 180, po

74 Air-water exchange gradients of selected polychlorinated biphenyl (PCB) congeners across a large

75 . the relative importance of low-chlorinated polychlorinated biphenyl (PCB) congeners and some OC-pes

76 We measured the concentrations of 205 polychlorinated biphenyl (PCB) congeners in 26 food item

77 ere investigated as sorbent materials for 11 polychlorinated biphenyl (PCB) congeners in aqueous conc

78 th four or more chlorines along with all 209 polychlorinated biphenyl (PCB) congeners in surface wate

79 d-PAHs, 3 perdeuterated parent-PAHs, and 100 polychlorinated biphenyl (PCB) congeners or coeluting co

80 We propose that polychlorinated biphenyl (PCB) congeners represent an id

81 ees N; 17.43 degrees E) and analyzed for 209 polychlorinated biphenyl (PCB) congeners using high-reso

82 Particulate and dissolved phase polychlorinated biphenyl (PCB) congeners were analyzed u

83 Polychlorinated biphenyl (PCB) congeners with multiple o

84 pregnant women established in 1988-1989, six polychlorinated biphenyl (PCB) congeners, hexachlorobenz

85 urs when cocktails of combustion residues or polychlorinated biphenyl (PCB) containing oils become in

86 ), polycyclic aromatic hydrocarbon (PAH) and polychlorinated biphenyl (PCB) emissions.

87 Causal evidence linking toxic injury to polychlorinated biphenyl (PCB) exposure is typically con

88 The development of an area-based polychlorinated biphenyl (PCB) food-web bioaccumulation

89 tivated carbon (AC) for in situ treatment of polychlorinated biphenyl (PCB) impacted sediments.

90 While the overall atmospheric polychlorinated biphenyl (PCB) levels in many urban area

91 n to extensively dechlorinate the commercial polychlorinated biphenyl (PCB) mixture Aroclor 1260.

92 croextraction (SPME) GC/MS data objects of 7 polychlorinated biphenyl (PCB) mixture standard solution

93 logically relevant levels of Aroclor 1254, a polychlorinated biphenyl (PCB) mixture, on moult, fatten

94 tyi strain JNA detoxifies highly chlorinated polychlorinated biphenyl (PCB) mixtures via 85 distinct

95 conversion of an adsorbed precursor state of polychlorinated biphenyl (PCB) molecules on the Si(111)-

96 hlorodiphenyldichloroethylene (p,p -DDE) and polychlorinated biphenyl (PCB) pollutants.

97 ension in residents living around the former polychlorinated biphenyl (PCB) production plant in Annis

98 EFs for other SVOCs including polychlorinated biphenyl (PCB), polychlorinated naphthal

99 ies reported an association between prenatal polychlorinated biphenyl (PCB)-153 exposure and reduced

100 rmacokinetic model to estimate monthly serum polychlorinated biphenyl (PCB)-153 levels in 441 infants

101 Blood concentrations of polychlorinated biphenyl (PCB)-153; 1-dichloro-2,2-bis (

102 reeding colonies within feeding range of the polychlorinated biphenyl (PCB)-contaminated New Bedford

103 ered a significant contributing mechanism in polychlorinated biphenyl (PCB)-induced thyroid disruptio

104 l ethers 154 (HR 1.53, 95% CI 0.90 to 2.61), polychlorinated biphenyls (PCB) 118 (HR 1.50, 95% CI 0.9

105 We investigated the major sources of polychlorinated biphenyls (PCB) and interpreted the envi

106 epidemic on time trends in human exposure to polychlorinated biphenyls (PCB) at the population level

107 The health risk of inhalation exposure to polychlorinated biphenyls (PCB) cannot be assessed with

108 There is a wealth of studies of polychlorinated biphenyls (PCB) in surface water and bio

109 samples near Sauget, IL, where 373000 mt of polychlorinated biphenyls (PCB) was produced between 193

110 anes (HCHs), hexachlorobenzene (HCB), and 26 polychlorinated biphenyl (PCBs) congeners in seawater an

111 s between quartiles of concentrations of 101 polychlorinated biphenyl (PCBs) congeners, congener grou

112 The levels of polychlorinated biphenyl (PCBs), polybrominated diphenyl

113 ised of approximately 95% DDE) (plasma), sum polychlorinated biphenyls (PCBs) (plasma), and sum polyb

114 In this study, we tested 25 polychlorinated biphenyls (PCBs) [PCB 3, 11, 52, 126, 13

115 Lipophilic polychlorinated biphenyls (PCBs) accumulate with obesity

116 ion of the ACC-HUMAN model was evaluated for polychlorinated biphenyls (PCBs) and applied to cVMS in

