ライフサイエンスコーパス: biphenyl

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

2 ary van der Waals interactions with a planar biphenyl.

3 s regarding expected human health effects of biphenyl.

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

5 the database entries are for polychlorinated biphenyls.

6 ment and factors of 3-10 for polychlorinated biphenyls.

7 reductive dechlorination of polychlorinated biphenyls.

8 thesis of a wide range of highly fluorinated biphenyls.

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

10 hloroethene (rho = 0.017) or polychlorinated biphenyl 153 (rho = -0.016), the other main organochlori

11 s, exemplified by dirhodium tetrakis[(R)-(1-(biphenyl)-2,2-diphenylcyclopropanecarboxylate)] [Rh2(R-B

12 ligand design based on the privileged (1,1'-biphenyl)-2-ylphosphine framework that offers a potentia

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

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

15 ecursors, C3h-symmetric cyclotri(ethynylene)(biphenyl-2,4'-diyl) and cyclotri(ethynylene)(p-terphenyl

16 arger cyclic tetramer cyclotetra(ethynylene)(biphenyl-2,4'-diyl).

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

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

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

20 eCNAu(JohnPhos)](+)SbF6(-) (JohnPhos = (1,1'-biphenyl-2-yl)-di-tert-butylphosphine) and the acetate a

21 eCNAu(JohnPhos)](+)SbF6(-) (JohnPhos = (1,1'-biphenyl-2-yl)-di-tert-butylphosphine) as the catalyst,

22 By functionalizing the privileged biphenyl-2-ylphosphine with a basic amino group at the r

23 molecular C-N bond formation of 2'-halo[1,1'-biphenyl]-2-amines by the photoinitiated SRN1 mechanism

24 molecular 7-endo-dig cyclization of 1-([1,1'-biphenyl]-2-yl)alkynones is reported.

25 4',6'-triisopropyl-3,4,5,6-tetramethyl-[1,1'-biphenyl]-2-yl)phos phine) was observed to result in the

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

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

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

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

30 l organic molecule, 4'-fluoro-N-phenyl-[1,1'-biphenyl]-3-carboxamide, was designed as a generic scaff

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

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

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

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

35 We prepared 13 derivatives of N-(biphenyl-4'-yl)methyl (R)-2-acetamido-3-methoxypropionam

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

37 sing this platform, we study prototypical Au-biphenyl-4,4'-dithiol-Au and Au-fullerene-Au junctions t

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

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

40 of ruthenium(II) arene complexes with the 4-(biphenyl-4-carbonyl)-3-methyl-1-phenyl-5-pyrazolonate li

41 Biphenyl-4-carboxylic acid-[2-(1H-indol-3-yl)-ethyl]-met

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

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

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

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

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

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

48 3,3,3-hexafluoro-2-hydroxypropan-2-yl)-[1,1'-biphenyl]-4-yl)met hyl)piperazin-1-yl) ethanone] suppres

49 -1-ium-4-yl)-2,2',3',5',6'-pent amethyl[1,1'-biphenyl]-4-yl)methanide; and four-ring 4TTMC, dicyano(4

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

51 intramolecular C-N and C-O cyclization of N-(biphenyl)acetamides based on the substituent electronic

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

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

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

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

56 Biphenyl and its metabolites may induce genetic damage,

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

58 Polychlorinated biphenyl and organochlorine pesticide concentrations in

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

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

61 -p-dioxins and dibenzofurans, polybrominated biphenyls and polybrominated diphenyl ethers.

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

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

64 otationally hindered naphthalene-substituted biphenyls and terphenyls.

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

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

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

68 Polychlorinated biphenyls are among the most well-studied endocrine-disr

69 Polyfluorinated biphenyls are interesting and promising substrates for m

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

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

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

73 ese include methoxy-substituted benzenes and biphenyls, aromatic amines, and substituted acetanilides

74 icants: lead, methylmercury, polychlorinated biphenyls, arsenic, and toluene.

