ライフサイエンスコーパス: diphenyl ether

1 tive to triclosan, a synthetic antimicrobial diphenyl ether.

2 ned with 1,8-octanediol) when polymerized in diphenyl ether.

3 tes a suitable alternative to decabrominated diphenyl ether.

4 e a replacement of the banned polybrominated diphenyl ethers.

5 polybrominated biphenyls and polybrominated diphenyl ethers.

6 tetrachloroethylene, and the polybrominated diphenyl ethers.

7 chlorinated naphthalenes, and polybrominated diphenyl ethers.

8 henyls, organophosphates, and polybrominated diphenyl ethers.

9 VOCs such as diphenyl ether, 1,3,5-trioxane, 5-methyl tridecane, 2-et

10 ntellectual disability due to polybrominated diphenyl ethers (11 million IQ points lost and 43 000 ca

11 Except for brominated diphenyl ether 153, a higher serum PBDE level was relate

12 contribution to the ERS were polybrominated diphenyl ethers 154 (HR 1.53, 95% CI 0.90 to 2.61), poly

13 i(biphenyl)-2,2'-bipyridine (15) and 4,4'-di(diphenyl ether)-2,2'-bipyridine (16), and the 1,10-phena

14 se in serum concentrations of polybrominated diphenyl ether-28 (PBDE-28) (beta = 2.5; 95% CI: -0.6, 5

15 1 polybrominated biphenyl, 10 polybrominated diphenyl ethers, 36 polychlorinated biphenyls (PCBs), an

16 t the brominated flame retardant, brominated diphenyl ether 47 (BDE 47).

17 6-3.27; P = .001), and 1 BFR (polybrominated diphenyl ether 47: OR = 2.69; 95% CI, 1.49-4.85; P = .00

18 e major metabolites of TCS and to brominated diphenyl ether-47.

19 Subsequent thermolysis of imidazoles 14 in diphenyl ether affords 2-phenyl-3H-imidazo[4,5-b]quinoli

20 ad low activities towards chloroacetanilide, diphenyl ether and aryloxphenoxypropionate herbicides.

21 Tri-decabrominated diphenyl ethers and 21 other flame retardants were deter

22 Lactational exposure to polybrominated diphenyl ethers and its relation to early childhood anth

23 th transformation products of polybrominated diphenyl ethers and naturally occurring compounds, under

24 M10 generate several congeners of brominated diphenyl ethers and their OH/OCHCH2 substituents, which

25 the inhibition of InhA by 14 triazole-based diphenyl ethers and use a combination of enzyme kinetics

26 oral changes in legacy (e.g., polybrominated diphenyl ethers) and alternative HFRs over a 30 year per

27 of polychlorinated biphenyls, polybrominated diphenyl ethers, and current-use/legacy pesticides were

28 s, polychlorinated biphenyls, polybrominated diphenyl ethers, and emerging persistent and bioaccumula

29 Bs), pentachlorophenol (PCP), polybrominated diphenyl ethers, and organochlorine pesticides (OCPs).

30 of polychlorinated biphenyls, polybrominated diphenyl ethers, and organochlorine through a river food

31 o PCBs, non dioxin-like PCBs, polybrominated diphenyl ethers, and perfluorinated alkyl substances and

32 ith 1-(het)aroyl-2-aryldiazenes in preheated diphenyl ether at ca. 150-250 degrees C for 5-25 min aff

33 t saFabI is the intracellular target for the diphenyl ether-based inhibitors.

34 o 9,9-dimethylxanthene (BD3), and finally to diphenyl ether (BD4 and BD5).

