ライフサイエンスコーパス: diphenyl

1 r orbital (HOMO) of N,N'-bis(1-naphthyl)N,N'-diphenyl-1,1'-biphenyl-4,4'-diamine (NPB) and lowest uno

2 ,9-dimethyl-1,10-phenanthroline (13), or 4,7-diphenyl-1,10-phenanthroline (14), were synthesized and

3 r samples after development 2,9-dimethyl-4,7-diphenyl-1,10-phenanthroline (BCP) coprecipitation proce

4 ,8-tetramethyl-1,10-phenanthroline 3, or 4,7-diphenyl-1,10-phenanthroline 4) can be tuned by subtle l

5 formula [ReO(OMe)(N^N)Cl2], where N^N = 4,7-diphenyl-1,10-phenanthroline, 1, or 3,4,7,8-tetramethyl-

6 and [Ru(dqpCO2Me)(ptpy)](2+) (2) (DIP = 4,7-diphenyl-1,10-phenanthroline, bdt = 1,2-benzenedithiolat

7 describe the development of a series of 1,4-diphenyl-1,2,3-triazole compounds that inhibit the Nrf2-

8 xyl)-fluorenyl-2,7-diyl)-end capped with 2,5-diphenyl-1,2,4-oxadiazole (PFLO) was used as the immobil

9 1,6-Diphenyl-1,3,5-hexatriene (DPH) is a commonly used fluor

10 monoclinic and orthorhombic crystals of 1,6-diphenyl-1,3,5-hexatriene.

11 n of 3-hydroxyflavones with trans, trans-1,4-diphenyl-1,3-butadiene is described.

12 ,6-bis(pyridyl)-1,2,4,5-tetrazine; dbm = 1,3-diphenyl-1,3-propanedionate) is reported.

13 benzthiazoline-6-sulphonic acid) (ABTS), 2,2-diphenyl-1-pcrylhydrazyl (DPPH), and 2,2'-azobis-2-methy

14 reducing antioxidant capacity (FRAP) and 2,2-diphenyl-1-picryhydrazyl (DPPH) free radical scavenging

15 mined using two different methods: DPPH (2,2-diphenyl-1-picryl hydrazyl) and ABTS (2,2'-azino-bis-3-e

16 nzothiazoline-6-sulfonic acid) and DPPH (2,2-diphenyl-1-picryl-hydrazyl-hydrate), which allowed us to

17 ctrochemical method based on the use of 2,2'-diphenyl-1-picrylhidrazyl free radical (DPPH) for the de

18 The decrease in 2,2'-diphenyl-1-picrylhidrazyl peak current intensity was mea

19 essible to be used as an alternative to 2,2'-diphenyl-1-picrylhidrazyl spectrophotometric based metho

20 atively high antiradical activity toward 2,2-diphenyl-1-picrylhydrazyl (7-92% and 5-93% for cognacs a

21 st scavenging activity determined using 2,2'-diphenyl-1-picrylhydrazyl (DPPH) (87% DPPH inhibition).

22 (using the total phenolic content (TPC), 2,2-diphenyl-1-picrylhydrazyl (DPPH) and ferric reducing ant

23 ty determined using the Folin-Ciocalteu, 2,2-diphenyl-1-picrylhydrazyl (DPPH) and ferric reducing ant

24 erric reducing antioxidant power (FRAP), 2,2-diphenyl-1-picrylhydrazyl (DPPH) and Folin-Ciocalteu (FC

25 T) were evaluated using chemical assays, 2,2-diphenyl-1-picrylhydrazyl (DPPH) and Oxygen radical abso

26 atography (HPLC) analysis combined with 2,2'-diphenyl-1-picrylhydrazyl (DPPH) assay (HPLC-DPPH).