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

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

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

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

79 Biphenyl-based compound 13f, the most active compound of

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

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

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

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

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

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

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

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

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

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

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

91 The biphenyl core has been studied for comparison.

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

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

94 The results showed that both 2-biphenyl derivative 20b and elongated derivative 6g beha

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

96 The biphenyl derivatives 2 and 3 are prototypes of a novel c

97 ngated analogues, (c) 2H-chromene, and (d) 2-biphenyl derivatives.

98 new family of chiral nucleophilic catalysts, biphenyl-derived phosphepines, and we apply them to an e

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

100 4-diazophenyl-dicarboxylate) and UWDM-3 (1,4-biphenyl-dicarboxylate) show that both frameworks are la

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

102 The prediction identified biphenyl dioxygenase from Paraburkholderia xenovorans LB

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

104 ns (PCDD/Fs) and dioxin like polychlorinated biphenyls (dl-PCB) is evaluated for the first time in th

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

106 , 4,4'-di(1H-phenanthro[9,10-d]imidazol-2-yl)biphenyl (DPI-BP), which can be dissolved into halogenat

107 One cyclic biphenyl ether compound inhibited intraerythrocytic grow

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

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

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

111 tential human health hazards associated with biphenyl exposure.

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

113 ligand that contains two electron-rich ortho-biphenyl groups and a cyclohexyl substituent.

114 and size of the organic linker in the order biphenyl > phenylene > ethanediyl.

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

132 er selected for hydroxylated polychlorinated biphenyl (OH-PCB) was covalently immobilized on the surf

133 Hydroxylated metabolites of polychlorinated biphenyls (OH-PCBs) have been found to be ubiquitous in

134 Their biphenyl or terphenyl connectivity prevents these macroc

135 a, with substrates including polychlorinated biphenyls or dioxins.

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

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

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

139 time, the plant manufactured polybrominated biphenyls (PBBs), hexabromobenzene (HBB), 1,1,1-trichlor

140 Polychlorinated biphenyl (PCB) and polybrominated diphenyl ether (PBDE)

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

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

143 as sorbent materials for 11 polychlorinated biphenyl (PCB) congeners in aqueous concentrations in th

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

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

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

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

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

149 ence linking toxic injury to polychlorinated biphenyl (PCB) exposure is typically confounded by the c

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

151 dechlorinate the commercial polychlorinated biphenyl (PCB) mixture Aroclor 1260.

152 PME) GC/MS data objects of 7 polychlorinated biphenyl (PCB) mixture standard solutions.

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

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

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

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

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

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

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

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

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

162 re is a wealth of studies of polychlorinated biphenyls (PCB) in surface water and biota of the Arctic

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

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

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

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

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

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

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

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

171 lative and toxic pollutants (polychlorinated biphenyls (PCBs) and hexachlorobenzene (HCB)) to lipid-n

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

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

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

175 ted diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs) and p,p'-dichlorodiphenyldichloroethyle

176 between prenatal exposure to polychlorinated biphenyls (PCBs) and p,p'-dichlorodiphenyldichloroethyle

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

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

179 y of contaminants, including polychlorinated biphenyls (PCBs) and polychlorinated dibenzo-p-dioxins a

180 and target analytes included polychlorinated biphenyls (PCBs) and polychlorinated dibenzo-p-dioxins a

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

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

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

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

185 Polychlorinated biphenyls (PCBs) are persistent hazardous chemicals that

186 Non-dioxin-like (NDL) polychlorinated biphenyls (PCBs) are widespread environmental contaminan

187 The release of polychlorinated biphenyls (PCBs) by a military radar station into Saglek

188 organic carbon content, and polychlorinated biphenyls (PCBs) concentrations in mussels and sediments

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

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

191 Chiral polychlorinated biphenyls (PCBs) display variable atropisomeric enrichme

192 esolved historical record of polychlorinated biphenyls (PCBs) from an Alpine ice core (Fiescherhorn g

193 cients at 37 degrees C of 18 polychlorinated biphenyls (PCBs) from water into (i) triolein (Ktriolein

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

195 lorine (OC) insecticides and polychlorinated biphenyls (PCBs) have been shown to have estrogenic, ant

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

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

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

199 for the determination of 18 polychlorinated biphenyls (PCBs) in fish was developed and validated.

