ライフサイエンスコーパス: organochlorine

1 udies for phthalate esters and 4 studies for organochlorines).

2 has an E(o)' value similar to that of other organochlorines.

3 ive of inputs and aquatic responses to these organochlorines.

4 ysis for the assessment of global cycling of organochlorines.

5 ociation between the agricultural use of the organochlorine 1,1,1-trichloro-2,2'bis(p-chlorophenyl)et

6 influence of weather or climate variables on organochlorine accumulation in Arctic wildlife, includin

7 ndicate that dieldrin and binary mixtures of organochlorines affect [Ca(2+)](i) already at concentrat

8 n spectroscopy to measure total non-volatile organochlorine and -bromine in five edible brown seaweed

9 -term changes in plasma concentrations of 20 organochlorine and 16 perfluoroalkyl pollutants in king

10 creased residues of common organophosphorus, organochlorine and carbamate pesticides by 30-70% on tom

11 that the literature suggests a link between organochlorine and in-utero pesticide exposure and impai

12 l and health externalities of the increasing organochlorine and organophosphate insecticide use in th

13 The observed association of organochlorine and organophosphate insecticides with dia

14 handling certain pesticides, in particular, organochlorine and organophosphate insecticides, may be

15 lopment with a focus on in-utero exposure to organochlorine and organophosphate pesticides.

16 romatic ions (PS), phthalate ions (PET), and organochlorine and polycyclic aromatic hydrocarbons ions

17 We previously reported associations between organochlorines and behaviors related to attention defic

18 ted after adjusting for prenatal exposure to organochlorines and metals but were no longer significan

19 s such as prenatal environmental exposure to organochlorines and metals, social risk factors, and gen

20 c effects should be considered in studies of organochlorines and neurodevelopment.

21 considerable interest in a possible role of organochlorines and polychlorinated biphenyls in the eti

22 ss-sectional association between ever use of organochlorines and risk of hypothyroidism and hyperthyr

23 We investigated PCBs and other organochlorines and risk of non-Hodgkin's lymphoma in a

24 ts) or chemical structure (organophosphates, organochlorines, and carbamates) with eye disorders were

25 ll 4 major classes (pyrethroids, carbamates, organochlorines, and organophosphates) of public health

26 Organochlorines are environmentally persistent contamina

27 , supplementary food did not alleviate their organochlorine burden.

28 or that dechlorination of naturally produced organochlorines can neutralize delta(37)Cl shifts caused

29 Specifically, ever use of the organochlorine chlordane (OR(adj) = 1.3 (95% CI: 0.99, 1

30 yls (PCBs) and other industrial or byproduct organochlorines (chlorobenzenes, pentachloroanisole, oct

31 h between inorganic chloride (Cl(inorg)) and organochlorine (Cl(org)), as well as between aliphatic C

32 ndly affect the toxicokinetics of lipophilic organochlorine compound (OC) burdens.

33 tion on the mechanisms through which another organochlorine compound, beta-hexachlorocyclohexane (bet

34 epleted than all known industrially produced organochlorine compounds (delta(37)Cl = -7 to +6 per tho

35 sistent organic pollutants (POPs), including organochlorine compounds (OCs) and perfluoroalkyl and po

36 ion between the combined exposure to several organochlorine compounds and composite CVD.

37 ts derived from high exposures to individual organochlorine compounds are well documented.

38 biphenyl 153 (rho = -0.016), the other main organochlorine compounds detected.

39 Our results suggest higher levels of some organochlorine compounds during pregnancy are associated

40 hlorine isotopic signatures (delta(37)Cl) of organochlorine compounds has been suggested as a tool to

41 e on low but continuous exposure to combined organochlorine compounds in the general population.

42 1.11-2.64) per 1-quartile increment of total organochlorine compounds mixture.

43 Organochlorine compounds such as o,p'-DDT and beta-HCH a

44 A total of 25 organochlorine compounds were measured in blood at basel

45 Higher blood concentrations of organochlorine compounds were not associated with increa

46 hlorodiphenyltrichloroethane (DDT) and other organochlorine compounds, are abundant in the environmen

47 S, OPEs, PAHs, polychlorinated biphenyls and organochlorine compounds, polybromodiphenyl ethers, and

48 relation of diabetes with POPs occurred with organochlorine compounds, such as trans-nonachlor, dichl

49 n the range of those previously measured for organochlorine compounds.

50 e knowledge regarding natural attenuation of organochlorine compounds.