27 tract was determined photometrically by 2,2'-diphenyl-1-picrylhydrazyl (DPPH) assay and by the use of

28 tested using spectrophotometric methods, 2,2-diphenyl-1-picrylhydrazyl (DPPH) free radical scavenging

29 A stable chromogenic radical 2,2-diphenyl-1-picrylhydrazyl (DPPH) is commonly used for th

30 mpound 1 displayed comparatively greater 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical quenching poten

31 ated for antioxidant activities with the 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical scavenging acti

32 ormed by: total phenolic contents (TPC), 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical scavenging acti

33 after pulsed electric fields (PEF) using 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical scavenging and

34 cant differences were found for relative 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical scavenging capa

35 n system, when measured according to its 2,2-diphenyl-1-picrylhydrazyl (DPPH) scavenging activity and

36 2,2-Diphenyl-1-picrylhydrazyl (DPPH) scavenging activity of

37 able Sri Lankan fruits were analysed for 2,2-diphenyl-1-picrylhydrazyl (DPPH) scavenging activity, fe

38 Antiglucosidase, 2,2-diphenyl-1-picrylhydrazyl (DPPH) scavenging and ferric r

39 tivity of the films was determined using 2,2-diphenyl-1-picrylhydrazyl (DPPH), and ferric-reducing an

40 sion and their antioxidant activities, a 2,2-diphenyl-1-picrylhydrazyl (DPPH)-guided purification of

41 y and the radical scavenging activity of 2,2-diphenyl-1-picrylhydrazyl (DPPH).

42 cellar exchange of polyphenols using the 2,2-diphenyl-1-picrylhydrazyl (DPPH.) free radical as a visi

43 5)(0)=0.042 mg/ml) demonstrated stronger 2,2-diphenyl-1-picrylhydrazyl DPPH radical-scavenging activi

44 antioxidant scavenging activity against 2,2-diphenyl-1-picrylhydrazyl free radical (DPPH) and 2,2'-a

45 antioxidant potential was determined by 2,2-diphenyl-1-picrylhydrazyl free radical assay and the ele

46 tional approach for the determination of 2,2-diphenyl-1-picrylhydrazyl free radical scavenging activi

47 ested by free radical scavenging against 2,2-diphenyl-1-picrylhydrazyl radical (DPPH) and 2,2'-azino-

48 The reactivity of SO2 with the 2,2-diphenyl-1-picrylhydrazyl radical (DPPH) and in Folin Ci

49 2,2-Diphenyl-1-picrylhydrazyl radical (DPPH) assay was used

50 Antioxidant capacity, determined by 2,2-diphenyl-1-picrylhydrazyl radical scavenging activity (D

51 content and antioxidant activities using 2,2-diphenyl-1-picrylhydrazyl radical scavenging activity an

52 ic acid equivalents/g dry matter and the 2,2-diphenyl-1-picrylhydrazyl radical scavenging activity wa

53 using four in vitro antioxidant assays (2,2-diphenyl-1-picrylhydrazyl radical scavenging activity, r

54 ed by measuring the capacity to scavenge 2,2 diphenyl-1-picrylhydrazyl radicals.

55 xtraction yield, uronic acid content and 2,2-diphenyl-1-picrylhydrazyl scavenging ability (IC50) were

56 ferric reducing antioxidant capacity and 2,2-diphenyl-1-picrylhydrazyl scavenging activity.

57 s vinifera) were studied using the DPPH (2,2-diphenyl-1-picrylhydrazyl) and Folin-Ciocalteu assays.

58 ies were first characterized using DPPH (2,2-diphenyl-1-picrylhydrazyl) and ORAC (oxygen radical abso

59 The antioxidant activity using DPPH (2,2-diphenyl-1-picrylhydrazyl) radical scavenging assay show

60 ic Reducing Ability of Plasma) and DPPH (2,2-Diphenyl-1-Picrylhydrazyl) radical scavenging assays.

61 with a commonly used spectrophotometric (2,2-diphenyl-1-picrylhydrazyl, DPPH) method.

