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

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

2 studied via the reductive dechlorination of polychlorinated biphenyls.

3 lychlorinated biphenyls and iron-dextran and polychlorinated biphenyls.

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

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

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

7 Polychlorinated biphenyl and organochlorine pesticide co

8 the entire cohort (n = 194) was analyzed for polychlorinated biphenyls and 1,1'-dichloro-2,2'-bis(4-c

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

10 Although environmental levels of polychlorinated biphenyls and certain organochlorine pes

11 Pollutants such as polychlorinated biphenyls and dioxins pose a serious thr

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

13 ions of the homozygous Hfe-null mutation and polychlorinated biphenyls and iron-dextran and polychlor

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

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

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

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

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

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

20 ed with iron, delta-aminolevulinic acid, and polychlorinated biphenyls; and mice with one null allele

21 Polychlorinated biphenyls are among the most well-studie

22 Although polychlorinated biphenyls are no longer sold as commerci

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

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

25 nans can use chlorinated aromatics including polychlorinated biphenyls as electron acceptors in a pro

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

27 ollutants such as chlorinated aliphatics and polychlorinated biphenyls as well as for binding heavy m

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

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

30 methanol solutions, and a series of 21 PCB (polychlorinated biphenyl) compounds were used to demonst

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

32 Polychlorinated biphenyl concentrations are decreasing i

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

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

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

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

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

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

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

40 ans LB400 (LB400), a well studied, effective polychlorinated biphenyl-degrader, has one of the two la

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

42 Exposures to polychlorinated biphenyls, dichlorodiphenyl trichloroeth

43 models suggest that early-life exposures to polychlorinated biphenyls, dichlorodiphenyl trichloroeth

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

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

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

47 administration alone or in combination with polychlorinated biphenyl exposure was porphyrinogenic in

48 and their influence, alone and combined with polychlorinated-biphenyl exposure.

49 rt modest associations of primarily prenatal polychlorinated biphenyl exposures with differences in n

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

51 exposures to organophosphate pesticides and polychlorinated biphenyls have been associated with abno

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

53 Levels of dioxins and polychlorinated biphenyls in fish are low, and potential

54 adults, and (4) health risks of dioxins and polychlorinated biphenyls in fish.

55 ncentrations of mercury in cord blood and of polychlorinated biphenyls in maternal milk were measured

56 he measurement of chlorinated pesticides and polychlorinated biphenyls in specimens obtained from hum

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

58 An example using polychlorinated biphenyl levels to classify women with a

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

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

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

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

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

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

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

66 ects of indoor pesticide use and exposure to polychlorinated biphenyls on pregnancy outcome and child

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

68 No adverse associations were found with polychlorinated biphenyl or 1,1'-dichloro-2,2'-bis(4-chl

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

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

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

72 ioremediation of man-made pollutants such as polychlorinated biphenyl (PCB) and dichlorodiphenyltrich

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

74 Polychlorinated biphenyl (PCB) and polybrominated diphen

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

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

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

78 the mean and SD in a data set ( N = 113) of polychlorinated biphenyl (PCB) concentrations using mult

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

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

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

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

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

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

85 rison study of the determination of selected polychlorinated biphenyl (PCB) congeners in shellfish ti

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

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

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

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

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

91 Polychlorinated biphenyl (PCB) congeners with multiple o

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

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

94 The history of anaerobic microbial polychlorinated biphenyl (PCB) dechlorination is traced

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

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

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

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

99 e measurements of several pairs of coeluting polychlorinated biphenyl (PCB) isomers in standard solut

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

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

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

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

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

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

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

107 The reactions of glutathione (GSH) with polychlorinated biphenyl (PCB) quinones having different

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

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

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

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

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

113 that Burkholderia xenovorans LB400, a potent polychlorinated biphenyl (PCB)-degrading bacterium, util

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

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

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

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

118 Polychlorinated biphenyls (PCB) have been suspected as p

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

120 ce suggests that increased concentrations of polychlorinated biphenyls (PCB) measured in blood or fat

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

122 e to endocrine-disrupting chemicals, such as polychlorinated biphenyls (PCB), may alter hormonal bala

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

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

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

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

127 e relation between environmental exposure to polychlorinated biphenyls (PCBs) and breast cancer risk.

