ライフサイエンスコーパス: biphenyl

1 CO3, NaClO4, and an electron transfer agent (biphenyl).

2 s regarding expected human health effects of biphenyl.

3 s the first example of a diboron analogue of biphenyl.

4 ary van der Waals interactions with a planar biphenyl.

5 the database entries are for polychlorinated biphenyls.

6 mechanism that forms DDs and dihydroxylated biphenyls.

7 y chlorinated pesticides and polychlorinated biphenyls.

8 thesis of a wide range of highly fluorinated biphenyls.

9 , maternal concentrations of polychlorinated biphenyl 118 (-1.4 mm Hg [95% CI: -2.6 to -0.2 mm Hg]) a

10 ylhexyl phthalate (DEHP) and polychlorinated biphenyl 153 (PCB153) on DNA fragmentation and motility

11 n-butyl phthalate (Pht), and polychlorinated biphenyl 153 (PCB153) on the proteome of primary organot

12 ferent 2-aryl moieties, namely, 3-thienyl, p-biphenyl, 2-naphthyl (23-35), were synthesized and biolo

13 y investigating substituted 2-(dimethylamino)biphenyl-2'-carboxaldehydes as substrates for further ex

14 are the formation of 1,8-naphthalimides and biphenyl-2,2'-dicarboxamide motifs in high yields.

15 ), A1899 (2''-[(4-methoxybenzoylamino)methyl]biphenyl-2-carboxylic acid 2,4-difluorobenzylamide), and

16 a dual probe system based on 4'-substituted biphenyl-2-carboxylic acids (BPAs) for analysis of photo

17 Compound 21 [N-(4'-cyano-3'-fluoro-biphenyl-2-yl)-4-methoxy-benzenesulfonamide] exhibits re

18 is enabled by a designed chiral bifunctional biphenyl-2-ylphosphine ligand.

19 By using biphenyl-2-ylphosphines functionalized with a remote ter

20 4',6'-triisopropyl-3,4,5,6-tetramethyl-[1,1'-biphenyl]-2-yl)phos phine) was observed to result in the

21 natural product 3,4,3',4'-tetrahydroxy-1,1'-biphenyl (3), the previously synthesized 2,3,8,9-tetrahy

22 MFM-300(V(III)) {[V(III)2(OH)2(L)], LH4=biphenyl-3,3',5,5'-tetracarboxylic acid} can be oxidized

23 f the series resulted in the discovery of N-(biphenyl-3-ylmethyl)-2-(4-ethyl-6,6-dimethyl-2-oxomorpho

24 Two linkers (L1=4,4',4'',4'''-([1,1'-biphenyl]-3,3',5,5'-tetrayltetrakis(ethyne-2,1-diyl)) te

25 Fe2(dobpdc) (H4dobpdc = 4,4'-dihydroxy-[1,1'-biphenyl]-3,3'-dicarboxylic acid), the terphenyl derivat

26 3'""-(1,3,5-triazine-2,4,6-triyl)tris(([1,1'-biphenyl]-3-carbonitrile)) (CN-T2T) (DeltaE(ST) = 30 meV

27 lpiperazin-1-yl)-3'-(morpholinomethyl)-[1,1'-biphenyl]-3-yl)-6-oxo-4 -(trifluoromethyl)-1,6-dihydropy

28 Most impressive was 4-((6-([1,1'-biphenyl]-3-yl)-9H-purin-2-yl)amino) benzenesulfonamide

29 moyl-3-yl ester) and URB694 (6-hydroxy-[1,1'-biphenyl]-3-yl-cyclohexylcarbamate), in squirrel monkeys

30 The biphenyl 4-hydroxylase (B4H) coding sequence of rowan (S

31 ive investigation of self-assembly in the Fe-biphenyl-4,4'-dicarboxylate system, demonstrating that c

32 l-4,4'-dicarboxylic acid (H(2)Me(2)BPDC) and biphenyl-4,4'-dicarboxylic acid (H(2)BPDC), which are co

33 hiol self-assembled monolayer, consisting of biphenyl-4,4'-dithiol (BPDT), was presented.