35 of small children (1-3 y old) to brominated diphenyl ether (BDE)-99 may exceed acceptable levels def

36 he flame retardant 2,2',4,4'-tetrabrominated diphenyl ether (BDE-47) have been shown to enhance adipo

37 etardant congener, 2,2',4,4'-tetrabrominated diphenyl ether (BDE-47), is often the major poly-BDE (PB

38 Brominated diphenyl ethers (BDE47, 99, 100, and 209) were measured

39 As the uses of polybrominated diphenyl ethers (BDEs) are being phased out in many coun

40 centrations (sigmaPBDE) of 15 polybrominated diphenyl ethers, BDEs 17, 28, 47, 49, 66, 71, 85, 99, 10

41 ation of saFabI inhibition by a series of 20 diphenyl ethers complemented by a collection of 9 saFabI

42 hlorinated biphenyl (PCB) and polybrominated diphenyl ether congeners is the dominant mode of uptake

43 hlorodiphenyltrichloroethane, and brominated diphenyl ether congeners, in higher trophic level (TL) o

44 The compound contains a benzimidazole diphenyl ether core that is flanked by the amidine catio

45 olychlorinated biphenyls, and polybrominated diphenyl ethers demonstrate significant maternal transfe

46 Values of whole fish Dlip-sil for brominated diphenyl ethers determined for three fish were in the ra

47 (including a newly discovered tribrominated diphenyl ether), dioxins, and bastadins, as well as the

48 an the bare Pd-Fe (<50%) in hydrotreating of diphenyl ether (DPE, modelling the strongest C-O linkage

49 lites of certain congeners of polybrominated diphenyl ether (e.g., 3-OH-BDE-47) have been suggested t

50 nd 27), diethers (e.g., 49, 50, and 56), and diphenyl ethers (e.g., 35 and 36) were the least active.

51 tetrahydrophthalimides (discussed below) and diphenyl ethers (e.g., acifluorfen) usually with little

52 Prenatal polybrominated diphenyl ether exposure and body mass index in children

53 Polybrominated diphenyl ether exposure and thyroid function tests in No

54 ornia children's exposures to polybrominated diphenyl ether flame retardants (PBDEs) are among the hi

55 sorbent Zn-atz-oba (H(2)oba = 4,4-dicarboxyl diphenyl ether; Hatz = 3-amino-1,2,4-triazole) enables s

56 The diphenyl ether herbicide acifluorfen at 1 microM strongl

57 oroacetanilide herbicide metolachlor and the diphenyl ether herbicide fluorodifen were fractionated i

58 GST V-V showed high GST activity towards the diphenyl ether herbicide fluorodifen, detoxified toxic a

59 Concentrations of polybrominated diphenyl ethers, hexabromocyclododecane (HBCDD), and nov

60 ative flame retardants (e.g., polybrominated diphenyl ethers, hexabromocyclododecane, bromobenzenes,

61 dely used as replacements for polybrominated diphenyl ethers in consumer products.

62 s, organochlorine pesticides, polybrominated diphenyl ethers in fat, and perfluoroalkyl substances in

63 rganochlorine pesticides, and polybrominated diphenyl ethers in mothers ranged from 897 to 13620 ng/g

64 chlorinated naphthalenes, and polybrominated diphenyl ethers in the environmentally relevant range 0-

65 e debromination pathways converting PBDEs to diphenyl ether, including several new routes, were ident

66 en the affinities of the investigated saFabI diphenyl ether inhibitors and their corresponding reside

67 ion of saFabI with triclosan and two related diphenyl ether inhibitors.

68 We report that this natural diphenyl ether inhibits Arabidopsis (Arabidopsis thalian

69 The diphenyl ether is highly twisted and gives the entire co

70 amidine compound containing a highly twisted diphenyl ether linkage.

71 Methoxy-brominated diphenyl ethers (MeO-BDEs) and chlorinated methyl- and d

72 Methoxylated polybrominated diphenyl ethers (MeO-PBDEs) have been found bioaccumulat

73 It also dehalogenated octa-brominated diphenyl ether mixture predominantly to tetra-BDEs, 2,4,

74 sulting crystal structures revealed that the diphenyl ether moiety of RT29 undergoes conformational c

75 Although hydroxylated polybrominated diphenyl ethers (OH-BDEs) are among the most abundant na

76 l formation from hydroxylated polybrominated diphenyl ethers (OH-PBDE) is a proposed pathway for PBDD

