ライフサイエンスコーパス: diphenyl

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

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

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

4 , [Ru(DIP)(2)(sq)](PF(6)) (Ru-sq) (DIP = 4,7-diphenyl-1,10-phenanthroline; sq = semiquinonate ligand)

5 ly, Ru-sq ([Ru(DIP)(2)(sq)](PF(6)) (DIP, 4,7-diphenyl-1,10-phenanthroline; sq, semiquinonate ligand),

6 t monocyclic aromatic 1,2,3,5-tetrazine, 4,6-diphenyl-1,2,3,5-tetrazine.

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

8 ivity comparable to that of the isomeric 3,6-diphenyl-1,2,4,5-tetrazine, display a single mode of cyc

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

10 ocuses on a series of carbazole-(C=C)(n)-2,5-diphenyl-1,3,4-oxadiazoles (n = 1-4) as conjugated pai-s

11 1,6-Diphenyl-1,3,5-hexatriene (DPH) is a commonly used fluor

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

13 ,6-bis(pyridyl)-1,2,4,5-tetrazine; dbm = 1,3-diphenyl-1,3-propanedionate) is reported.

14 ee and bound phenolic contents and DPPH (2,2-diphenyl-1- picrylhydrazyl) radical scavenging activity

15 Mechanistic studies reveal that 3,4-diphenyl-1-methylisoquinoline is an active intermediate

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

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

18 results are corroborated by an increased 2,2-diphenyl-1-picryl hydrazyl (DPPH) scavenging activity, t

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

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

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

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

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

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

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

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

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

28 lbenzthiazoline-6-sulfonic acid) (ABTS), 2,2-diphenyl-1-picrylhydrazyl (DPPH) and nitric oxide assays

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

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

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

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

33 metry/Mass Spectrometry (HPLC-MS/MS) and 2,2-diphenyl-1-picrylhydrazyl (DPPH) free radical scavenging

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

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

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

37 ethanolic peel extract exhibited a high 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical scavenging acti

38 used to estimate antioxidant activity by 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical scavenging acti

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

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

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

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

43 power, and used this concept to develop 2,2-diphenyl-1-picrylhydrazyl (DPPH), 2,2'-azino-bis(3-ethyl

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

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

46 of preparative thin layer chromatography-2,2-diphenyl-1-picrylhydrazyl (PTLC-DPPH) bioautography tech

47 Antioxidant activities evaluated using 2,2-diphenyl-1-picrylhydrazyl and 2,2'-azino-bis (3-ethylben

48 ivity and increased in proline content, 2, 2-diphenyl-1-picrylhydrazyl antioxidant activities and fer

49 5)(0)=0.042 mg/ml) demonstrated stronger 2,2-diphenyl-1-picrylhydrazyl DPPH radical-scavenging activi

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

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

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

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

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

55 wing antioxidants were studied using the 2,2-diphenyl-1-picrylhydrazyl radical (DPPH) assay: butylate

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

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

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

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

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

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

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

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

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

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

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

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

68 With this aim, thiocyanate and DPPP (diphenyl-1-pyrenylphosphine) fluorescence methods were c

69 loaddition of 3-(6-ethynyl-pyridin-2-yl)-5,6-diphenyl-[1,2,4]triazine dipolarophiles with structurall

70 uction of 1,3-bis(2,6-diisopropylphenyl)-2,4-diphenyl-1H-imidazol-3-ium chloride (1) resulted in the

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

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

73 4,4-Diphenyl-2-azabuta-1,3-dienes with two electron-acceptor

74 3,4-Diphenyl-2-azabuta-1,3-dienes, resulting from reaction o

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

76 by formal elimination of ethanol yields 3,5-diphenyl-2-phosphafuran (DPF) in 43% yield.

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

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

79 er hand, proline content and antioxidant 1,1-diphenyl-2-picryl-hydrazyl (DPPH) radical scavenging act

80 ro peroxidation and reducing assays: (i) 1,1-diphenyl-2-picryl-hydrazyl free radical (DPPH) scavengin

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

82 From the results of the 1,1-diphenyl-2-picrylhydrazyl (DPPH(*)) and 2,2'-azinobis (3

83 8 mg GAE/g), antioxidant activity in the 1,1-diphenyl-2-picrylhydrazyl (DPPH) (8.90 mumol TEAC/g) and

84 dical scavenging effect in vitro against 1,1-diphenyl-2-picrylhydrazyl (DPPH) and 2,2'-Azino-bis (3-e

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

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

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

88 Through Folin-Ciocalteau and 1,1-diphenyl-2-picrylhydrazyl (DPPH) colorimetric assays, GB

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

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

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

92 ties, Gl-L and Gd-L exhibited comparable 1,1-diphenyl-2-picrylhydrazyl and hydroxyl radical-scavengin

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

94 was analyzed using the following tests: 1-1-diphenyl-2-picrylhydrazyl radical (DPPH), 2,2'-azinobis-

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

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

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

98 ydrogen peroxide, nitric oxide and DPPH (1,1-diphenyl-2-picrylhydrazyl), and inhibition of 5-LOX, COX