34 ld junctions with prototypical molecules (Au-biphenyl-4,4'-dithiol-Au, Au-terphenyl-4,4''-dithiol-Au

35 With 3'-chloro-4'-(alpha-d-mannopyranosyloxy)biphenyl-4-carbonitrile (10j) a FimH antagonist with an

36 thoxy-3,4-dihydro-1 H-isoquinolin-2-ylmethyl)biphenyl-4-ol] (MC70), modifying the phenolic group of t

37 Compounds PKTHPP (1-{1-[6-(biphenyl-4-ylcarbonyl)-5,6,7,8-tetrahydropyrido[4,3-d]-p

38 h arylboronic acids and a new reagent, 3-((p-biphenyl-4-ylmethyl)thio)-6-methyltetrazine (b-Tz), proc

39 -(carbamimidoylcarbamoyl)-2',3-dinitro-[1,1'-biphenyl]-4-carboxylate ( 26: ) preferentially inhibited

40 -(carbamimidoylcarbamoyl)-2',3-dinitro-[1,1'-biphenyl]-4-carboxylate ( 27: ) acts both on adamantane-

41 omoaryl)-naphthalen-1-ols (or 2'-bromo-[1,1'-biphenyl]-4-ols) with internal alkynes, affording a seri

42 AMPK activators, exemplified by 5-((5-([1,1'-biphenyl]-4-yl)-6-chloro-1H-benzo[d]imidazol-2-yl)oxy)-2

43 the discovery of an aminopyrazole, 2-([1,1'-biphenyl]-4-yl)-N-(5-cyclobutyl-1H-pyrazol-3-yl)acetamid

44 )ethoxy)carbonyl)amino)isoxazol-5 -yl)-[1,1'-biphenyl]-4-yl)cyclopropane-1-carboxylic acid) in rhesus

45 roxyamino)-2-oxo-1-(3',4',5'-trifluoro-[1,1'-biphenyl]-4-yl)ethyl)-4-(methylsulfonamido)benzamide (6a

46 -1-ium-4-yl)-2,2',3',5',6'-pent amethyl[1,1'-biphenyl]-4-yl)methanide; and four-ring 4TTMC, dicyano(4

47 In this system, 4-cyano-4'-pentyl biphenyl (5CB) was doped with a sulfur- and nitrogen-con

48 llection resulted in the identification of a biphenyl acetic acid fragment 3, which bound in the palm

49 le, we describe the discovery of a series of biphenyl acid derivatives as potent APJ receptor agonist

50 We pursued further modifications to the biphenyl aglycone resulting in significantly improved ac

51 Starting from the carboxylate substituted biphenyl alpha-d-mannoside 9, affinity and the relevant

52 mplex, bridged biaryl molecule with imbedded biphenyl, amine, and lactam moieties, 7,8-diallyl-5-benz

53 Malus spp.) and pear (Pyrus spp.) accumulate biphenyl and dibenzofuran phytoalexins, with aucuparin a

54 Biphenyl and its metabolites may induce genetic damage,

55 lenes ([12]CPPs) containing four alternating biphenyl and naphthyl units were synthesized.

56 Polychlorinated biphenyl and organochlorine pesticide concentrations in

57 ctions of soil bacteria active in processing biphenyl and related aromatic compounds in soil, reveali

58 aromatic hydrocarbons, seven polychlorinated biphenyls and eight organochlorine pesticides were inves

59 s in K(EOM/olive oil) of two polychlorinated biphenyls and four chlorinated benzenes were below a fac

60 atropisomers of the naphthalene-substituted biphenyls and terphenyls bearing 1,2-type or 1,3-type ch

61 Sterically hindered naphthalene-substituted biphenyls and terphenyls were synthesized in good yields

62 otationally hindered naphthalene-substituted biphenyls and terphenyls.

63 early-life exposure to PCBs (polychlorinated biphenyls) and DDE [1,1-dichloro-2,2-bis(p-chlorophenyl)

64 In this Article, naphthalene, biphenyl, and haloarene-linked new triarylethenes are co

65 k of results regarding lead, polychlorinated biphenyls, and phthalates.