77 Hydroxylated polybrominated diphenyl ethers (OH-PBDEs) are of growing concern, as th

78 sion of selected hydroxylated polybrominated diphenyl ethers (OH-PBDEs) to dioxins and other products

79 mpounds, such as hydroxylated polybrominated diphenyl ethers (OH-PBDEs), their corresponding protein

80 Polybrominated diphenyl ethers partitioned comparably to legacy POPs.

81 e bioaccumulation patterns of polybrominated diphenyl ether (PBDE) and phthalate ester (PAE) pollutan

82 As a result of the polybrominated diphenyl ether (PBDE) ban in the mid-2000s, the chemical

83 hlorinated biphenyl (PCB) and polybrominated diphenyl ether (PBDE) concentrations and profiles in pai

84 (PCB) congeners 153 and 180, polybrominated diphenyl ether (PBDE) congeners 47 and 99, and p,p'-DDE.

85 inated naphthalene (PCN), and polybrominated diphenyl ether (PBDE) congeners as well as some pesticid

86 chloroethylene (DDE) and four polybrominated diphenyl ether (PBDE) congeners from maternal and/or chi

87 47 targeted FRs, including 12 polybrominated diphenyl ether (PBDE) congeners, 19 other brominated FRs

88 Polybrominated diphenyl ether (PBDE) exposure is associated with preter

89 Prenatal polybrominated diphenyl ether (PBDE) exposures are a public health conc

90 Polybrominated diphenyl ether (PBDE) flame retardants are environmental

91 Polybrominated diphenyl ether (PBDE) flame retardants are widespread, i

92 Polybrominated diphenyl ether (PBDE) flame retardants have been shown t

93 Polybrominated diphenyl ether (PBDE) flame retardants have been used in

94 involved in the metabolism of polybrominated diphenyl ether (PBDE) flame retardants in humans, result

95 s a biomarker for exposure to polybrominated diphenyl ether (PBDE) flame retardants was assessed in h

96 Polybrominated diphenyl ether (PBDE) flame retardants were once widely

97 With the phase-out of polybrominated diphenyl ether (PBDE) flame retardants, the use of new a

98 ated global human exposure to polybrominated diphenyl ether (PBDE) flame retardants.

99 Relative to commercial polybrominated diphenyl ether (PBDE) formulations, the ratio of PBDD/Fs

100 With the phase-out of the polybrominated diphenyl ether (PBDE) FR mixture PentaBDE in 2005, alter

101 placements for the phased-out polybrominated diphenyl ether (PBDE) mixtures, and they are now commonl

102 e retardants, including three polybrominated diphenyl ether (PBDE) replacement chemicals, were freque

103 hlorinated biphenyl (PCB) and polybrominated diphenyl ether (PBDE) residues and gene expression in em

104 own about the distribution of polybrominated diphenyl ethers (PBDE) -also known as flame retardants-

105 iethylhexyl phthalate (DEHP), polybrominated diphenyl ethers (PBDE) and polychlorinated biphenyls (PC

106 itats where contaminants like polybrominated diphenyl ethers (PBDE) are common.

107 The analytes were polybrominated diphenyl ethers (PBDE), Dechlorane Plus (DP), decabromod

108 Amphipods were exposed to polybrominated diphenyl ether (PBDEs) congeners (BDE-28, -47, -99, -100

109 nyls (PCBs) (plasma), and sum polybrominated diphenyl ethers (PBDEs) (plasma), 12-100-fold greater th

110 Polybrominated diphenyl ethers (PBDEs) alter thyroid hormone homeostasi

111 Polybrominated diphenyl ethers (PBDEs) and alternative flame retardants

112 50% sand) receiving selected polybrominated diphenyl ethers (PBDEs) and chlorinated paraffins (CPs)

113 e of a comprehensive suite of polybrominated diphenyl ethers (PBDEs) and current-use flame retardants