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

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

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

131 Polychlorinated biphenyls (PCBs) and enantiomer fraction

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

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

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

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

136 exposure to electromagnetic fields (EMFs) or polychlorinated biphenyls (PCBs) and mortality from pros

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

138 Polychlorinated biphenyls (PCBs) and organochlorine pest

139 Polychlorinated biphenyls (PCBs) and organochlorine pest

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

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

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

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

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

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

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

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

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

149 Polychlorinated biphenyls (PCBs) and polychlorinated dib

150 For polychlorinated biphenyls (PCBs) and polychlorinated dib

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

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

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

154 Polychlorinated biphenyls (PCBs) and some pesticides wer

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

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

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

158 Polychlorinated biphenyls (PCBs) are associated with a b

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

160 Polychlorinated biphenyls (PCBs) are one of the most ubi

161 Polychlorinated biphenyls (PCBs) are persistent hazardou

162 Polychlorinated biphenyls (PCBs) are persistent organic

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

164 Polychlorinated biphenyls (PCBs) are toxic, persistent,

165 Polychlorinated biphenyls (PCBs) are ubiquitous environm

166 Noncoplanar polychlorinated biphenyls (PCBs) are widely dispersed in

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

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

169 The microbial degradation of polychlorinated biphenyls (PCBs) by the biphenyl catabol

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

171 Polychlorinated biphenyls (PCBs) comprise a group of per

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

173 Polychlorinated biphenyls (PCBs) continue to be contamin

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

175 Chiral polychlorinated biphenyls (PCBs) display variable atropi

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

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

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

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

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

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

182 Studies into bioaccumulation of polychlorinated biphenyls (PCBs) have increasingly focus

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

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

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

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

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

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

189 Determining dissolved concentrations of polychlorinated biphenyls (PCBs) in sediment pore (inter

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

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

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

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

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

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

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

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

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

199 Plants metabolize polychlorinated biphenyls (PCBs) into hydroxylated deriv

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

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

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

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

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

205 Polychlorinated biphenyls (PCBs) manufactured in Annisto

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

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

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

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

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

211 Coplanar polychlorinated biphenyls (PCBs) promote adipocyte infla

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

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

214 Polychlorinated biphenyls (PCBs) remain chemicals of con

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

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

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

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

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

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

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

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

223 Polychlorinated biphenyls (PCBs) were used as toxicant,

224 Polychlorinated biphenyls (PCBs) with less chlorine atom

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

226 (2,4,6-TBP), OH-PBDEs) and organochlorines (polychlorinated biphenyls (PCBs), 1,1-bis(4,4'-dichlorod

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

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

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

230 e relation between exposure to low levels of polychlorinated biphenyls (PCBs), a class of persistent

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

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

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

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

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

236 -2,2-bis(p-chlorophenyl)ethylene (p,p -DDE), polychlorinated biphenyls (PCBs), and hexachlorobenzene

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

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

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

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

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

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

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

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

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

246 Plasma polychlorinated biphenyls (PCBs), dichlorodiphenyltrichl

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

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

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

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

251 to determine whether serum concentrations of polychlorinated biphenyls (PCBs), hexachlorobenzene, p,p

252 A method for the determination of 146 polychlorinated biphenyls (PCBs), including four non-ort

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

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

255 Polychlorinated biphenyls (PCBs), once used widely in tr

256 Polychlorinated biphenyls (PCBs), organochlorine pestici

257 for the simultaneous measurement of selected polychlorinated biphenyls (PCBs), organochlorine pestici

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

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

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

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

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

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

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

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

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

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

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

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

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

271 The metabolites of polychlorinated biphenyls (PCBs), such as hydroxylated P

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

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

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

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 non-ortho- and eight mono-ortho-substituted polychlorinated biphenyls (PCBs).

283 nic halogenated organic compounds, including polychlorinated biphenyls (PCBs).

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

285 Polychlorinated-biphenyls (PCBs) were introduced in the

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

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

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

289 Biologically significant levels of polychlorinated biphenyls, polybrominated diphenyl ether

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

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

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

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

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

295 Legacy polychlorinated biphenyls ( summation operator18PCBs) an

296 Polycyclic aromatic hydrocarbons and polychlorinated biphenyls were also detected.

297 Polychlorinated biphenyls were also porphyrinogenic in t

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