66 Polyfluorinated biphenyls are interesting and promising substrates for m

67 Although polychlorinated biphenyls are no longer sold as commercial mixtures, the

68 sistent contaminants such as polychlorinated biphenyls are thought to influence tissue homeostasis an

69 A series of substituted biphenyls are ultimately identified as future synthetic

70 Sn-mediated radical transformation of biphenyl aryl acetylenes into functionalized phenanthren

71 -dicyclohexylphosphino-2'-(N,N-dimethylamino)biphenyl as the ligand, both electron-rich and electron-

72 Next, we use benzene and polychlorinated biphenyls as examples to illustrate how this approach ma

73 he cationic gold phosphine complex [{PCy2 (o-biphenyl)}Au(NCMe)](+) SbF6 (-) (Cy=cyclohexyl) catalyze

74 veloped a novel multifunctional C2-symmetric biphenyl-based diamine-tethered bis(thiourea) organocata

75 igand with [(COD)IrOMe](2) ) was optimal for biphenyl-based phosphines.

76 rt an easily recyclable, novel Si-containing biphenyl-based template that directs efficient functiona

77 ominated diphenyl ethers (PBDEs), brominated biphenyl (BB)-153, and hexabromocyclododecane (HBCD), in

78 he loss rates of vapor phase polychlorinated biphenyls became more rapid between 1995 and 2015, which

79 ks by measuring and modeling polychlorinated biphenyl bioaccumulation by four marine benthic species.

80 tent organic pollutants, involves the upper (biphenyl, BP) and lower (benzoate, BZ) degradation pathw

81 Substituting the phenylene by a biphenyl bridge causes the lifetime of the CS state at z

82 f charge recombination in the triad with the biphenyl bridge.

83 Compared with the corresponding biphenyl-bridged 2D CCP-HATN-BDAN (2D CCP-BD), the bithi

84 ounds such as CBP (4,4-Bis(N-carbazolyl)-1,1-biphenyl) can lead to a moderate increase of about an or

85 iperidine or quinuclidine unit attached to a biphenyl carbamate, 5-fluoro substitution was responsibl

86 agonistic properties were determined for the biphenyl carbamates 13m and 13n, neutral antagonism was

87 eridinyl- and two quinuclidinium-substituted biphenyl carbamates OFH243 (13n), OFH244 (13m), OFH3911

88 pm) doped into a 4,4'-bis(N-carbazolyl)-1,1'-biphenyl, CBP, host.

89 ay bioaccumulation test with polychlorinated biphenyls, chlorpyrifos, and four marine benthic inverte

90 uran phytoalexins, with aucuparin as a major biphenyl compound.

91 were compared with the total polychlorinated biphenyl concentration trends.

92 eripubertal serum dioxin and polychlorinated biphenyl concentrations with pubertal timing among Russi

93 levels of HOCs, for example, polychlorinated biphenyl congeners, dichlorodiphenyltrichloroethane, and

94 ong children living near the polychlorinated biphenyl-contaminated New Bedford Harbor (NBH) Superfund

95 The biphenyl core has been studied for comparison.

96 rylfluorosulfate probes 3 and 4, featuring a biphenyl core, very selectively and efficiently modify c

97 furans (PCDFs), and coplanar polychlorinated biphenyls (CP-PCBs) concentrations and age-corrected tre

98 ere synthesized and evaluated, including the biphenyl derivative Fe2(dobpdc) (H4dobpdc = 4,4'-dihydro

99 nar UiO-67 ([Zr6O4(OH)4 (bpdc)6], bpdc: 4,4'-biphenyl dicarboxylate) and UiO-abdc ([Zr6O4(OH)4 (abdc)

100 of a natural occurring benzodioxole and its biphenyl dimer, which both display noteworthy biological

101 The prediction identified biphenyl dioxygenase from Paraburkholderia xenovorans LB

102 otent peptide 12f [His(2-biphenyl)-Trp-His(2-biphenyl)] displayed high in vitro activity against C. n

103 rans (PCDFs) and dioxin-like polychlorinated biphenyls (dl-PCBs) in the Pilica River and Sulejow Rese

104 ns (PCDD/Fs) and dioxin-like polychlorinated biphenyls (dl-PCBs) were measured in plankton samples fr

105 r mixing model with DDTs and polychlorinated biphenyls enabled source differentiation between shelf d

106 ation of experimental animal studies of oral biphenyl exposure took into account the variety of study

107 y is also a potential human health hazard of biphenyl exposure.