114 Thirty-five polybrominated diphenyl ethers (PBDEs) and eight other alternative flam

115 the certified NIST value for polybrominated diphenyl ethers (PBDEs) and had an average accuracy for

116 he dermal bioaccessibility of polybrominated diphenyl ethers (PBDEs) and hexabromocyclododecane (HBCD

117 ewed the available records of polybrominated diphenyl ethers (PBDEs) and hexabromocyclododecanes (HBC

118 ychlorinated biphenyl (PCBs), polybrominated diphenyl ethers (PBDEs) and induction of cytochrome's P4

119 the boiling points of several polybrominated diphenyl ethers (PBDEs) and methylated derivatives (MeO-

120 ame retardants (OFRs) such as polybrominated diphenyl ethers (PBDEs) and novel halogenated flame reta

121 r organic pollutants, such as polybrominated diphenyl ethers (PBDEs) and organophosphate esters (OPEs

122 In the present study, polybrominated diphenyl ethers (PBDEs) and other flame retardants (FRs)

123 Polybrominated diphenyl ethers (PBDEs) and poly- and perfluoroalkylated

124 lysis of ultratrace levels of polybrominated diphenyl ethers (PBDEs) and polybrominated dibenzo-p-dio

125 Polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (P

126 Polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (P

127 ompartment for the storage of polybrominated diphenyl ethers (PBDEs) and polychlorinated dibenzo-p-di

128 ores in 2013 and analyzed for polybrominated diphenyl ethers (PBDEs) and related flame retardants.

129 This is the first report of polybrominated diphenyl ethers (PBDEs) and select hexachlorocyclohexane

130 The concentrations of polybrominated diphenyl ethers (PBDEs) and selected alternative bromina

131 Polybrominated diphenyl ethers (PBDEs) are a class of brominated flame

132 Polybrominated diphenyl ethers (PBDEs) are a class of flame retardants

133 Polybrominated diphenyl ethers (PBDEs) are a class of persistent compou

134 Polybrominated diphenyl ethers (PBDEs) are a type of flame retardants w

135 Polybrominated diphenyl ethers (PBDEs) are bioaccumulating flame retard

136 Polybrominated diphenyl ethers (PBDEs) are brominated flame retardant c

137 (OH-) and methoxylated (MeO-) polybrominated diphenyl ethers (PBDEs) are compounds present in the mar

138 Polybrominated diphenyl ethers (PBDEs) are flame retardant chemicals us

139 Polybrominated diphenyl ethers (PBDEs) are flame-retardant chemicals th

140 ver, epidemiologic studies on polybrominated diphenyl ethers (PBDEs) are limited despite animal studi

141 Polybrominated diphenyl ethers (PBDEs) are lipophilic flame retardants

142 Polybrominated diphenyl ethers (PBDEs) are persistent and bioaccumulati

143 Polybrominated diphenyl ethers (PBDEs) are persistent chemicals that ha

144 Polybrominated diphenyl ethers (PBDEs) are persistent organic pollutant

145 Polybrominated diphenyl ethers (PBDEs) are persistent, bioaccumulative,

146 Polybrominated diphenyl ethers (PBDEs) are prevalent environmental poll

147 Polybrominated diphenyl ethers (PBDEs) are structurally similar to poly

148 Polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental con

149 Polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental pol

150 Polybrominated diphenyl ethers (PBDEs) are ubiquitous pollutants that c

151 ead use of persistent organic polybrominated diphenyl ethers (PBDEs) as commercial flame retardants h

152 atic hydrocarbons (PAHs), and polybrominated diphenyl ethers (PBDEs) at two urban sites indicated con

153 A reduction in the use of polybrominated diphenyl ethers (PBDEs) because of human health concerns

154 Prenatal exposures to polybrominated diphenyl ethers (PBDEs) can harm neurodevelopment in hum

155 Fish is the major source of polybrominated diphenyl ethers (PBDEs) for Finnish consumers.

156 timates of dietary intakes of polybrominated diphenyl ethers (PBDEs) for residents of areas of Taizho