117 s, orders of magnitude greater than those of polychlorinated biphenyls (PCBs) and decabromodiphenyl e

118 farms in Switzerland heavily contaminated by polychlorinated biphenyls (PCBs) and dioxins (PCDD/Fs),

119 lative, and toxic substances (PBTs), such as polychlorinated biphenyls (PCBs) and dioxins, from the w

120 Polychlorinated biphenyls (PCBs) and enantiomer fraction

121 We investigated the effects of polychlorinated biphenyls (PCBs) and exercise on the com

122 l ethers (PBDEs) are structurally similar to polychlorinated biphenyls (PCBs) and have both central (

123 stent, bioaccumulative and toxic pollutants (polychlorinated biphenyls (PCBs) and hexachlorobenzene (

124 valuated associations between serum PBBs and polychlorinated biphenyls (PCBs) and markers of thyroid

125 ve largely affirmed the relationship between polychlorinated biphenyls (PCBs) and non-Hodgkin lymphom

126 Polychlorinated biphenyls (PCBs) and organochlorine pest

127 , air, and zooplankton for a range of legacy polychlorinated biphenyls (PCBs) and organochlorine pest

128 Polychlorinated biphenyls (PCBs) and organochlorine pest

129 Polychlorinated biphenyls (PCBs) and organochlorine pest

130 onally, typical outdoor contaminants such as polychlorinated biphenyls (PCBs) and organochlorine pest

131 ummation operatorHg), methyl mercury (MeHg), polychlorinated biphenyls (PCBs) and other industrial or

132 Polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs) and p,p'-dichlorodiphen

133 the association between prenatal exposure to polychlorinated biphenyls (PCBs) and p,p'-dichlorodiphen

134 estigated the association between cord serum polychlorinated biphenyls (PCBs) and p,p'-dichlorodiphen

135 Concentrations of total polychlorinated biphenyls (PCBs) and polybrominated biph

136 ersistent organic pollutants (POPs), such as polychlorinated biphenyls (PCBs) and polybrominated diph

137 cted by a variety of contaminants, including polychlorinated biphenyls (PCBs) and polychlorinated dib

138 and winter 2011 and target analytes included polychlorinated biphenyls (PCBs) and polychlorinated dib

139 Polychlorinated biphenyls (PCBs) and polychlorinated dib

140 For polychlorinated biphenyls (PCBs) and polychlorinated dib

141 n San Diego Bay, CA, we measured sorption of polychlorinated biphenyls (PCBs) and polycyclic aromatic

142 del performance was evaluated using data for polychlorinated biphenyls (PCBs) and polycyclic aromatic

143 s are important regional sources of airborne polychlorinated biphenyls (PCBs) and population-scale ai

144 rategy on pollutant occurrence of lipophilic polychlorinated biphenyls (PCBs) and protein-associated

145 nthropogenic pollutants including lipophilic polychlorinated biphenyls (PCBs) and protein-associated

146 Polychlorinated biphenyls (PCBs) and some pesticides wer

147 Analyzed OHCs were polychlorinated biphenyls (PCBs) and their hydroxylated

148 Changes in atropisomer composition of chiral polychlorinated biphenyls (PCBs) and their mono- and dih

149 Polychlorinated biphenyls (PCBs) are a group of 209 pers

150 Polychlorinated biphenyls (PCBs) are environmental toxic

151 Polychlorinated biphenyls (PCBs) are known human carcino

152 Coplanar and noncoplanar polychlorinated biphenyls (PCBs) are known to have diffe

153 Polychlorinated biphenyls (PCBs) are persistent hazardou

154 Polychlorinated biphenyls (PCBs) are persistent organic

155 Organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs) are reported in 97 air

156 Polychlorinated biphenyls (PCBs) are toxic, persistent,

157 Polychlorinated biphenyls (PCBs) are toxic, persistent,

158 Non-dioxin-like (NDL) polychlorinated biphenyls (PCBs) are widespread environm

159 Polychlorinated biphenyls (PCBs) are widespread, persist

160 icular, we recommend chlorpyrifos, lead, and polychlorinated biphenyls (PCBs) be systematically revie

161 The release of polychlorinated biphenyls (PCBs) by a military radar sta

162 a tool for predicting the bioaccumulation of polychlorinated biphenyls (PCBs) by pelagic and mobile f

