Childhood Brain Tumors, Residential Insecticide Exposure, and Pesticide Metabolism Genes

被引:46
作者
Nielsen, Susan Searles [1 ]
McKean-Cowdin, Roberta [2 ]
Farin, Federico M. [3 ]
Holly, Elizabeth A. [4 ]
Preston-Martin, Susan [2 ]
Mueller, Beth A. [1 ,5 ]
机构
[1] Fred Hutchinson Canc Res Ctr, Div Publ Hlth Sci, Seattle, WA 98109 USA
[2] Univ So Calif, Dept Prevent Med, Keck Sch Med, Kenneth Norris Jr Comprehens Canc Ctr, Los Angeles, CA 90089 USA
[3] Univ Washington, Dept Environm & Occupat Hlth Sci, Ctr Ecogenet & Environm Hlth, Seattle, WA 98195 USA
[4] Univ Calif San Francisco, Sch Med, Dept Epidemiol & Biostat, San Francisco, CA 94143 USA
[5] Univ Washington, Sch Publ Hlth & Community Med, Dept Epidemiol, Seattle, WA 98195 USA
基金
美国国家卫生研究院;
关键词
acetylcholinesterase inhibition; childhood cancer; children; gene-environment interaction; insecticides; pesticides; xenobiotic metabolism; BUTYRYLCHOLINESTERASE K-VARIANT; CONTAINING MONOOXYGENASE-1 FMO1; FLAVIN-CONTAINING MONOOXYGENASE; HUMAN PARAOXONASE PON1; ORGANOPHOSPHORUS COMPOUNDS; ENVIRONMENT INTERACTION; THIOETHER COMPOUNDS; IN-VITRO; POLYMORPHISMS; EXPRESSION;
D O I
10.1289/ehp.0901226
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
BACKGROUND: Insecticides that target the nervous system may play a role in the development of childhood brain tumors (CBTs). Constitutive genetic variation affects metabolism of these chemicals. METHODS: We analyzed population-based case-control data to examine whether CBT is associated with the functional genetic polymorphisms PON1(C-108T), PON1(Q192R), PON1(L55M), BCHEA539T, FMO1(C-9536A), FMO3(E158K), ALDH3A1(S134A), and GSM (null). DNA was obtained from newborn screening archives for 201 cases and 285 controls, <= 10 years of age, and born in California or Washington State between 1978 and 1990. Conception-to-diagnosis home insecticide treatment history was ascertained by interview. RESULTS: We observed no biologically plausible main effects for any of the metabolic polymorphisms with CBT risk. However, we observed strong interactions between genotype and insecticide exposure during childhood. Among exposed children, CBT risk increased per PON1(-108T) allele [odds ratio (OR) = 1.8; 95% confidence interval (CI), 1.1-3-0] and FMO1(-9536A) (*6) allele (OR = 2.7; 95% CI, 1.2-5-9), whereas among children never exposed, CBT risk was not increased (PON1: OR = 0.7; 95% CI, 0.5-1.0, interaction p = 0.005; FMO1: OR = 1.0; 95% CI, 0.6-1.6, interaction p = 0.009). We observed a similar but statistically nonsignificant interaction between childhood exposure and BCHEA539T (interaction p = 0.08). These interactions were present among both Hispanic and non-Hispanic white children. CONCLUSION: Based on known effects of these variants, these results suggest that exposure in childhood to organophosphorus and perhaps to carbamate insecticides in combination with a reduced ability to detoxify them may be associated with CBT. Confirmation in other studies is required.
引用
收藏
页码:144 / 149
页数:6
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