ライフサイエンスコーパス: polychlorinated

1 nnows onto the separated analyte signal of a polychlorinated alkanes (chlorinated paraffins) technica

2 The polychlorinated aromatic antimicrobials triclosan and tr

3 The photodegradation of chlorothalonil, a polychlorinated aromatic fungicide widely used in agricu

4 x families of persistent organic pollutants: polychlorinated benzenes, polychlorinated biphenyls, pol

5 ry actions in the U.S. concerning persistent polychlorinated biocides, showing a potential path forwa

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

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

8 Polychlorinated biphenyl (PCB) and polybrominated diphen

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

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

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

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

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

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

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

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

17 Polychlorinated biphenyl (PCB) congeners with multiple o

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

40 Polychlorinated biphenyl and organochlorine pesticide co

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

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

43 Polychlorinated biphenyl concentrations are decreasing i

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

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

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

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

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

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

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

51 Legacy polychlorinated biphenyls ( summation operator18PCBs) an

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

69 Lipophilic polychlorinated biphenyls (PCBs) accumulate with obesity

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

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

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

73 Polychlorinated biphenyls (PCBs) and enantiomer fraction

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

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

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

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

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

79 Polychlorinated biphenyls (PCBs) and organochlorine pest

80 Polychlorinated biphenyls (PCBs) and organochlorine pest

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

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

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

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

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

86 For polychlorinated biphenyls (PCBs) and polychlorinated dib

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

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

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

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

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

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

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

94 Polychlorinated biphenyls (PCBs) and some pesticides wer

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

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

97 Polychlorinated biphenyls (PCBs) are environmental toxic

98 Polychlorinated biphenyls (PCBs) are known human carcino

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

100 Polychlorinated biphenyls (PCBs) are persistent hazardou

101 Polychlorinated biphenyls (PCBs) are toxic, persistent,

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

103 Polychlorinated biphenyls (PCBs) are widespread, persist

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

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

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

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

108 Polychlorinated biphenyls (PCBs) continue to be contamin

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

110 Chiral polychlorinated biphenyls (PCBs) display variable atropi

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

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

113 Polychlorinated biphenyls (PCBs) had both agonistic and

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

130 Plants metabolize polychlorinated biphenyls (PCBs) into hydroxylated deriv

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

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

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

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

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

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

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

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

139 Polychlorinated biphenyls (PCBs) pose significant risk t

140 Coplanar polychlorinated biphenyls (PCBs) promote adipocyte infla

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

142 Polychlorinated biphenyls (PCBs) remain chemicals of con

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

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

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

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

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

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

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

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

151 Polychlorinated biphenyls (PCBs) with less chlorine atom

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

153 (2,4,6-TBP), OH-PBDEs) and organochlorines (polychlorinated biphenyls (PCBs), 1,1-bis(4,4'-dichlorod

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

179 Polychlorinated biphenyls (PCBs), organochlorine pestici

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

208 Polychlorinated biphenyls are among the most well-studie

209 Although polychlorinated biphenyls are no longer sold as commerci

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

227 We measured polychlorinated biphenyls, organochlorine pesticides, po

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

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

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

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

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

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

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

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

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

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

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

239 studied via the reductive dechlorination of polychlorinated biphenyls.

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

241 Polychlorinated-biphenyls (PCBs) were introduced in the

242 including diethylhexyl phthalate (DEHP) and polychlorinated bisphenol 153 (PCB153), were detected in

243 olumn is utilized, as is common practice for polychlorinated dibenzo-p-dioxin (dioxin) and related co

244 In this paper, a new data set of polychlorinated dibenzo-p-dioxin and dibenzofuran (PCDD/

245 The discrepancies between polychlorinated dibenzo-p-dioxin to polychlorinated dibe

246 Polychlorinated dibenzo-p-dioxins (PCDD) and dibenzofura

247 ease of contaminants, including highly toxic polychlorinated dibenzo-p-dioxins (PCDD) and dibenzofura

248 network has been established to investigate polychlorinated dibenzo-p-dioxins (PCDDs) and polychlori

249 CO2), volatile organic compounds (VOCs), and polychlorinated dibenzo-p-dioxins (PCDDs) and polychlori

250 Polychlorinated dibenzo-p-dioxins (PCDDs) are a class of

251 Although polychlorinated dibenzo-p-dioxins (PCDDs) quantified in

252 Polychlorinated dibenzo-p-dioxins (PCDDs), as a class of

253 altic wild salmon and compared with those of polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans

254 The levels of polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinat

255 Our research reports polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinat

256 For polychlorinated biphenyls (PCBs) and polychlorinated dibenzo-p-dioxins (PCDDs), solubility-de

257 [2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), polychlorinated dibenzo-p-dioxins (PCDDs)], furans, poly

258 Polychlorinated dibenzo-p-dioxins and -furans (PCDD/Fs)

259 cluding polychlorinated biphenyls (PCBs) and polychlorinated dibenzo-p-dioxins and -furans (PCDD/Fs).