163 a bottleneck in the bacterial degradation of polychlorinated biphenyls (PCBs) by the Bph catabolic pa

164 ration, sediment organic carbon content, and polychlorinated biphenyls (PCBs) concentrations in musse

165 Polychlorinated biphenyls (PCBs) continue to be contamin

166 Both mercury (Hg) and polychlorinated biphenyls (PCBs) demonstrate food web bi

167 Chiral polychlorinated biphenyls (PCBs) display variable atropi

168 Non-dioxin-like (NDL) polychlorinated biphenyls (PCBs) enhance the activity of

169 At the contaminated sites, polychlorinated biphenyls (PCBs) frequently coexist with

170 a highly time-resolved historical record of polychlorinated biphenyls (PCBs) from an Alpine ice core

171 partition coefficients at 37 degrees C of 18 polychlorinated biphenyls (PCBs) from water into (i) tri

172 Polychlorinated biphenyls (PCBs) had both agonistic and

173 Exposure to chiral polychlorinated biphenyls (PCBs) has been associated wit

174 While microbial dechlorination of polychlorinated biphenyls (PCBs) has been observed in se

175 In previous studies, the incorporation of polychlorinated biphenyls (PCBs) has been quantified in

176 Organochlorine (OC) insecticides and polychlorinated biphenyls (PCBs) have been shown to have

177 rine (OC) pesticides and the more persistent polychlorinated biphenyls (PCBs) have well-established d

178 d to investigate the spatial distribution of polychlorinated biphenyls (PCBs) in air.

179 cial meat starter cultures on degradation of polychlorinated biphenyls (PCBs) in dry fermented sausag

180 nd robust method for the determination of 18 polychlorinated biphenyls (PCBs) in fish was developed a

181 mental exposures that affect accumulation of polychlorinated biphenyls (PCBs) in humans are complex a

182 pounds were applied independently to measure polychlorinated biphenyls (PCBs) in mesocosms with (1) N

183 The remediation of polychlorinated biphenyls (PCBs) in soils and sediments

184 Indoor air concentrations of polychlorinated biphenyls (PCBs) in some buildings are o

185 s show that there is a close coupling of the polychlorinated biphenyls (PCBs) in the atmosphere and s

186 Concentrations of polychlorinated biphenyls (PCBs) in the Delaware River c

187 From the concentrations of polychlorinated biphenyls (PCBs) in the PDMS, we assesse

188 g medium, we measured the uptake kinetics of polychlorinated biphenyls (PCBs) in XAD and of water in

189 Ambient air concentrations of polychlorinated biphenyls (PCBs) in Zurich, Switzerland,

190 Polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) interact with the thyro

191 l describing deposition and incorporation of polychlorinated biphenyls (PCBs) into an Alpine glacier

192 Plants metabolize polychlorinated biphenyls (PCBs) into hydroxylated deriv

193 ical fate model quantifying incorporation of polychlorinated biphenyls (PCBs) into the Silvretta glac

194 Degradation of polychlorinated biphenyls (PCBs) is initiated by cytochr

195 The oxidative degradation of biphenyl and polychlorinated biphenyls (PCBs) is initiated in Pandora

196 on of sediments contaminated with commercial polychlorinated biphenyls (PCBs) is potentially achievab

197 itu passive sampling of strongly hydrophobic polychlorinated biphenyls (PCBs) is still challenged by

198 Although inhalation of atmospheric polychlorinated biphenyls (PCBs) is the most universal e

199 Polychlorinated biphenyls (PCBs) manufactured in Annisto

200 ntal and human data suggest that exposure to polychlorinated biphenyls (PCBs) may induce ototoxicity,

201 llutants (POPs) such as dioxins, furans, and polychlorinated biphenyls (PCBs) may influence leukocyte

202 terized the variability in concentrations of polychlorinated biphenyls (PCBs) measured in residential

203 er was calibrated by measuring the uptake of polychlorinated biphenyls (PCBs) over 8 weeks in an indo

204 omatic hydrocarbons (PAHs), heavy metals and polychlorinated biphenyls (PCBs) over the past decade is

205 We investigated whether polychlorinated biphenyls (PCBs) partitioning between th

206 Polychlorinated biphenyls (PCBs) pose significant risk t

207 Coplanar polychlorinated biphenyls (PCBs) promote adipocyte infla

208 Non-dioxin-like (NDL) polychlorinated biphenyls (PCBs) promote dendritic growt

209 Previous studies demonstrated that coplanar polychlorinated biphenyls (PCBs) promote proinflammatory

210 Polychlorinated biphenyls (PCBs) remain chemicals of con

211 polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs) tend to accumulate in s

