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 VOCs), particulate matter (PM(10), PM(2.5)), polychlorinated and polybrominated dioxins/furans (PCDD/

3 The polychlorinated aromatic antimicrobials triclosan and tr

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

5 including polycyclic aromatic hydrocarbons, polychlorinated benzenes and biphenyls, and substituted

6 e of the catalyst includes dehalogenation of polychlorinated benzenes, bromobenzene, iodobenzene, and

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

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

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

10 Polychlorinated biphenyl (PCB) and polybrominated diphen

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

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

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

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

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

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

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

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

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

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

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

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

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

24 Polychlorinated biphenyl (PCB) congeners with multiple o

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

47 Polychlorinated biphenyl and organochlorine pesticide co

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

49 Polychlorinated biphenyl concentrations are decreasing i

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

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

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

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

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

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

56 Legacy polychlorinated biphenyls ( summation operator18PCBs) an

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

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

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

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

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

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

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

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

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

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

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

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

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

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

74 Polychlorinated biphenyls (PCBs) and enantiomer fraction

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

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

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

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

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

80 Polychlorinated biphenyls (PCBs) and organochlorine pest

81 Polychlorinated biphenyls (PCBs) and organochlorine pest

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

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

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

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

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

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

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

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

90 Polychlorinated biphenyls (PCBs) and polychlorinated dib

91 For polychlorinated biphenyls (PCBs) and polychlorinated dib

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

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

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

95 Polychlorinated biphenyls (PCBs) and some pesticides wer

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

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

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

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

100 Polychlorinated biphenyls (PCBs) are persistent hazardou

101 Polychlorinated biphenyls (PCBs) are persistent organic

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

103 Polychlorinated biphenyls (PCBs) are toxic, persistent,

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

131 Plants metabolize polychlorinated biphenyls (PCBs) into hydroxylated deriv

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

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

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

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

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

137 Polychlorinated biphenyls (PCBs) manufactured in Annisto

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

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

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

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

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

143 Coplanar polychlorinated biphenyls (PCBs) promote adipocyte infla

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

145 Polychlorinated biphenyls (PCBs) remain chemicals of con

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

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

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

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

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

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

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

153 Polychlorinated biphenyls (PCBs) with less chlorine atom

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

155 (2,4,6-TBP), OH-PBDEs) and organochlorines (polychlorinated biphenyls (PCBs), 1,1-bis(4,4'-dichlorod

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

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

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

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

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

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

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

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

164 -2,2-bis(p-chlorophenyl)ethylene (p,p -DDE), polychlorinated biphenyls (PCBs), and hexachlorobenzene

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

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

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

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

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

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

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

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

173 Plasma polychlorinated biphenyls (PCBs), dichlorodiphenyltrichl

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

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

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

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

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

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

180 Polychlorinated biphenyls (PCBs), organochlorine pestici

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

205 Polychlorinated biphenyls are among the most well-studie

206 Although polychlorinated biphenyls are no longer sold as commerci

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

231 studied via the reductive dechlorination of polychlorinated biphenyls.

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

233 Polychlorinated-biphenyls (PCBs) were introduced in the

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

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

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

237 mendments to reduce the availability of aged polychlorinated dibenzo-p-dioxin/dibenzofurans (PCDD/Fs)

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

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

240 FA) and for the formation and destruction of polychlorinated dibenzo-p-dioxins (PCDD) and polychlorin

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

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

243 Emissions including polychlorinated dibenzo-p-dioxins (PCDDs) and polychlori

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

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

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

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

248 [2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), polychlorinated dibenzo-p-dioxins (PCDDs)], furans, poly

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

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

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

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

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

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

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

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

257 cluding persistent organic pollutants, i.e., polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

258 Polychlorinated biphenyls (PCBs) and polychlorinated dibenzo-p-dioxins and dibenzofurans (PCD

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

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

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

262 volved in the gas-phase synthesis of PCDD/F (polychlorinated dibenzo-p-dioxins and polychlorinated di

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

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

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

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

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

268 polycyclic aromatic hydrocarbons (PAHs) and polychlorinated-dibenzo-p-dioxins and dibenzofurans (PCD

269 tu thin-layer capping was carried out in the polychlorinated dibenzodioxin and dibenzofuran (PCDD/F)

270 ds (VOCs), polyaromatic hydrocarbons (PAHs), polychlorinated dibenzodioxins and -furans (PCDDs/PCDFs)

271 rinated benzenes, polychlorinated biphenyls, polychlorinated dibenzodioxins, polychlorinated dibenzof

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

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

274 de filter and report effects on emissions of polychlorinated dibenzodioxins/furans (PCDD/Fs).

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

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

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

278 polychlorinated dibenzo-p-dioxins (PCDD) and polychlorinated dibenzofurans (PCDF), abbreviated PCDD/F

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

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

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

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

283 olychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs), polyaromatic hydr

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

285 CDD/F (polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans, also known as dioxins).

286 d biphenyls, polychlorinated dibenzodioxins, polychlorinated dibenzofurans, polychlorinated naphthale

287 phase formation of two groups of pollutants, polychlorinated dibenzothiophenes (PCDT) and polychlorin

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 benzodioxins, polychlorinated dibenzofurans, polychlorinated naphthalenes, and polybrominated dipheny

295 y's constants for polychlorinated biphenyls, 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 polychlorinated dibenzothiophenes (PCDT) and polychlorinated thianthrenes (PCTA) from their 2-chlorot

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