108 tential human health hazards associated with biphenyl exposure.

109 A) has evaluated the human health hazards of biphenyl exposure.

110 ictive models for cord serum polychlorinated biphenyls (expressed as a sum, [Formula: see text]), [Fo

111 n to optimize our previously described ortho-biphenyl Gal and GalNAc FmlH antagonists such as compoun

112 ing an ether-linked isopropylsulfonamide and biphenyl group, was pharmacologically augmented by conve

113 recognition, [4,4'-di(1H-tetrazol-5-yl)-1,1'-biphenyl] (H(2)L(3)) was used as the linker, which also

114 coupling of aryl boronic acids and esters to biphenyls has been recognized as a common byproduct in S

115 mitting dopants in 4,4'-bis(9H-carbazol-9-yl)biphenyl host exhibited bluish green electroluminescence

116 was doped into a 4,4'-bis(N-carbazolyl)-1,1'-biphenyl host layer, and the resultant orientation of th

117 Alpine glaciers, we analyzed polychlorinated biphenyls in an ice core from the temperate Silvretta gl

118 slower for DDs and faster for dihydroxylated biphenyls in comparison to that for triclosan.

119 sured concentrations of five polychlorinated biphenyls in different-size fish depurated over the cour

120 (L, 3,3',5,5'-tetra(1 H-imidazol-1-yl)-1,1'-biphenyl) in a 2:1 molar ratio yielded a water-soluble [

121 netic damage, but a role for genotoxicity in biphenyl-induced carcinogenicity has not been establishe

122 In contrast, the formation of biphenyl is facilitated by the coordination of a bidenta

123 ty of this strategy to access dihydroxylated biphenyls is demonstrated with several examples.

124 Human health effects of biphenyl: key findings and scientific issues.

125 Commencing with a biphenyl lead, bioisosteres formed by replacing one phen

126 phene as well as in a 1 nm thin carbonaceous biphenyl membrane.

127 vation at this receptor, among the tetrazolo-biphenyl-methyl derivatives, translating into excellent

128 electronic properties produced by phenyl and biphenyl moieties attached to the vinylene ends.

129 be trapped by the fast 6-endoclosure at the biphenyl moiety in good to excellent yields.

130 onformational change upon binding of the P1'-biphenyl moiety of the inhibitor suggests an explanation

131 logues with a prolonged half-life, while the biphenyl moiety revealed the most potent analogue 1b.

132 hrough a systematic SAR study carried out on biphenyl moiety.

133 us photocatalytic systems (dicyanoanthracene/biphenyl, N-methylquinolinium, triphenylpyrylium, and th

134 we report an SAR exploration of a series of biphenyl-N-[4-[4-(2,3-substituted-phenyl)piperazine-1-yl

135 ns of laboratory-generated SOA from toluene, biphenyl, naphthalene, and 1,8-dimethylnaphthalene.

136 action mechanisms of the phenyl radical with biphenyl/naphthalene theoretically and experimentally, w

137 Non-dioxin-like polychlorinated biphenyls (NDL-PCBs) contribute to the dietary intake of

138 and crowded beta-diketones featuring bulky o-biphenyl or m-terphenyl fragments were prepared in good

139 a, with substrates including polychlorinated biphenyls or dioxins.