51 of dietary sources and maternal transfer on organochlorine concentrations ( summation operatorOCs) i

52 A longitudinal study of peripubertal serum organochlorine concentrations and semen parameters in yo

53 physiological variables and lipid-normalized organochlorine concentrations distinguished amphipods fr

54 Organochlorine concentrations range from 120 to 630 mg.k

55 We examined organochlorine contaminant (OC) concentrations in the bl

56 ed and wild salmon from around the world for organochlorine contaminants, we show that concentrations

57 class pesticides comprising ESI-amenable and organochlorine contaminants.

58 literature, which suggests that exposure to organochlorines contributes to non-Hodgkin's lymphoma ri

59 Among the organochlorines detected were monochlorinated, e.g., chl

60 The organochlorine dichlorodiphenyltrichloroethane (DDT), a

61 nsecticides (chlorpyrifos, diazinon) with an organochlorine (dieldrin) and a metal (Ni(2+)) for simil

62 rganophosphates (chlorpyrifos, diazinon), an organochlorine (dieldrin) and a metal (Ni(2+)) for their

63 rganophosphates (chlorpyrifos, diazinon), an organochlorine (dieldrin) and a metal (Ni(2+)); we utili

64 ty in the data was associated with declining organochlorine emissions (up to 70.2% for murres and 77.

65 Aliphatic organochlorine exceeds aliphatic organobromine but is po

66 rt an association between low-level prenatal organochlorine exposure and ADHD-like behaviors in child

67 This shows that the relation between organochlorine exposure and NHL risk may be modified by

68 ow clear evidence for an association between organochlorine exposure and obesity; however, a suggesti

69 re used to estimate the relationship between organochlorine exposure and sperm disomy outcomes.

70 mmon, and evidence of an association between organochlorine exposure and thyroid disease is increasin

71 Organochlorine exposure was linked to non-Hodgkin lympho

72 Overweight and BMI were unrelated to organochlorine exposure.

73 Organochlorine exposures measured at age 14 and in adult

74 slands, a population with a known history of organochlorine exposures.

75 Furthermore, the delta(37)Cl in bulk organochlorines extracted from boreal forest soils were

76 37)Cl values of FDH products as well of bulk organochlorines extracted from pristine forest soil for

77 experiments demonstrated that the release of organochlorines from Lake Strawbridge sediments was main

78 ter group (OR = 1.52; 95% CI: 1.09-1.95) and organochlorine group (OR = 1.98; 95% CI: 1.34-2.62).

79 study, participants with higher exposures to organochlorines had an increased probability of experien

80 und support for indirect negative effects of organochlorines, highly toxic pollutants to seabirds, on

81 useful to understand sources and cycling of organochlorines in nature.

82 xposure to "environmental estrogens" such as organochlorines in pesticides and industrial chemicals h

83 Observations of organochlorines in the gas and particle phases reflect t

84 Hodgkin lymphoma and body burden of selected organochlorines in the general population in a nested ca

85 sticides in the positive mode and 80% of the organochlorines in the negative mode.

86 (an integrated functional measure of several organochlorines) in plasma, and alpha-chlordane (dust me

87 These data support a role of organochlorines, in addition to fungicides, in the etiol

88 ntrations of DDT, its metabolites, and other organochlorines, including polychlorinated biphenyls (PC

89 The organochlorine insecticide aldrin was also associated wi

90 er 143-50-0) has been used extensively as an organochlorine insecticide but is nowadays banned under

91 t CYP6M2 is also capable of metabolizing the organochlorine insecticide DDT in the presence of solubi

92 Parkinson's disease (PD); in particular, the organochlorine insecticide dieldrin is believed to be as

93 -trichlorophenoxy)acetic acid (2,4,5-T); the organochlorine insecticide dieldrin; and the organophosp

94 2-bis(p-chlorophenyl)ethane (DDT), the first organochlorine insecticide, and pyrethroid insecticides

95 ench West Indies, chlordecone (CLD), a toxic organochlorine insecticide, was extensively applied to b

96 ased odds of hypothyroidism with ever use of organochlorine insecticides (adjusted odds ratio (OR(adj

97 in the highest exposed HPEEs, including two organochlorine insecticides (DDT and lindane) and four h

98 Applicators who had used the organochlorine insecticides aldrin, chlordane, and hepta

99 Extraction efficiency of PFE for nonpolar organochlorine insecticides and slightly polar triazine

100 -use of two pesticide classes, fumigants and organochlorine insecticides, and seven individual pestic

101 In H4IIEcells, four organochlorine insecticides, bifenthrin, and 3-PBA decre

102 Toxicants such as organochlorine insecticides, lead ammunition, and veteri

103 for pyrethroids than for organophosphorus or organochlorine insecticides, which suggests that the FOC

104 l gene (Vgsc), target-site of pyrethroid and organochlorine insecticides.