62 aving a p-hydroxyl group showed moderate 2,2-diphenyl-1-picrylhydrazyl-radical-scavenging activity an

63 P) in edible oils and fats using the reagent diphenyl-1-pyrenylphosphine (DPPP) was developed and val

64 2,3-diazatwistpentacene (2, IUPAC name: 9,16-diphenyl-11,14-di(pyridin-2-yl)-1,6-dihydrobenzo[8,9]tri

65 2,3-diazatwistpentacene (3, IUPAC name: 9,16-diphenyl-11,14-di(thien-2-yl)-1,6-dihydrobenzo[8,9]triph

66 positive allosteric modulator 3-cyano-N-(1,3-diphenyl-1H-pyrazol-5-yl) or CDPPB.

67 he systemic administration of 3-Cyano-N-(1,3-diphenyl-1H-pyrazol-5-yl)benzamide (CDPPB) an mGluR5 pos

68 ling protocol between 3-aryl-substituted-1,1-diphenyl-2-azaallyl derivatives and vinyl bromides has b

69 4,4-Diphenyl-2-azabuta-1,3-dienes with two electron-acceptor

70 3,4-Diphenyl-2-azabuta-1,3-dienes, resulting from reaction o

71 For example, (Z)-2,5-diphenyl-2-pentene was produced in 70 % yield with E/Z=5

72 for their ability to reduce free radical 1,1-diphenyl-2-picrihidrazil (DPPH) and for the ability to i

73 nd also other model stable radicals like 1,1-diphenyl-2-picryl-hydazyl, and 2,2'-azinobis3-ethylbenzo

74 papers was evaluated based on scavenging 1,1-diphenyl-2-picryl-hydrazyl (DPPH) and tyrosinase inhibit

75 de (NO) donor, and successfully quenched 1,1-Diphenyl-2-picryl-hydrazyl (DPPH), a stable free radical

76 The 2,2-diphenyl-2-picryl-hydrazyl, pH differential and Folin-Ci

77 ies of the samples were determined using 1,1-diphenyl-2-picrylhydrazyl (DPPH) and reducing power assa

78 phic (HPTLC) method combined with direct 1,1-diphenyl-2-picrylhydrazyl (DPPH) assay to rapidly assess

79 g and the IC50 of the extract, using the 1,1-diphenyl-2-picrylhydrazyl (DPPH) assay, was 57.81 mug/ml

80 The total polyphenol content (TPC) and 1,1-diphenyl-2-picrylhydrazyl (DPPH) differed significantly

81 vitro antioxidant assays, including the 1,1-diphenyl-2-picrylhydrazyl (DPPH) radical method, reducin

82 t the polysaccharides showed interesting 1,1-diphenyl-2-picrylhydrazyl (DPPH) radical-scavenging capa

83 1,1-Diphenyl-2-picrylhydrazyl (DPPH) scavenging ability was

84 MRP obtained by ultrasound exhibited 1,1-diphenyl-2-picrylhydrazyl (DPPH) scavenging activity and

85 the parent molecule was evaluated using 1,1-diphenyl-2-picrylhydrazyl (DPPH), ferric reducing antiox

86 their reaction with the stable radical 2,2'-diphenyl-2-picrylhydrazyl (DPPH).

87 high radical scavenging activities with 1,1-diphenyl-2-picrylhydrazyl and 2,2'-azino-bis(3-ethylbenz

88 Monoterpenes, exhibited low 2,2-diphenyl-2-picrylhydrazyl hydrate (DPPH) and 2,2'-azinob

89 d excellent antioxidant activity such as 1,1-diphenyl-2-picrylhydrazyl radical scavenging activity (I

90 erric reducing antioxidant power), DPPH (1,1-diphenyl-2-picrylhydrazyl radical) and Folin-Ciocalteu a

91 from Tabat cultivar showed higher DPPH (1,1-diphenyl-2-picrylhydrazyl radical) scavenging and ferric

92 Ciocalteu assay, and the traditional DPPH (1-diphenyl-2-picrylhydrazyl) method for antioxidant power

93 Clarity, DPPH (1,1-diphenyl-2-picrylhydrazyl) radical scavenging activity a

94 1,1-Diphenyl-2-pricrylhydrazy (DPPH) radical scavenging acti

95 y used octocrylene (2-ethylhexyl-2-cyano-3,3-diphenyl-2-propenoate, OCT) was frequently found in the

96 a-1,3-dienes, resulting from reaction of 2,3-diphenyl-2H-azirine and diazo compounds, do not produce

97 using MTT (2-(4,5-dimethyl-2-thiazolyl)-3,5-diphenyl-2H-tetrazolium bromide) assay.