212 ke Michigan Mass Balance Project (LMMBP) for polychlorinated biphenyls (PCBs) that was conducted in 1

213 d water (KDOC) for three cVMS, and for three polychlorinated biphenyls (PCBs) that were used as refer

214 polycyclic aromatic hydrocarbons (PAHs), and polychlorinated biphenyls (PCBs) using gas chromatograph

215 The synthesis of 12 (37)Cl-labeled polychlorinated biphenyls (PCBs) was carried out by the

216 nt desorption of hexachlorobenzene (HCB) and polychlorinated biphenyls (PCBs) was studied for the alg

217 on density, but mercury, chlorobenzenes, and polychlorinated biphenyls (PCBs) were explained better b

218 lybrominated diphenyl ethers (PBDEs), and 36 polychlorinated biphenyls (PCBs) were measured before co

219 The transfer kinetics of 14 polychlorinated biphenyls (PCBs) were measured in gut fl

220 Polychlorinated biphenyls (PCBs) were used as toxicant,

221 Polychlorinated biphenyls (PCBs) with less chlorine atom

222 the toxicities of environmentally persistent polychlorinated biphenyls (PCBs) with lower numbers of c

223 (2,4,6-TBP), OH-PBDEs) and organochlorines (polychlorinated biphenyls (PCBs), 1,1-bis(4,4'-dichlorod

224 chlorinated dibenzodioxins/dibenzofurans, 18 polychlorinated biphenyls (PCBs), 3 hexabromocyclododeca

225 of 8 phthalate metabolites, bisphenol A, 25 polychlorinated biphenyls (PCBs), 6 organochlorine pesti

226 index was a sum of weighted quartiles for 5 polychlorinated biphenyls (PCBs), 7 polycyclic aromatic

227 hanisms underpinning the biomagnification of polychlorinated biphenyls (PCBs), a globally prevalent g

228 henyl, 10 polybrominated diphenyl ethers, 36 polychlorinated biphenyls (PCBs), and 7 perfluorochemica

229 including organochlorine pesticides (OCPs), polychlorinated biphenyls (PCBs), and brominated flame r

230 orinated dibenzo-p-dioxins (PCDDs)], furans, polychlorinated biphenyls (PCBs), and corresponding toxi

231 lor, dichlorodiphenyldichloroethylene (DDE), polychlorinated biphenyls (PCBs), and dioxins and dioxin

232 as been reported to respire on the notorious polychlorinated biphenyls (PCBs), and functional genes r

233 benzo-p-dioxins and dibenzofurans (PCDD/Fs), polychlorinated biphenyls (PCBs), and hexachlorobenzene

234 -2,2-bis(p-chlorophenyl)ethylene (p,p -DDE), polychlorinated biphenyls (PCBs), and hexachlorobenzene

235 ted polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pes

236 Polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), and persistent pestici

237 ing polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and polychlorinated di

238 hlorodiphenyldicholorethylene (p,p -DDE) and polychlorinated biphenyls (PCBs), and sperm aneuploidy i

239 polybrominated diphenyl ethers (PBDEs), two polychlorinated biphenyls (PCBs), and two organochlorine

240 Polychlorinated biphenyls (PCBs), banned in the United S

241 as dichlorodiphenyltrichloroethane (DDT) and polychlorinated biphenyls (PCBs), but has not been well

242 These included polychlorinated biphenyls (PCBs), current-use pesticides

243 Plasma polychlorinated biphenyls (PCBs), dichlorodiphenyltrichl

244 Dioxins, furans, and polychlorinated biphenyls (PCBs), dioxin-like and non-di

245 esent in nonpolar sediment extracts, such as polychlorinated biphenyls (PCBs), dioxins, furans (PCDD/

246 ersistent Organic Pollutants (POPs), such as polychlorinated biphenyls (PCBs), have been reported in

247 istent organic pollutants, particularly with polychlorinated biphenyls (PCBs), have happen in food an

248 tlantic tomcod from the Hudson River (HR) to polychlorinated biphenyls (PCBs), is unknown.