140 sma concentrations of summed polychlorinated biphenyls, organochlorine pesticides, and polybrominated

141 ds, methyl triclosan (MTCS), polychlorinated biphenyls, organochlorine pesticides, and polycyclic aro

142 We measured polychlorinated biphenyls, organochlorine pesticides, polybrominated dip

143 s of dioxins, dibenzofurans, polychlorinated biphenyls, organochlorines, organophosphates, phenols, m

144 sruptor classes:bisphenol A, polychlorinated biphenyls, organophosphates, and polybrominated diphenyl

145 organochlorine pesticides, 1 polybrominated biphenyl (PBB), 7 perfluoroalkyl chemicals (PFCs), 10 po

146 n Michigan residents consumed polybrominated biphenyl (PBB)-laced animal products leading to one of t

147 gan residents were exposed to polybrominated biphenyls (PBBs) through an accidental contamination of

148 Here, we examined polychlorinated biphenyl (PCB) and polybrominated diphenyl ether (PBDE)

149 Physical partitioning of polychlorinated biphenyl (PCB) and polybrominated diphenyl ether congene

150 n to serum concentrations of polychlorinated biphenyl (PCB) congener groups and three chlorinated pes

151 processes in fish can alter polychlorinated biphenyl (PCB) congener patterns in fish, but these patt

152 ed the concentrations of 205 polychlorinated biphenyl (PCB) congeners in 26 food items: beef steak, b

153 chlorines along with all 209 polychlorinated biphenyl (PCB) congeners in surface water, treated and u

154 We propose that polychlorinated biphenyl (PCB) congeners represent an ideal tracer to qu

155 Polychlorinated biphenyl (PCB) congeners with multiple ortho chlorine su

156 stablished in 1988-1989, six polychlorinated biphenyl (PCB) congeners, hexachlorobenzene (HCB), and d

157 omatic hydrocarbon (PAH) and polychlorinated biphenyl (PCB) emissions.

158 AC) for in situ treatment of polychlorinated biphenyl (PCB) impacted sediments.

159 nt levels of Aroclor 1254, a polychlorinated biphenyl (PCB) mixture, on moult, fattening, migratory a

160 etoxifies highly chlorinated polychlorinated biphenyl (PCB) mixtures via 85 distinct dechlorination r

161 hloroethylene (p,p -DDE) and polychlorinated biphenyl (PCB) pollutants.

162 nts living around the former polychlorinated biphenyl (PCB) production plant in Anniston, Alabama.

163 Fs for other SVOCs including polychlorinated biphenyl (PCB), polychlorinated naphthalene (PCN), and p

164 el to estimate monthly serum polychlorinated biphenyl (PCB)-153 levels in 441 infants (ages 1-12 mont

165 within feeding range of the polychlorinated biphenyl (PCB)-contaminated New Bedford Harbor (NBH, MA,

166 1.53, 95% CI 0.90 to 2.61), polychlorinated biphenyls (PCB) 118 (HR 1.50, 95% CI 0.95 to 2.39), PCB

167 tigated the major sources of polychlorinated biphenyls (PCB) and interpreted the environmental fate p

168 trends in human exposure to polychlorinated biphenyls (PCB) at the population level using a mechanis

169 sk of inhalation exposure to polychlorinated biphenyls (PCB) cannot be assessed with high confidence

170 uget, IL, where 373000 mt of polychlorinated biphenyls (PCB) was produced between 1936 and 1977 and 1

171 les of concentrations of 101 polychlorinated biphenyl (PCBs) congeners, congener groups and three chl

172 The levels of polychlorinated biphenyl (PCBs), polybrominated diphenyl ethers (PBDEs)

173 ately 95% DDE) (plasma), sum polychlorinated biphenyls (PCBs) (plasma), and sum polybrominated diphen

174 In this study, we tested 25 polychlorinated biphenyls (PCBs) [PCB 3, 11, 52, 126, 136, and 153 and t

175 Lipophilic polychlorinated biphenyls (PCBs) accumulate with obesity, but during wei

176 UMAN model was evaluated for polychlorinated biphenyls (PCBs) and applied to cVMS in combination with

177 nitude greater than those of polychlorinated biphenyls (PCBs) and decabromodiphenyl ether (BDE209).