98 s extract using standard assays, namely, 1,1-diphenyl-2picrylhydrazyl (DPPH) free radical ability and

99 tuted (+)-(2R,4S)-2-carbomethoxy-4-cyano-2,4-diphenyl-3-pentanone 1.

100 lated germylene complex [PhBP(Ph)3]Ru[CN(2,6-diphenyl-4-MeC6H2)](H)( horizontal lineGeH(t)Bu) (8) was

101 with the benzyl complex [PhBP(Ph)3]Ru[CN(2,6-diphenyl-4-MeC6H2)][eta(1)-CH2(3,5-Me2C6H3)] (7).

102 -pyrido[1,2-a]pyrimidin-4-ones, 1-4, and 2,3-diphenyl-4H-pyrido[1,2-a]pyrimidin-4-ones, 5-7.

103 rate a phosphine oxide XB acceptor and a 1,4-diphenyl-5-iodotriazole XB donor within the same molecul

104 A series of 1,3-diphenyl-6-alkyl/arylfulvenes was prepared, and the elec

105 ing the conjugation at the 6-position of 1,3-diphenyl-6-arylfulvenes increases the reversibility of t

106 ,3-g]phthalazine); 1,4-di(pyridin-2-yl)-6,13-diphenyl-7:8,11:12-bisbenzo-2,3-diazatwistpentacene (2,

107 g]phth alazine); and 1,4-di(thien-2-yl)-6,13-diphenyl-7:8,11:12-bisbenzo-2,3-diazatwistpentacene (3,

108 Furthermore, pirenzepine, diphenyl-acetoxy-N-methyl-piperidine and mecamylamine ha

109 blunted by M1- (pirezenpine; 2 mum) and M3- (diphenyl-acetoxy-N-methyl-piperidine; 100 nm) receptor b

110 ibody, the organocatalyst featuring a chiral diphenyl amino alcohol moiety instead derived its prefer

111 e compounds DMAC (N,N'-dimethyl), DPAC (N,N'-diphenyl), and FlPAC (N-phenyl-N'-fluorenyl) reveal sign

112 scein derivative covalently linked to a 9,10-diphenyl anthracene moiety has been synthesized, and its

113 fords (+)-(2R,3R)-2-carbomethoxy-3-cyano-2,3-diphenyl-butane 2 with two adjacent stereogenic, all-car

114 nate metathesis reaction with 4,4'-methylene diphenyl diisocyanate (4,4'-MDI) circumvents harsh react

115 cies, industrial MDA mixtures, and methylene diphenyl diisocyanate (MDI) mixtures used in polyurethan

116 e MDA, multimeric MDA species, and methylene diphenyl diisocyanate (MDI) mixtures.

117 MDA is a precursor to methylene diphenyl diisocyanate (MDI), a hard block component in p

118 With diphenyl diselenide (PhSeSePh) (5 mol%) as the pre-catal

119 ried out by (77)Se NMR spectroscopy by using diphenyl diselenide as the substrate.

120 esters synthesis from several anhydrides and diphenyl diselenide was developed.

121 ls included the dialkyl/diphenyl disulfides, diphenyl diselenide, and 1-octadecanethiol, but not t-bu

122 ng di-n-butyl disulfide, diphenyl disulfide, diphenyl diselenide, di-n-butyl sulfide, diphenyl seleni

123 ion in the presence of a catalytic amount of diphenyl diselenide.