260 ed biphenyls ( summation operator18PCBs) and polychlorinated dibenzo-p-dioxins and dibenzofurans ( su

261 Concentrations of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

262 The pollution trend of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

263 Spatial and temporal trends of sources of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

264 ncluded polychlorinated biphenyls (PCBs) and polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

265 ckground occurrence of gas and aerosol phase polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

266 chlorophenols are known to be precursors of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

267 including polycyclic aromatic hydrocarbons, polychlorinated dibenzo-p-dioxins and dibenzofurans, pol

268 Polychlorinated dibenzo-p-dioxins and furans (PCDD/Fs) a

269 s (PBDEs), polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins and furans (PCDD/Fs),

270 at frequently lead to catalytic formation of polychlorinated dibenzo-p-dioxins and polychlorinated di

271 e conditions and the subsequent formation of polychlorinated dibenzo-p-dioxins, polychlorinated diben

272 with chlorine) react photochemically to form polychlorinated dibenzo-p-dioxins.

273 lations of PM10 with SO2, NOx, heavy metals, polychlorinated dibenzo-p-dioxins/furan (PCDD/F), polycy

274 PAHs), polychlorinated biphenyls (PCBs), and polychlorinated dibenzo-p-dioxins/furans (PCDD/Fs) to re

275 rinated benzenes, polychlorinated biphenyls, polychlorinated dibenzodioxins, polychlorinated dibenzof

276 Environmental contaminants (17 polychlorinated dibenzodioxins/dibenzofurans, 18 polychl

277 safe with respect to their potential to form polychlorinated dibenzodioxins/furans (PCDD/Fs).

278 between polychlorinated dibenzo-p-dioxin to polychlorinated dibenzofuran (PCDD to PCDF) ratios in la

279 mation of polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans (PCDD/F, dioxins), and the

280 ion of polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans (PCDD/Fs) from their precu

281 f polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) and dioxin-like po

282 olychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) at Global Atmosphe

283 olychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) were sampled using

284 s polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), and coplanar poly

285 ncluded polychlorinated naphthalenes (PCNs), polychlorinated dibenzofurans (PCDFs), chlorinated and m

286 Both AhRs of white sturgeon had RePs for polychlorinated dibenzofurans more similar to TEFs for b

287 d biphenyls, polychlorinated dibenzodioxins, polychlorinated dibenzofurans, polychlorinated naphthale

288 nd dibenzofurans, polychlorinated biphenyls, polychlorinated diphenyl ethers, polybrominated dibenzo-

289 are produced and used as complex mixtures of polychlorinated n-alkanes containing thousands of isomer

290 Cs including polychlorinated biphenyl (PCB), polychlorinated naphthalene (PCN), and polybrominated di

291 There are relatively few studies of polychlorinated naphthalenes (PCNs) for biota in polar r

292 ns (PAHs), polychlorinated biphenyls (PCBs), polychlorinated naphthalenes (PCNs), and polybrominated

293 ntaminants varied among species and included polychlorinated naphthalenes (PCNs), polychlorinated dib

294 y's constants for polychlorinated biphenyls, polychlorinated naphthalenes, and polybrominated dipheny

295 benzodioxins, polychlorinated dibenzofurans, polychlorinated naphthalenes, and polybrominated dipheny

296 The 59 target analytes included toxaphenes, polychlorinated naphthalenes, organochlorine pesticides,

297 pplications in streamlining the synthesis of polychlorinated natural products such as the chlorosulfo

298 d semiquinone radicals in CL generation from polychlorinated phenols and Fenton system.

299 radioactive (106)Ru contaminant exists in a polychlorinated Ru(III) form, partly or entirely as beta

300 was successfully applied to a thermally aged polychlorinated tridecane formulation (Cl5-Cl9).