99 1,1-Diphenyl-2-pricrylhydrazy (DPPH) radical scavenging acti

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

101 ndex SI for 3-(4,5-dimethyl-2-thiazolyl)-2,5-diphenyl-2H-tetrazolium bromide (MTT) assay, >28.90 to 1

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

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

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

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

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

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

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

109 let energy differences (DeltaE(ST) ) in 9,9'-diphenyl-9H,9'H-3,3'-bicarbazole (BCzPh):3',3'",3'""-(1,

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

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

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

113 rward and scalable methodology to synthesize diphenyl arylphosphonates at 20 degrees C within 1-2 h i

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

115 varying the molar ratio of beta-cyclodextrin:diphenyl carbonate (beta-CD:DPC; 1:2, 1:6 and 1:10).

116 ystallinity of NS was enhanced by increasing diphenyl carbonate concentration.

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

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

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

120 ssed with a 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyl diphenyltetrazolium bromide (MTT) assay and a l

121 Among all the tested species, diphenyl diselenide based materials appear to be the mos

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

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

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

125 ds with aryl and alkyl disulfides as well as diphenyl diselenide.

126 rs needed for the diselenide exchange, makes diphenyl diselenides ideal for self-healing materials.

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

128 yl peroxide, heptafluoroisopropyl iodide and diphenyl disulfide.

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

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

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

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

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

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

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

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

137 47 targeted FRs, including 12 polybrominated diphenyl ether (PBDE) congeners, 19 other brominated FRs

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

139 Polybrominated diphenyl ether (PBDE) flame retardants are environmental

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

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

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

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

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

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

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

147 6-3.27; P = .001), and 1 BFR (polybrominated diphenyl ether 47: OR = 2.69; 95% CI, 1.49-4.85; P = .00

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

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

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

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

152 Polybrominated diphenyl ether exposure and thyroid function tests in No

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

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

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

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

157 tes a suitable alternative to decabrominated diphenyl ether.

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

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

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

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

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

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

164 Polybrominated diphenyl ethers (PBDEs) alter thyroid hormone homeostasi

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

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

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

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

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

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

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

172 Polybrominated diphenyl ethers (PBDEs) are bioaccumulating flame retard

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

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

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

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

177 Polybrominated diphenyl ethers (PBDEs) are lipophilic flame retardants

178 Polybrominated diphenyl ethers (PBDEs) are persistent and bioaccumulati

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

180 Polybrominated diphenyl ethers (PBDEs) are ubiquitous environmental con

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

243 henyls, organophosphates, and polybrominated diphenyl ethers.

244 chlorinated naphthalenes, and polybrominated diphenyl ethers.

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

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

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

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

249 z consists of a mainchain backbone where the diphenyl groups localize at the 9-position as steric bul

250 of one or more CSBM per week from baseline, diphenyl methane laxatives at a dose of 10 mg once daily

251 el movements (CSBMs) per week, the stimulant diphenyl methane laxatives bisacodyl and sodium picosulf

252 Although diphenyl methane laxatives ranked first at 4 weeks, pati

253 a,j]phenazine) and two electron-donors (N,N'-diphenyl-p-phenyelendiamine) has been rationally designe

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

255 2) = 2,2'-dimercapto-3,3'-bis(trimethylsilyl)diphenyl)phenylphosphine; H is a dissociable proton) wit

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

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

258 Diphenyl phosphate (DPHP) is an aryl phosphate ester (AP

259 (2-ethylhexyl diphenyl phosphate (EHDP) and diphenyl phosphate (DPhP)) coated on (NH(4))(2)SO(4) par

260 ,3-dichloro-2-propyl) phosphate (BDCIPP) and diphenyl phosphate (DPHP)) were most commonly detected (

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

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

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

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

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

266 logical evolution of two OPFRs (2-ethylhexyl diphenyl phosphate (EHDP) and diphenyl phosphate (DPhP))

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

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

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

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

271 mbination of triphenylphosphine selenide and diphenyl phosphate as a catalyst, a wide range of unsatu

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

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

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

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

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

277 an expensive small molecule such as 2,8-bis(diphenyl-phosphoryl)dibenzo[b,d]thiophene (PPT) as the a

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

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

280 fonatocalix[4]arene (SC4AD) and naphthyl-1,8-diphenyl pyridinium derivative (NPS) as a light-harvesti

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

282 trophilic aromatic substitution of the ortho-diphenyl ring.

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

284 f a glycosyl phosphate with 6- O- tert-butyl diphenyl silyl group and a d-glucuronic acid-containing

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

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

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

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

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

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

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

292 to the free luminophore, which involves the diphenyl sulfone moiety.

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

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

295 zoles, 2-methyl-5-phenyl-tetrazoles, and 2,5-diphenyl-tetrazoles follow similar trends and are explic

296 utes, and a 3-[4,5-dimethylthiazol-2-yl]-2,5 diphenyl tetrazolium bromide (MTT) assay with photoabsor

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

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

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

300 A diphenyl trisulfide-selenium nanowire (DPTS-Se) organic-