124 Additionally, we present evidence that diphenyl disulfide ((PhS)2) operates on a common catalyt

125 temperature, including di-n-butyl disulfide, diphenyl disulfide, diphenyl diselenide, di-n-butyl sulf

126 yl peroxide, heptafluoroisopropyl iodide and diphenyl disulfide.

127 urface silicon radicals included the dialkyl/diphenyl disulfides, diphenyl diselenide, and 1-octadeca

128 eld-effect transistor applications including diphenyl-DPP and dithienyl-DPP-based polymers as the mos

129 ometry to measure 10 tri- to heptabrominated diphenyl eithers in serum samples.

130 Stilbenes are diphenyl ethene compounds produced naturally in a wide v

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

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

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

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

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

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

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

138 47 targeted FRs, including 12 polybrominated diphenyl ether (PBDE) congeners, 19 other brominated FRs

139 Polybrominated diphenyl ether (PBDE) flame retardants are environmental

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

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

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

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

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

145 6-3.27; P = .001), and 1 BFR (polybrominated diphenyl ether 47: OR = 2.69; 95% CI, 1.49-4.85; P = .00

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

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

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

149 Polybrominated diphenyl ether exposure and thyroid function tests in No

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

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

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

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

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

155 tes a suitable alternative to decabrominated diphenyl ether.

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

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

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

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

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

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

162 Polybrominated diphenyl ethers (PBDEs) alter thyroid hormone homeostasi

163 Polybrominated diphenyl ethers (PBDEs) and alternative flame retardants

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

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

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

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

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

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

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

171 Polybrominated diphenyl ethers (PBDEs) are bioaccumulating flame retard

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

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

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

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

176 Polybrominated diphenyl ethers (PBDEs) are lipophilic flame retardants

177 Polybrominated diphenyl ethers (PBDEs) are persistent and bioaccumulati

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

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

180 Polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental con

181 Polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental pol

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

247 e a replacement of the banned polybrominated diphenyl ethers.

248 polybrominated biphenyls and polybrominated diphenyl ethers.

249 tetrachloroethylene, and the polybrominated diphenyl ethers.

250 chlorinated naphthalenes, and polybrominated diphenyl ethers.

251 Interaction of 4,5-dimethyl-2-(2-oxo-1,2-diphenyl)ethoxy-1,3,2-dioxaphospholane, bearing a carbox

252 C(4)-gem-dimethyl group and four a C(4)-gem-diphenyl group adjacent to the C(5)-isopropyl substituen

253 nylnaphthopyran and its analog, in which the diphenyl groups are fused in the form of fluorene, allow

254 tion, but not by an NADPH oxidase inhibitor, diphenyl iodonium chloride, which inhibits ABA-dependent

255 yzed racemization processes in atropisomeric diphenyl-like frameworks are classically described as th

256 zation of 2,5-bis[(alpha-hydroxy-alpha,alpha-diphenyl)methyl]tellurophene with a diketopyrrolopyrrole

257 Diphenyl methylphosphonate causes peroxisome clustering

258 n stable radicals, such as verdazyls and N,N-diphenyl-N'-picrylhydrazyl, and even rivaling the intrin

259 The lipophilic antioxidant N,N'-diphenyl-p-phenylenediamine protected TLF-1-treated T. b

260 l phosphate (2IPPDPP), 2,4-diisopropylphenyl diphenyl phosphate (24DIPPDPP), and bis(2-isopropylpheny

261 and the ITP mixture, with 2-isopropylphenyl diphenyl phosphate (2IPPDPP), 2,4-diisopropylphenyl diph

262 ,3-dichloro-2-propyl) phosphate (BDCIPP) and diphenyl phosphate (DPHP)) were most commonly detected (

263 ), bis(1-chloro-2-propyl) phosphate (BCIPP), diphenyl phosphate (DPHP), 2 alkylated DPHPs, and TBBA i

264 s(1,3-dichloro-2-propyl) phosphate (BDCIPP), diphenyl phosphate (DPHP), isopropylphenyl phenyl phosph

265 s(1,3-dichloropropyl) phosphate (BDCIPP) and diphenyl phosphate (DPHP), metabolites of TDCIPP and TPH

266 e in the formation of the hydrolysis product diphenyl phosphate (DPHP), the seemingly most abundant i

267 d its primary metabolite is considered to be diphenyl phosphate (DPHP).