105 t before DDT use, suggesting that a regional organochlorine legacy may exist in the modern food webs

106 Higher organochlorine levels appear in samples with more lipid

107 spiny lobster and crayfish samples, several organochlorines linked to chlordecone have been annotate

108 cused on suspect screening from a list of 26 organochlorines linked to chlordecone, and non-targeted

109 These results support an association between organochlorines (mainly PCBs) and neuropsychological mea

110 Organochlorine molecules (Clorg) are surprisingly abunda

111 n with relatively high levels of exposure to organochlorines, no clear associations with obesity or B

112 g methodologies for new and newly discovered organochlorines not included in databases have been deve

113 Concentrations of several organochlorine (OC) compounds were determined for glauco

114 e assessed the association between childhood organochlorine (OC) exposure and adult semen parameters.

115 Organochlorine (OC) insecticides and polychlorinated bip

116 vironmental exposure of humans to persistent organochlorine (OC) insecticides lindane (HCH) and dield

117 Organochlorine (OC) pesticides and the more persistent p

118 Organochlorine (OC) pesticides pose a significant enviro

119 persistent organic pollutants (POPs: legacy organochlorines [OCs], polybrominated diphenyl ethers [P

120 fidence interval: 1.02, 2.59) and a group of organochlorines (odds ratio = 1.64, 95% confidence inter

121 elated behaviors and assess whether prenatal organochlorine or metal exposures, sociodemographic fact

122 AMD was associated with ever use of organochlorine [OR=2.7 (95% CI: 1.8, 4.0)] and organopho

123 In addition, the presence of carbamates, organochlorines, organophosphates and triazines were als

124 s, dibenzofurans, polychlorinated biphenyls, organochlorines, organophosphates, phenols, metals, and

125 ination of 35 multiclass pesticide residues (organochlorine, organophosphorus and synthetic pyrethroi

126 ion of French West Indies (FWI) soils by the organochlorine pesticide chlordecone poses environmental

127 Polychlorinated biphenyl and organochlorine pesticide concentrations in maternal mid-

128 Recent studies on in-utero exposure to the organochlorine pesticide dichlorodiphenyltrichloroethane

129 f data on the amount and distribution of the organochlorine pesticide dichlorodiphenyltrichloroethane

130 We report measurements of organochlorine pesticide diffusion and partition coeffic

131 the tropical Atlantic Ocean, neither PCB nor organochlorine pesticide dissolved concentrations varied

132 as developed for detection of the persistent organochlorine pesticide gamma-hexachlorocyclohexane (ga

133 ionnaire concerning factors affecting plasma organochlorine pesticide levels and the immune system.

134 e (AIBN) as the initiator and gamma-HCCH, an organochlorine pesticide molecule, as the template.

135 ng multivariate approach for the analysis of organochlorine pesticide residues in 6 varieties of bean

136 The estrogenic action of some persistent organochlorine pesticide residues may play a role in the

137 and coaxial systems were determined using 16 organochlorine pesticide solutions separated by gas chro

138 Chlordecone is an organochlorine pesticide that has been extensively used

139 hloroethane (DDT) is a persistent estrogenic organochlorine pesticide that is a rodent hepatic tumor

140 Chlordecone is an organochlorine pesticide that was extensively used in th

141 Endosulfan is a persistent organochlorine pesticide that was globally distributed b

142 results suggest that the temporal pattern of organochlorine pesticide use strongly influenced Peregri

143 nd relative to the spatiotemporal pattern of organochlorine pesticide use.

144 wild-type ERalpha, recognized toxaphene (an organochlorine pesticide) as an agonist.

145 95% credible interval [CrI], 0.30 to 0.59), organochlorine pesticides (beta = 0.22; 95% CrI, 0.15 to

146 valuated the impact of childhood exposure to organochlorine pesticides (OCP) on pubertal development.

147 as analyzed for atmospheric deposition of 36 organochlorine pesticides (OCPs) and 7 industrial compou

148 The Arctic has been contaminated by legacy organochlorine pesticides (OCPs) and currently used pest

149 Organochlorine pesticides (OCPs) and polychlorinated bip

150 ed persistent organic pollutants, especially organochlorine pesticides (OCPs) and polychlorinated bip

151 and 2014 show different trends for different organochlorine pesticides (OCPs) and polychlorinated bip

152 of the occurrence and distribution of legacy organochlorine pesticides (OCPs) and the current use pes

153 and sources of gaseous and freely dissolved organochlorine pesticides (OCPs) and their air-water exc