178 land heavily contaminated by polychlorinated biphenyls (PCBs) and dioxins (PCDD/Fs), occurring in the

179 Polychlorinated biphenyls (PCBs) and enantiomer fractions (EFs) of PCB e

180 are structurally similar to polychlorinated biphenyls (PCBs) and have both central (learning and mem

181 tions between serum PBBs and polychlorinated biphenyls (PCBs) and markers of thyroid function among M

182 Polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) ar

183 Polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) co

184 ankton for a range of legacy polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) wa

185 outdoor contaminants such as polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) we

186 c pollutants (POPs), such as polychlorinated biphenyls (PCBs) and polybrominated diphenyl ethers (PBD

187 For polychlorinated biphenyls (PCBs) and polychlorinated dibenzo-p-dioxins (

188 regional sources of airborne polychlorinated biphenyls (PCBs) and population-scale airborne exposure,

189 lutants including lipophilic polychlorinated biphenyls (PCBs) and protein-associated per- and polyflu

190 ant occurrence of lipophilic polychlorinated biphenyls (PCBs) and protein-associated poly- and perflu

191 Polychlorinated biphenyls (PCBs) and some pesticides were measured in ai

192 Polychlorinated biphenyls (PCBs) are a group of 209 persistent organic p

193 Polychlorinated biphenyls (PCBs) are environmental toxicants; PCB exposu

194 Polychlorinated biphenyls (PCBs) are known human carcinogens that are by

195 Coplanar and noncoplanar polychlorinated biphenyls (PCBs) are known to have different routes and

196 Polychlorinated biphenyls (PCBs) are persistent hazardous chemicals that

197 Polychlorinated biphenyls (PCBs) are toxic, persistent, and lipophilic c

198 Polychlorinated biphenyls (PCBs) are widespread, persistent contaminants

199 mend chlorpyrifos, lead, and polychlorinated biphenyls (PCBs) be systematically reviewed in order to

200 cting the bioaccumulation of polychlorinated biphenyls (PCBs) by pelagic and mobile fish and shellfis

201 Polychlorinated biphenyls (PCBs) continue to be contaminants of concern

202 Both mercury (Hg) and polychlorinated biphenyls (PCBs) demonstrate food web biomagnification i

203 Polychlorinated biphenyls (PCBs) had both agonistic and antagonistic eff

204 Exposure to chiral polychlorinated biphenyls (PCBs) has been associated with neurodevelopme

205 microbial dechlorination of polychlorinated biphenyls (PCBs) has been observed in sediments over the

206 tudies, the incorporation of polychlorinated biphenyls (PCBs) has been quantified in the accumulation

207 ides and the more persistent polychlorinated biphenyls (PCBs) have well-established dose-dependent to

208 the spatial distribution of polychlorinated biphenyls (PCBs) in air.

209 r cultures on degradation of polychlorinated biphenyls (PCBs) in dry fermented sausages over 28days o

210 ied independently to measure polychlorinated biphenyls (PCBs) in mesocosms with (1) New Bedford Harbo

211 Indoor air concentrations of polychlorinated biphenyls (PCBs) in some buildings are one or more order

212 Concentrations of polychlorinated biphenyls (PCBs) in the Delaware River currently exceed

213 mbient air concentrations of polychlorinated biphenyls (PCBs) in Zurich, Switzerland, are reported fo

214 Plants metabolize polychlorinated biphenyls (PCBs) into hydroxylated derivatives (OH-PCBs)

215 quantifying incorporation of polychlorinated biphenyls (PCBs) into the Silvretta glacier, a temperate

216 Degradation of polychlorinated biphenyls (PCBs) is initiated by cytochrome P450 (CYP) e

217 ling of strongly hydrophobic polychlorinated biphenyls (PCBs) is still challenged by slow approach to

218 such as dioxins, furans, and polychlorinated biphenyls (PCBs) may influence leukocyte telomere length

219 ons (PAHs), heavy metals and polychlorinated biphenyls (PCBs) over the past decade is discussed.

