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

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

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

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

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

8 The observed association of organochlorine and organophosphate insecticides with dia

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

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

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

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

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

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

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

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

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

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

19 Organochlorines are environmentally persistent contamina

20 , supplementary food did not alleviate their organochlorine burden.

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

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

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

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

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

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

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

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

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

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

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

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

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

34 e knowledge regarding natural attenuation of organochlorine compounds.

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

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

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

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

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

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

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

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

43 The organochlorine dichlorodiphenyltrichloroethane (DDT), a

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

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

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

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

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

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

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

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

52 Organochlorine exposure was linked to non-Hodgkin lympho

53 Overweight and BMI were unrelated to organochlorine exposure.

54 Organochlorine exposures measured at age 14 and in adult

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

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

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

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

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

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

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

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

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

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

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

66 The organochlorine insecticide aldrin was also associated wi

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

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

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

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

71 2-bis(p-chlorophenyl)ethane (DDT), the first organochlorine insecticide, and pyrethroid insecticides

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

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

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

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

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

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

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

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

80 Organochlorine molecules (Clorg) are surprisingly abunda

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

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

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

84 Organochlorine (OC) insecticides and polychlorinated bip

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

86 Organochlorine (OC) pesticides and the more persistent p

87 Organochlorine (OC) pesticides pose a significant enviro

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

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

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

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

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

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

94 Polychlorinated biphenyl and organochlorine pesticide concentrations in maternal mid-

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

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

97 We report measurements of organochlorine pesticide diffusion and partition coeffic

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

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

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

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

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

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

104 Chlordecone is an organochlorine pesticide that has been extensively used

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

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

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

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

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

110 Organochlorine pesticides (OCPs) and polychlorinated bip

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

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

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

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

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

116 Organochlorine pesticides (OCPs) have been linked to adu

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

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

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

120 ), 14 non-BDE flame retardants (FRs), and 25 organochlorine pesticides (OCPs) were analyzed in air sa

121 Organochlorine pesticides (OCPs) were measured in the su

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

144 2-tk-CAT and mouse PXR demonstrated that the organochlorine pesticides transnonachlor and chlordane a

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

161 Among the organochlorine pesticides, the most abundant was dieldri

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

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

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

165 ,6-tribromophenol (2,4,6-TBP), OH-PBDEs) and organochlorines (polychlorinated biphenyls (PCBs), 1,1-b

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

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

168 te associations between lifetime exposure to organochlorines, specifically dichlorodiphenyldicholoret

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

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

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

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

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

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