157 and simple method to extract polybrominated diphenyl ethers (PBDEs) from human placenta for analysis

158 ,dibenzofurans (PBDD/Fs), and polybrominated diphenyl ethers (PBDEs) from trial combustion of 10 wt %

159 Polybrominated diphenyl ethers (PBDEs) have been used extensively to fl

160 Polybrominated diphenyl ethers (PBDEs) have been widely used as flame r

161 lorine pesticides (OCPs), and polybrominated diphenyl ethers (PBDEs) in air and soil, their fugacitie

162 ely used as a replacement for polybrominated diphenyl ethers (PBDEs) in commercial flame retardant mi

163 iously generated data set for polybrominated diphenyl ethers (PBDEs) in dated sediment cores of West

164 odevelopmental disorders, and polybrominated diphenyl ethers (PBDEs) in flame-retardant chemicals are

165 ort on patterns and trends in polybrominated diphenyl ethers (PBDEs) in the plasma of 284 bald eagle

166 Serum concentrations of polybrominated diphenyl ethers (PBDEs) in U.S. women are believed to be

167 ts that combined exposures to polybrominated diphenyl ethers (PBDEs) may exceed acceptable levels in

168 concentrations of individual polybrominated diphenyl ethers (PBDEs) ranged from 0.036 to 0.95 ng/g l

169 onsumer products treated with polybrominated diphenyl ethers (PBDEs) reach the end of their life cycl

170 Polybrominated diphenyl ethers (PBDEs) reduce blood concentrations of t

171 breast milk concentrations of polybrominated diphenyl ethers (PBDEs) that are among the highest in th

172 abromobisphenol A (TBBPA) and polybrominated diphenyl ethers (PBDEs) to nonhalogenated products, wher

173 absorption of eight mono- to deca-brominated diphenyl ethers (PBDEs) was investigated for the first t

174 ed commercial formulations of polybrominated diphenyl ethers (PBDEs) were banned in the United States

175 Rs), Dechlorane Plus (DP) and polybrominated diphenyl ethers (PBDEs) were investigated during a sampl

176 ated naphthalenes (PCNs), and polybrominated diphenyl ethers (PBDEs) were measured in needle, branch,

177 ated biphenyls (PCBs), and 14 polybrominated diphenyl ethers (PBDEs) were measured in two metropolita

178 Polybrominated diphenyl ethers (PBDEs) were widely used as flame retard

179 at predictors of exposure to polybrominated diphenyl ethers (PBDEs) with a focus on dietary and hous

180 Fourteen polybrominated diphenyl ethers (PBDEs), 14 non-BDE flame retardants (FR

181 for the measurement of eight polybrominated diphenyl ethers (PBDEs), 2,2',4,4',5,5'-hexabromobipheny

182 en developed to measure eight polybrominated diphenyl ethers (PBDEs), 2,2',4,4',5,5'-hexabromobipheny

183 cted in house dust, including polybrominated diphenyl ethers (PBDEs), 2-ethylhexyl-2,3,4,5-tetrabromo

184 polychlorinated biphenyls, 2 polybrominated diphenyl ethers (PBDEs), 3 phenols, 4 parabens, 10 phtha

185 polychlorinated biphenyls, 2 polybrominated diphenyl ethers (PBDEs), 5 perfluoroalkyl substances (PF

186 , and the recently phased-out polybrominated diphenyl ethers (PBDEs), all of which were historically

187 perfluoroalkyl acids (PFAAs), polybrominated diphenyl ethers (PBDEs), and "novel" brominated flame re

188 oroalkyl chemicals (PFCs), 10 polybrominated diphenyl ethers (PBDEs), and 36 polychlorinated biphenyl

189 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), and a range of pesticides.