220 We investigated whether polychlorinated biphenyls (PCBs) partitioning between the dissolved and

221 Polychlorinated biphenyls (PCBs) pose significant risk to the developing

222 Coplanar polychlorinated biphenyls (PCBs) promote adipocyte inflammation and impa

223 Polychlorinated biphenyls (PCBs) remain chemicals of concern more than t

224 Balance Project (LMMBP) for polychlorinated biphenyls (PCBs) that was conducted in 1994-1995.

225 or three cVMS, and for three polychlorinated biphenyls (PCBs) that were used as reference chemicals.

226 nthesis of 12 (37)Cl-labeled polychlorinated biphenyls (PCBs) was carried out by the chlorination of

227 Polychlorinated-biphenyls (PCBs) were introduced in the late 1920s and u

228 henyl ethers (PBDEs), and 36 polychlorinated biphenyls (PCBs) were measured before conception for 234

229 The transfer kinetics of 14 polychlorinated biphenyls (PCBs) were measured in gut fluid mimic system

230 Polychlorinated biphenyls (PCBs) with less chlorine atoms exhibit a grea

231 f environmentally persistent polychlorinated biphenyls (PCBs) with lower numbers of chlorine atoms (L

232 -PBDEs) and organochlorines (polychlorinated biphenyls (PCBs), 1,1-bis(4,4'-dichlorodiphenyl)-2,2,2-t

233 nzodioxins/dibenzofurans, 18 polychlorinated biphenyls (PCBs), 3 hexabromocyclododecane (HBCD) isomer

234 of weighted quartiles for 5 polychlorinated biphenyls (PCBs), 7 polycyclic aromatic hydrocarbons (PA

235 ning the biomagnification of polychlorinated biphenyls (PCBs), a globally prevalent group of regulate

236 ochlorine pesticides (OCPs), polychlorinated biphenyls (PCBs), and brominated flame retardants (BFRs)

237 -p-dioxins (PCDDs)], furans, polychlorinated biphenyls (PCBs), and corresponding toxic equivalents (T

238 and dibenzofurans (PCDD/Fs), polychlorinated biphenyls (PCBs), and hexachlorobenzene (HCB) in streamw

239 holorethylene (p,p -DDE) and polychlorinated biphenyls (PCBs), and sperm aneuploidy in men from the g

240 diphenyl ethers (PBDEs), two polychlorinated biphenyls (PCBs), and two organochlorine pesticides usin

241 Dioxins, furans, and polychlorinated biphenyls (PCBs), dioxin-like and non-dioxin-like, have

242 c Pollutants (POPs), such as polychlorinated biphenyls (PCBs), have been reported in some developing

243 sure to another contaminant, polychlorinated biphenyls (PCBs), may be responsible for the positive fi

244 romatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), and

245 ted diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), and

246 during 2010-2011, including polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), poly

247 veral ubiquitous pollutants (polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), poly

248 ese contaminants, as well as polychlorinated biphenyls (PCBs), organochlorine pesticides, and polyaro

249 ybrominated diphenyl ethers, polychlorinated biphenyls (PCBs), per- and polyfluoroalkyl substances (P

250 romatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs)

251 esponding flows reported for polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs)

252 or legacy and emerging POPs (polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs)

253 h significantly higher total polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs)

254 ted diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins and

255 romatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), polychlorinated naphthalenes (PCNs), a

256 ficients were determined for polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons (PAHs

257 ted diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons (PAHs

258 ment concentrations of seven polychlorinated biphenyls (PCBs), seven polycyclic aromatic hydrocarbons

259 lorine pesticides (OCPs) and polychlorinated biphenyls (PCBs), which are biomagnified along the food

260 Serum concentrations of polychlorinated biphenyls (PCBs), which are chemicals with endocrine-dis

261 homogenized and spiked with polychlorinated biphenyls (PCBs), with silicone films of variable thickn

262 1254 (A-1254), a mixture of polychlorinated biphenyls (PCBs).

