ライフサイエンスコーパス: diphenyl ether

1 tive to triclosan, a synthetic antimicrobial diphenyl ether.

2 tes a suitable alternative to decabrominated diphenyl ether.

3 tetrachloroethylene, and the polybrominated diphenyl ethers.

4 chlorinated naphthalenes, and polybrominated diphenyl ethers.

5 e a replacement of the banned polybrominated diphenyl ethers.

6 polybrominated biphenyls and polybrominated diphenyl ethers.

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

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

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

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

11 1 polybrominated biphenyl, 10 polybrominated diphenyl ethers, 36 polychlorinated biphenyls (PCBs), an

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

13 6-3.27; P = .001), and 1 BFR (polybrominated diphenyl ether 47: OR = 2.69; 95% CI, 1.49-4.85; P = .00

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

44 Polybrominated diphenyl ether exposure and thyroid function tests in No

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

46 The diphenyl ether herbicide acifluorfen at 1 microM strongl

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

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

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

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

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

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

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

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

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

56 amidine compound containing a highly twisted diphenyl ether linkage.

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

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

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

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

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

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

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

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

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

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

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

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

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

70 47 targeted FRs, including 12 polybrominated diphenyl ether (PBDE) congeners, 19 other brominated FRs

71 Polybrominated diphenyl ether (PBDE) flame retardants are environmental

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

87 Polybrominated diphenyl ethers (PBDEs) alter thyroid hormone homeostasi

88 Polybrominated diphenyl ethers (PBDEs) and alternative flame retardants

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

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

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

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

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

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

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

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

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

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

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

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

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

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

103 Polybrominated diphenyl ethers (PBDEs) are bioaccumulating flame retard

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

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

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

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

108 Polybrominated diphenyl ethers (PBDEs) are lipophilic flame retardants

109 Polybrominated diphenyl ethers (PBDEs) are persistent and bioaccumulati

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

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

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

113 Polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental con

114 Polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental pol

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

197 000 ng g(-1) lw, and those of polybrominated diphenyl ethers ( summation operatorPBDEs) were 64,900 a

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

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

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

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

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

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