190 ve purposes, levels of Mirex, polybrominated diphenyl ethers (PBDEs), and decabromodiphenylethane (DB

191 anochlorine pesticides, PAHs, polybrominated diphenyl ethers (PBDEs), and emerging flame retardants,

192 modiphenyl ethane (DBDPE), 13 polybrominated diphenyl ethers (PBDEs), and hexabromocyclododecane (HBC

193 ging flame retardants (EFRs), polybrominated diphenyl ethers (PBDEs), and isomers of hexabromocyclodo

194 zo-p-dioxins (PBDDs), dibenzofurans (PBDFs), diphenyl ethers (PBDEs), and mixed monobromo/chloro dibe

195 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), and organochlorine pesticides (

196 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), and organochlorine pesticides)

197 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), and organochlorine pesticides,

198 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), and other halogenated flame ret

199 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), and pesticides.

200 lated flame retardants, i.e., polybrominated diphenyl ethers (PBDEs), brominated biphenyl (BB)-153, a

201 neurodevelopmental impacts of polybrominated diphenyl ethers (PBDEs), but few have examined diagnosed

202 alogenated compounds, such as polybrominated diphenyl ethers (PBDEs), chloroethanes, and chloroethene

203 enzofurans (PBDD/Fs) from the polybrominated diphenyl ethers (PBDEs), commonly deployed in brominated

204 retardants/natural products (polybrominated diphenyl ethers (PBDEs), decabromobiphenyl (BB-209), dec

205 contaminants (HOCs), such as polybrominated diphenyl ethers (PBDEs), depends on the congeners' physi

206 r flame retardants, including polybrominated diphenyl ethers (PBDEs), halogenated phenols and bisphen

207 estigates the distribution of polybrominated diphenyl ethers (PBDEs), hexabromocyclododecane (HBCD) a

208 outh Africa, and analyzed for polybrominated diphenyl ethers (PBDEs), hexabromocyclododecane (HBCD),

209 Samples were analyzed for polybrominated diphenyl ethers (PBDEs), hexabromocyclododecanes (HBCDDs

210 e estimated human exposure to polybrominated diphenyl ethers (PBDEs), hexabromocyclododecanes (HBCDDs

211 y measuring concentrations of polybrominated diphenyl ethers (PBDEs), hexabromocyclododecanes (HBCDs)

212 nochlorine pesticides (OCPs), polybrominated diphenyl ethers (PBDEs), hydroxylated PBDEs (OH-PBDEs),

213 r decabromobiphenyl (BB-209), polybrominated diphenyl ethers (PBDEs), hydroxylated PBDEs (OH-PBDEs),

214 Since the phase-out of polybrominated diphenyl ethers (PBDEs), large amounts of alternative ha

215 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), novel brominated flame retardan

216 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), organochlorine pesticides (OCPs

217 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), organochlorine pesticides (OCPs

218 o flame retardants, including polybrominated diphenyl ethers (PBDEs), organophosphate esters (OPEs),

219 on three FR groups, including polybrominated diphenyl ethers (PBDEs), organophosphate FRs (OPFRs), an

220 w exposure of POPs, including polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs

221 Polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs

222 Polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs

223 ompounds (SVOCs)--phthalates, polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs

224 provided serum for measure of polybrominated diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs

225 n California and analyzed for polybrominated diphenyl ethers (PBDEs), polycyclic aromatic hydrocarbon

226 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), polycyclic aromatic hydrocarbon

227 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), polycyclic aromatic hydrocarbon

228 After the phase-out of polybrominated diphenyl ethers (PBDEs), the use of alternative flame re

229 For polybrominated diphenyl ethers (PBDEs), this within-age temporal trend

230 orinated biphenyls (PCBs) and polybrominated diphenyl ethers (PBDEs), to new environments during thei

231 chlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs), tris(4-chlorophenyl)methanol (T

232 to 2007 and analyzed for two polybrominated diphenyl ethers (PBDEs), two polychlorinated biphenyls (

233 Polybrominated diphenyl ethers (PBDEs), used as commercial flame-retard

234 a major source of exposure to polybrominated diphenyl ethers (PBDEs), which are found at high levels

235 e compounds are replacing the polybrominated diphenyl ethers (PBDEs), which have been removed or soon

236 ma concentrations of maternal polybrominated diphenyl ethers (PBDEs), which were used as flame retard

237 lorine pesticides (OCPs), and polybrominated diphenyl ethers (PBDEs).