263 entally relevant mixtures of polychlorinated biphenyls (PCBs).

264 ic organic chemicals such as polychlorinated biphenyls (PCBs).

265 ive for in situ treatment of polychlorinated biphenyls (PCBs).

266 sed to study the toxicity of polychlorinated biphenyls (PCBs); however, it is typically unknown how m

267 ted diphenyl ethers [PBDEs], polychlorinated biphenyls [PCBs], and organochlorine pesticides [OCPs])

268 the surface (e.g., sum of 14 polychlorinated biphenyls, PCBs: 0.84 pg L(-1)) were similar to previous

269 , organochlorine pesticides, polychlorinated biphenyls, polybrominated diphenyl ethers, and emerging

270 stigate transfer pathways of polychlorinated biphenyls, polybrominated diphenyl ethers, and organochl

271 s: polychlorinated benzenes, polychlorinated biphenyls, polychlorinated dibenzodioxins, polychlorinat

272 nce of Henry's constants for polychlorinated biphenyls, polychlorinated naphthalenes, and polybromina

273 xanediamine with 5,15-di[3',5'-diformyl(1,1'-biphenyl)]porphyrin affords a porphyrin tubular organic

274 The available health effects data for biphenyl provides suggestive evidence for carcinogenicit

275 (II)cycles derived from various 2-(N-R-amino)biphenyls (R = H, Me, CF3CO, MeSO2, CF3SO2) react with h

276 reductive elimination to generate ethane and biphenyl, respectively.

277 substituted side arms (with double-torsional biphenyl rings) of tetratopic porphyrin linkers leads to

278 4-Hydroxylation of the biphenyl scaffold, formed by biphenyl synthase (BIS), is

279 ion around the central carbon-carbon bond of biphenyl so that it could be directly observed by x-ray

280 (ortho-tolyl)amide and o,o,o'-trisubstituted biphenyl structural units to provide a geometry better-s

281 Legacy polychlorinated biphenyls ( summation operator18PCBs) and polychlorinate

282 xylation of the biphenyl scaffold, formed by biphenyl synthase (BIS), is catalyzed by a cytochrome P4

283 he basis of Wittig's seminal observations on biphenyl synthesis from phenyl lithium and fluorobenzene

284 an appropriate aromatic system, such as the biphenyl system, and a free carboxyl group leads to high

285 The applicability of this D-shaped biphenyl template-based strategy is demonstrated by synt

286 cular copolymerization of chiral and achiral biphenyl tetracarboxamides in alkanes.

287 Importantly, one of the compounds, biphenyl tetrazole tert-butyl Cl-amidine (compound 13),

288 Here, we report a class of biphenyl triazoles among which stands out a lead compoun

289 The most potent peptide 12f [His(2-biphenyl)-Trp-His(2-biphenyl)] displayed high in vitro a

290 e beta-elimination pathway is suppressed for biphenyl-type ligands due to the shielding of Pd(II) by

291 bacterial guilds involved in utilizing (13)C-biphenyl (unchlorinated analogue of PCBs) and/or (13)C-b

292 m Sphingobium sp. catabolizes lignin-derived biphenyl via a meta-cleavage pathway.

293 Interestingly, the axially chiral biphenyl was found to be configurationally stable, but t

294 A rather nonpolar model analyte, biphenyl, was found to significantly change ionization p

295 enzo-p-dioxins (DDs) and 2,2'-dihydroxylated biphenyls-was also investigated.

296 hydrocinnamoyl ketones, Weinreb amides, and biphenyl Weinreb amides.

297 cinogenicity and noncancer health hazards of biphenyl were examined based on evidence from experiment

298 l)benzene or 4,4'-bis(diethylphosphonomethyl)biphenyl with C(3) -symmetric 2,3,8,9,14,15-hexa(4-formy

299 PCBs) was carried out by the chlorination of biphenyl with isotopically enriched chlorine gas, genera

300 tical withCSi(Me)2CH2CH2SiMe2H}] (P=P(tBu)2o-biphenyl) with triphenylcarbenium tetrakis(pentafluoroph