154 Polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) are neurodevelopmental

155 polycyclic aromatic hydrocarbons (PAHs), and organochlorine pesticides (OCPs) by equilibrating 13 sil

156 Polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) concentrations in snow

157 d use change on the potential re-emission of organochlorine pesticides (OCPs) from background and agr

158 Organochlorine pesticides (OCPs) have been linked to adu

159 , the volatility and degradation of BFRs and organochlorine pesticides (OCPs) in soil was investigate

160 legacy polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) was undertaken in the C

161 , snow, sea-ice, and seawater for a range of organochlorine pesticides (OCPs) was undertaken through

162 such as polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) were also analyzed for

163 ), 14 non-BDE flame retardants (FRs), and 25 organochlorine pesticides (OCPs) were analyzed in air sa

164 Organochlorine pesticides (OCPs) were measured in the su

165 Polychlorinated biphenyls (PCBs) and organochlorine pesticides (OCPs) were measured in Wester

166 Limited human data suggest an association of organochlorine pesticides (OCPs) with adverse effects on

167 Here, we investigated the occurrence of 21 organochlorine pesticides (OCPs), 14 current use pestici

168 Atmospheric levels of 22 organochlorine pesticides (OCPs), 45 polychlorinated bip

169 f selected polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), and brominated flame r

170 s (PBDEs), polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), and lipids.

171 Bs), polybrominated diphenyl ethers (PBDEs), organochlorine pesticides (OCPs), and per- and polyfluor

172 nes, pentachloroanisole, octachlorostyrene), organochlorine pesticides (OCPs), and polybrominated dip

173 ns (PAHs), polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), and polybrominated dip

174 Bs), polybrominated diphenyl ethers (PBDEs), organochlorine pesticides (OCPs), and polycyclic aromati

175 ls that exhibit hormonal properties, such as organochlorine pesticides (OCPs), may affect endometrios

176 ollutants (polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), polybrominated dipheny

177 including polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), polybrominated dipheny

178 rsistent environmental pollutants, including organochlorine pesticides (OCPs), polychlorinated biphen

179 PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs).

180 l (PCP), polybrominated diphenyl ethers, and organochlorine pesticides (OCPs).

181 of 22 polychlorinated biphenyls and 7 of 10 organochlorine pesticides (OCPs).

182 polybrominated diphenyl ethers (PBDEs), and organochlorine pesticides (OCPs).

183 y per exposure-mixture quartile increase for organochlorine pesticides (odds ratio [OR], 1.44 [95% cr

184 BDEs], polychlorinated biphenyls [PCBs], and organochlorine pesticides [OCPs]) in 101 Southern Califo

185 In this work, we report the detection of the organochlorine pesticides aldrin, dieldrin, lindane, and

186 ols to allow trace determination of selected organochlorine pesticides and hormones by gas chromatogr

187 Laboratory release experiments on the organochlorine pesticides DDT, DDE, DDD, and chlordane i

188 lines globally following the introduction of organochlorine pesticides during the late 1940s and 1950

189 n of dieldrin, our data shows PCBs and other organochlorine pesticides have remained stable or increa

190 Tissue distribution patterns of organochlorine pesticides in bovine carcasses varied sig

191 eduction and then complete ban on the use of organochlorine pesticides in the UK.

192 isphere air, concentrations of HCB and other organochlorine pesticides increased several-fold.

193 also did not respond to other commonly used organochlorine pesticides like DDT and DDE.

194 (DLLME) protocol for the determination of 15 organochlorine pesticides residues in honey is proposed.

195 was applied to the analysis of the selected organochlorine pesticides residues in various honey samp

196 er and human population density while legacy organochlorine pesticides such as p,p'-DDE, lindane, and

197 analysis of analytes ranging from non-polar organochlorine pesticides to polar drugs, including peni

198 2-tk-CAT and mouse PXR demonstrated that the organochlorine pesticides transnonachlor and chlordane a

199 wo polychlorinated biphenyls (PCBs), and two organochlorine pesticides using gas chromatography-mass

200 pothesis that reproductive failure caused by organochlorine pesticides was an important driver of the

201 s, seven polychlorinated biphenyls and eight organochlorine pesticides were investigated.