249 ted that co-exposure to another contaminant, polychlorinated biphenyls (PCBs), may be responsible for

250 Several ubiquitous pollutants (polychlorinated biphenyls (PCBs), organochlorine pestici

251 of polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), organochlorine pestici

252 in San Francisco during 2010-2011, including polychlorinated biphenyls (PCBs), organochlorine pestici

253 e of polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), organochlorine pestici

254 Polychlorinated biphenyls (PCBs), organochlorine pestici

255 be shown that these contaminants, as well as polychlorinated biphenyls (PCBs), organochlorine pestici

256 pesticides, polybrominated diphenyl ethers, polychlorinated biphenyls (PCBs), per- and polyfluoroalk

257 o determine concentrations of mercury, lead, polychlorinated biphenyls (PCBs), pesticides, brominated

258 ceeding the corresponding flows reported for polychlorinated biphenyls (PCBs), polybrominated dipheny

259 were analyzed for legacy and emerging POPs (polychlorinated biphenyls (PCBs), polybrominated dipheny

260 The contaminants were polychlorinated biphenyls (PCBs), polybrominated dipheny

261 trace level (low- to subppb) GC-MS data for polychlorinated biphenyls (PCBs), polybrominated dipheny

262 results suggested that air concentrations of polychlorinated biphenyls (PCBs), polybrominated dipheny

263 oth ecotypes with significantly higher total polychlorinated biphenyls (PCBs), polybrominated dipheny

264 ing polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), polybrominated dipheny

265 ding polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), polychlorinated dibenz

266 ike polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), polychlorinated naphth

267 tes, polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), polycyclic aromatic hy

268 r partition coefficients were determined for polychlorinated biphenyls (PCBs), polycyclic aromatic hy

269 of surface sediment concentrations of seven polychlorinated biphenyls (PCBs), seven polycyclic aroma

270 transcripts were positively correlated with polychlorinated biphenyls (PCBs), the dominant POP in be

271 nd bodyweight, as well as the transfer of 19 polychlorinated biphenyls (PCBs), were assessed in bioas

272 ecially organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs), which are biomagnified

273 Serum concentrations of polychlorinated biphenyls (PCBs), which are chemicals wi

274 which have been homogenized and spiked with polychlorinated biphenyls (PCBs), with silicone films of

275 ity of hydrophobic organic chemicals such as polychlorinated biphenyls (PCBs).

276 polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs).

277 and Ship Canal, which volatilizes ~7.5 kg/yr polychlorinated biphenyls (PCBs).

278 ction and magnitude of air-water exchange of polychlorinated biphenyls (PCBs).

279 agreement and confirmed previous results for polychlorinated biphenyls (PCBs).

280 dietary assimilation and fecal depuration of polychlorinated biphenyls (PCBs).

281 zes the dihydroxylation of biphenyl and many polychlorinated biphenyls (PCBs).

282 ted to be effective for in situ treatment of polychlorinated biphenyls (PCBs).

283 ponse to Aroclor 1254 (A-1254), a mixture of polychlorinated biphenyls (PCBs).

284 city of environmentally relevant mixtures of polychlorinated biphenyls (PCBs).

285 ure models are used to study the toxicity of polychlorinated biphenyls (PCBs); however, it is typical

286 Polychlorinated-biphenyls (PCBs) were introduced in the

287 precursors in the arctic environment (e.g., polychlorinated biphenyls [PCBs]).

288 OPs (polybrominated diphenyl ethers [PBDEs], polychlorinated biphenyls [PCBs], and organochlorine pes

289 h Atlantic near the surface (e.g., sum of 14 polychlorinated biphenyls, PCBs: 0.84 pg L(-1)) were sim

290 ted naphthalenes, organochlorine pesticides, polychlorinated biphenyls, polybrominated diphenyl ether

291 Here, we investigate transfer pathways of polychlorinated biphenyls, polybrominated diphenyl ether

292 rganic pollutants: polychlorinated benzenes, polychlorinated biphenyls, polychlorinated dibenzodioxin

293 rinated dibenzo-p-dioxins and dibenzofurans, polychlorinated biphenyls, polychlorinated diphenyl ethe

294 perature dependence of Henry's constants for polychlorinated biphenyls, polychlorinated naphthalenes,

295 dy sediments contaminated with petroleum and polychlorinated biphenyls, respectively, and variations

296 Legacy polychlorinated biphenyls ( summation operator18PCBs) an

297 Polycyclic aromatic hydrocarbons and polychlorinated biphenyls were also detected.

298 re similar to TEFs for birds, while RePs for polychlorinated biphenyls were most similar to TEFs for

299 , manufactured organic contaminants (such as polychlorinated biphenyls) were retained and concentrate

300 ycyclic aromatic hydrocarbons and 93-97% for polychlorinated biphenyls with 5 and 4 wt % AC dose, res