200 that affect accumulation of polychlorinated biphenyls (PCBs) in humans are complex and not fully und

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

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

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

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

205 osition and incorporation of polychlorinated biphenyls (PCBs) into an Alpine glacier (Fiescherhorn, S

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

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

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

209 ata suggest that exposure to polychlorinated biphenyls (PCBs) may induce ototoxicity, though results

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

211 ability in concentrations of polychlorinated biphenyls (PCBs) measured in residential dust.

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

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

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

215 atic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs) tend to accumulate in sediment beds whe

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

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

218 tic hydrocarbons (PAHs), and polychlorinated biphenyls (PCBs) using gas chromatography-mass spectrome

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

220 hexachlorobenzene (HCB) and polychlorinated biphenyls (PCBs) was studied for the alga Monoraphidium

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

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

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

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

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

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

227 metabolites, bisphenol A, 25 polychlorinated biphenyls (PCBs), 6 organochlorine pesticides, 8 bromina

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

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

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

231 to respire on the notorious polychlorinated biphenyls (PCBs), and functional genes responsible for P

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

233 ted diphenyl ethers (PBDEs), polychlorinated biphenyls (PCBs), and persistent pesticides have been me

234 romatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and polychlorinated dibenzo-p-dioxins/

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

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

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

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

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

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

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

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

243 Polychlorinated biphenyls (PCBs), organochlorine pesticides, and methylm

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

245 The contaminants were polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs)

246 w- to subppb) GC-MS data for polychlorinated biphenyls (PCBs), polybrominated diphenyl ethers (PBDEs)

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

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

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

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

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

252 e positively correlated with polychlorinated biphenyls (PCBs), the dominant POP in beluga.

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

254 1254 (A-1254), a mixture of polychlorinated biphenyls (PCBs).

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

256 atic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs).

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

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

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

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

261 p-dioxins and dibenzofurans, polychlorinated biphenyls, polychlorinated diphenyl ethers, polybrominat

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

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

264 direct intramolecular C-N cyclization of N-(biphenyl)pyridin-2-amines to 6-arylbenzimidazoles and N-

265 zoles and carbazoles from the reaction of N-(biphenyl)pyridin-2-amines with hypervalent iodine(III) r

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

267 reductive elimination to generate ethane and biphenyl, respectively.

268 taminated with petroleum and polychlorinated biphenyls, respectively, and variations in AC-sediment c

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

270 4-Hydroxylation of the biphenyl scaffold, formed by biphenyl synthase (BIS), is

271 hile reductive elimination to form Fe(eta(6)-biphenyl)(SciOPP) occurs upon reaction of FeCl2(SciOPP)

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

273 Additional displacement of the PMIs by a biphenyl spacer along the long axis prevents excimer for

274 y columns manufactured with phenyl-hexyl and biphenyl stationary phases (r(2) > 0.98).

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

276 optimization round, we explored a series of biphenyl-substituted iminosugars of both configurations

277 Biphenyl-substituted L-ido-configured deoxynojirimycin d

278 Legacy polychlorinated biphenyls ( summation operator18PCBs) and polychlorinate

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

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

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

282 th dozens of isomers (e.g., tetrachlorinated biphenyls, TeCBs).

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

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

285 med the ability of the Pdo system to oxidize biphenyl, the LMW PAHs naphthalene, phenanthrene, anthra

286 mprising thiol-modified bis(diarylamino)4,4'-biphenyl (TPD) molecules attached to a CdS quantum dot (

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

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

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

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

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

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

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

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

295 Fs for birds, while RePs for polychlorinated biphenyls were most similar to TEFs for fishes.

296 rganic contaminants (such as polychlorinated biphenyls) were retained and concentrated in adults, cau

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

298 hydrocarbons and 93-97% for polychlorinated biphenyls with 5 and 4 wt % AC dose, respectively, when

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

300 yl complex [(P)Au(eta(1)-C7H7)] (P=P(tBu)2(o-biphenyl)) with triphenylcarbenium tetrafluoroborate at