202 sensitivity of SERS for the detection of the organochlorine pesticides with a limit of detection reac

203 ts suggest that toxaphene and chlordane, two organochlorine pesticides with estrogen-like activity, b

204 , di-2(ethylhexyl)phthalate, and some legacy organochlorine pesticides) approach or exceed HQ values

205 il-air values for pesticides (other than the organochlorine pesticides) have not been robustly develo

206 polybrominated diphenyl ethers (PBDEs), and organochlorine pesticides) to comprehensively assess the

207 Parental serum concentrations of 9 organochlorine pesticides, 1 polybrominated biphenyl (PB

208 ded biospecimens for the quantification of 9 organochlorine pesticides, 1 polybrominated biphenyl, 10

209 Nine metals, 3 organochlorine pesticides, 5 polychlorinated biphenyls,

210 Three organochlorine pesticides, 5 polychlorinated biphenyls,

211 ol A, 25 polychlorinated biphenyls (PCBs), 6 organochlorine pesticides, 8 brominated flame retardants

212 ndescribed in vivo evidence that a subset of organochlorine pesticides, agrichemicals, and environmen

213 levels of polychlorinated biphenyls (PCBs), organochlorine pesticides, and flame retardants in Weste

214 Polychlorinated biphenyls (PCBs), organochlorine pesticides, and methylmercury (MeHg) are

215 as well as polychlorinated biphenyls (PCBs), organochlorine pesticides, and polyaromatic hydrocarbons

216 rations of summed polychlorinated biphenyls, organochlorine pesticides, and polybrominated diphenyl e

217 triclosan (MTCS), polychlorinated biphenyls, organochlorine pesticides, and polycyclic aromatic hydro

218 AD-2 resin adsorption and analyzed for PCBs, organochlorine pesticides, PAHs, polybrominated diphenyl

219 e, PCB-44, PCB-52, PCB-153, PCB-180, several organochlorine pesticides, PBDE-10, PBDE-28, PBDE-116, m

220 Metals, legacy organochlorine pesticides, PCBs, and contaminants of eme

221 of seven food groups and the blood levels of organochlorine pesticides, polybrominated diphenyl ether

222 We measured polychlorinated biphenyls, organochlorine pesticides, polybrominated diphenyl ether

223 ed toxaphenes, polychlorinated naphthalenes, organochlorine pesticides, polychlorinated biphenyls, po

224 red when using argon-based gases for certain organochlorine pesticides, suggesting the discharge gas

225 Among the organochlorine pesticides, the most abundant was dieldri

226 polybrominated diphenyl ethers (PBDEs), and organochlorine pesticides, were quantified in plasma sam

227 argely halogenated methoxylated benzenes and organochlorine pesticides, were then subjected to target

228 els of polychlorinated biphenyls and certain organochlorine pesticides--hexachlorobenzene, dichlorodi

229 g 21 PCB congeners, 8 PBDE congeners, and 21 organochlorine pesticides.

230 d subsequently a complete ban on, the use of organochlorine pesticides; (ii) improvements in Peregrin

231 te variables for time lags of 0 to 10 yr and organochlorine pollutant concentrations spanning 1975-20

232 Organochlorine pollutant data sets spanning 40 years, wh

233 ts regarding the relation between persistent organochlorine pollutants (POPs) and endometriosis in wo

234 These observations indicate that organochlorine pollutants will form indoors when bleach

235 re associated with higher BMI, and levels of organochlorine pollutants, cobalt, and molybdenum were a

236 ,6-tribromophenol (2,4,6-TBP), OH-PBDEs) and organochlorines (polychlorinated biphenyls (PCBs), 1,1-b

237 ufficient for a positive association of some organochlorine POPs with type 2 diabetes.

238 tive ingredient applied for organophophates, organochlorines, pyrethroids, and carbamates were aggreg

239 mixture of 31 pesticides (organophosphates, organochlorines, pyrethroids, and others) at spiking lev

240 ence in An. gambiae that organophosphate and organochlorine resistance is conferred by overexpression

241 f 0.07 with the chlorine covalently bound as organochlorine species, many of which are aromatic.

242 te associations between lifetime exposure to organochlorines, specifically dichlorodiphenyldicholoret

243 ous studies, prenatal exposure to persistent organochlorines such as 1,1,-dichloro-2,2-bis(p-chloroph

244 th climate change, concentrations of certain organochlorines such as hexachlorobenzene and p, p'-DDE

245 al method was developed for determination of organochlorine, synthetic pyrethroid, organophosphate an

246 t CPO plays a key role in production of soil organochlorines, this observation points to the addition

247 phenyls, polybrominated diphenyl ethers, and organochlorine through a river food web, assessing the d

248 We quantified food web organochlorine transfer in the Cumberland Sound (Nunavut

249 ce following a reduction and eventual ban on organochlorine use facilitated the observed increase in

250 ternal serum that was collected before these organochlorines were banned in the United States.

251 dic children, a negative association of PC4 (organochlorines) with ever eczema (OR 0.78, 0.61-0.99) w