268 triphenyl phosphate (TPHP), and 2-ethylhexyl diphenyl phosphate (EHDP).

269 triphenyl phosphate (TPHP) and 2-ethylhexyl diphenyl phosphate (EHDPHP), are emerging contaminants t

270 ged from 0.01 mg/day/person for 2-ethylhexyl diphenyl phosphate (EHDPP) to 5.12 mg/day/person for TCI

271 ri-n-butyl phosphate (TnBP) and 2-ethylhexyl-diphenyl phosphate (EHDPP) were the most abundant OPE co

272 e atmospheric concentrations of 2-ethylhexyl diphenyl phosphate (EHDPP; 610 +/- 220 pg m(-3)) measure

273 in yields of 60-95% by reduction of derived diphenyl phosphate esters with lithium triethylborohydri

274 trobin, dibutyl phthalate, tert-butyl-phenyl diphenyl phosphate, and the isopropylated triaryl phosph

275 ving rise to a variety of compounds, such as diphenyl phosphate, para-hydroxy-triphenyl phosphate, an

276 ed by the selective Kv 1.5 channel inhibitor diphenyl phosphine oxide-1 but unaffected by the presenc

277 tive identification of the nonmutagen benzyl(diphenyl) phosphine oxide in a mutagenic fraction.

278 sed strategy for the direct determination of diphenyl phthalate (DPP) in food and biological samples

279 +/-0.00-155.16+/-0.98mg/100g of TPC, 50% 2,2-diphenyl picryl hydrazyl (DPPH) inhibition, 7.36+/-0.43-

280 f the antioxidant properties using the DPPH (diphenyl picryl hydrazyl) assay method shows the pyrrole

281 the tea products was determined using a 2,2'-diphenyl picrylhydrazyl (DPPH) radical assay method.

282 g from the previously identified 3-cyano-4,6-diphenyl-pyridines, we chemically modified this scaffold

283 ine intermediates from 1-alkynes, chiral (S)-diphenyl(pyrrolidin-2-yl)methanol, and propiolates gave

284 trophilic aromatic substitution of the ortho-diphenyl ring.

285 Halogen substitution of the diphenyl rings of (+/-)-1 gave several amide analogues w

286 of (+/-)-1 were synthesized wherein (1) the diphenyl rings were substituted with methyl, trifluorome

287 de, diphenyl diselenide, di-n-butyl sulfide, diphenyl selenide, diphenyl sulfide, 1-octadecanethiol,

288 The 5,5-diphenyl substitution associated with a benzylaminomethy

289 On the other hand, triplet state of diphenyl sulfide also showed competitive C-S bond cleava

290 The direct irradiation of diphenyl sulfide and p-substituted thioanisoles in the p

291 otection produced by some small molecules, a diphenyl sulfide compound was revealed to be a new phosp

292 iving phenyl sulfinic acid and ionization to diphenyl sulfide radical cation that in turn led to diph

293 nide, di-n-butyl sulfide, diphenyl selenide, diphenyl sulfide, 1-octadecanethiol, t-butyl disulfide,

294 and 1-octadecanethiol, but not t-butylthiol, diphenyl sulfide/selenide, and di-n-butyl sulfide.

295 the basis of these data, a diverse family of diphenyl sulfides has been developed and pharmacological

296 l sulfide radical cation that in turn led to diphenyl sulfoxide.

297 Comparison to the redox-inactive diphenyl tetrazine ligand as a control experiment illust

298 videnced by 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyl tetrazolium bromide (MTT) assay, lactate dehydr

299 rypan blue, 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyl-tetrazolium bromide (MTT), and apoptosis assays

300 health, the 3-(4,5-dimethythiazol-2-yl)-2,5-diphenyl-tetrazolium-bromide cell viability assay, the l