238 n of BPs by UV irradiation of polybrominated diphenyl ethers (PBDEs).

239 ram (GLFMSP) and analyzed for polybrominated diphenyl ethers (PBDEs).

240 rinated compounds (PFCs), and polybrominated diphenyl ethers (PBDEs).

241 nated bisphenol A (BBPA), and polybrominated diphenyl ethers (PBDEs).

242 ng disruptive toxins, such as polybrominated diphenyl ethers (PBDEs).

243 nated flame retardants [e.g., polybrominated diphenyl ethers (PBDEs)] and perfluoroalkyl and polyfluo

244 -brominated flame retardants [polybrominated diphenyl ethers (PBDEs)]-are credibly linked to adverse

245 nochlorine pesticides (OCPs), polybrominated diphenyl-ethers (PBDEs), polycyclic aromatic hydrocarbon

246 legacy organochlorines [OCs], polybrominated diphenyl ethers [PBDEs,] and hexabromocyclododecane [HBC

247 s of several classes of POPs (polybrominated diphenyl ethers [PBDEs], polychlorinated biphenyls [PCBs

248 Both legacy (e.g., polybrominated diphenyl ethers; PBDEs) and emerging (e.g., hexabromoben

249 Although five polybrominated diphenyl ether (PDBE) congeners and BB153 are still freq

250 rbons, phthalates, aldehydes, polybrominated diphenyl ethers, perfluorinated substances, and alkylphe

251 tituted arenes such as anisole, thioanisole, diphenyl ether, phenol, naphthol, di- and trimethoxy ben

252 Cyperin is a natural diphenyl ether phytotoxin produced by several fungal pla

253 , polychlorinated biphenyls, polychlorinated diphenyl ethers, polybrominated dibenzo-p-dioxins and di

254 of organochlorine pesticides, polybrominated diphenyl ethers, polychlorinated biphenyls (PCBs), per-

255 c chemical group, followed by polybrominated diphenyl ethers, polycyclic aromatic hydrocarbons, and p

256 rimary amines undergo thermal cyclization in diphenyl ether providing easy access to 4-aryl-2-(trimet

257 mean concentrations of total polybrominated diphenyl ethers ranged from 11 to 150 pg/m3, and tributy

258 Debromination of PBDEs to diphenyl ether remains a rare phenomenon and is so far s

259 Pet tags were analyzed for 36 polybrominated diphenyl ethers, six organophosphate esters (OPEs), and

260 is reaction, absorption of light energy by a diphenyl ether substrate results in homolytic C-O bond c

261 000 ng g(-1) lw, and those of polybrominated diphenyl ethers ( summation operatorPBDEs) were 64,900 a

262 Contrarily, the "emerging" polybrominated diphenyl ethers' ( summation operator27PBDEs) median con

263 etween 10(6) and 10(9) (e.g., polybrominated diphenyl ethers), the relative importance of near- and f

264 on of the dithiocarbamate group in refluxing diphenyl ether to form alpha,beta- and/or beta,gamma-uns

265 Eleven polybrominated diphenyl ether (tri- to deca-BDE) congeners and 2,2',4,4

266 Tri- to decabrominated diphenyl ethers (tri-decaBDEs), isomer-specific hexabrom

267 ffect (k(H) /k(D) =5.7) for the reactions of diphenyl ether under H(2) and D(2) atmosphere and a posi

268 ommon trait of sewage sludge microbiota, and diphenyl ether was produced as the end-product at varyin

269 tion analysis of 39 mono- to heptabrominated diphenyl ethers was developed.

270 To study this, tri-decabrominated diphenyl ethers were analyzed in outgoing air samples co

271 ed to the discovery of a triazole-containing diphenyl ether with an increased residence time on InhA

272 ighest penta-BDEs removal (89.9 +/- 7.3%) to diphenyl ether within 60 days.