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Cancer Epidemiology, Biomarkers & Prevention
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MDR1 Gene Variants, Indoor Insecticide Exposure, and the Risk of Childhood Acute Lymphoblastic Leukemia

Kevin Y. Urayama, John K. Wiencke, Patricia A. Buffler, Anand P. Chokkalingam, Catherine Metayer and Joseph L. Wiemels
Kevin Y. Urayama
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John K. Wiencke
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Patricia A. Buffler
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Anand P. Chokkalingam
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Catherine Metayer
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Joseph L. Wiemels
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DOI: 10.1158/1055-9965.EPI-07-0007 Published June 2007
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Tables

  • Table 1.

    Allele frequencies in non-Hispanic White and Hispanic control children

    SNPAlleleNon-Hispanic White
    Hispanic
    P*
    nFrequency (%)nFrequency (%)
    T−129CT16594.915195.7
    C5.14.30.617
    C1236TC16855.415053.3
    T44.646.70.609
    G2677T/AG16553.615057.3
    T43.338.0
    A3.14.70.274
    C3435TC17046.215254.6
    T53.845.40.032
    • ↵* Pearson χ2 test was used to test the difference in allele frequencies between non-Hispanic Whites and Hispanic control children.

  • Table 2.

    Analysis of MDR1 SNPs and risk of childhood ALL

    GenotypeCases (n = 294)Controls (n = 369)OR (95% CI)*
    T−129C
        TT253 (89.7)330 (90.9)1.00 (Reference)
        TC27 (9.6)32 (8.8)1.09 (0.62-1.93)
        CC2 (0.7)1 (0.3)2.68 (0.23-30.96)
        TC + CC29 (10.3)33 (9.1)1.12 (0.64-1.97)
    C1236T
        CC73 (25.7)97 (26.6)1.00 (Reference)
        CT144 (50.7)199 (54.5)0.90 (0.61-1.33)
        TT67 (23.6)69 (18.9)1.15 (0.73-1.81)
        CT + TT211 (74.3)268 (73.4)0.97 (0.67-1.40)
    G2677T/A
        GG79 (28.2)104 (28.8)1.00 (Reference)
        GT or GA144 (51.4)192 (53.2)1.01 (0.70-1.46)
        TA, TT, or AA57 (20.4)65 (18.0)1.26 (0.78-2.05)
        Non-GG201 (71.8)257 (71.2)1.06 (0.74-1.51)
    C3435T
        CC81 (27.6)100 (27.1)1.00 (Reference)
        CT140 (47.6)178 (48.2)0.98 (0.67-1.42)
        TT73 (24.8)91 (24.7)0.99 (0.65-1.49)
        CT + TT213 (72.4)269 (72.9)0.98 (0.69-1.39)
    • ↵* ORs and 95% CI were calculated using conditional logistic regression (matching factors: date of birth, sex, Hispanic status, and maternal race).

  • Table 3.

    Analysis of MDR1 haplotypes and risk of childhood ALL

    C1236TG2677T/AC3435TCasesControlsOR (95% CI)*
    Hap 1CGC38.840.30.92 (0.58-1.45)
    Hap 2CGT8.08.80.83 (0.37-1.88)
    Hap 3TGC6.15.51.07 (0.41-2.75)
    Hap 4TTT38.337.31.09 (0.68-1.75)
    Hap 5†xAx3.53.80.91 (0.28-2.92)
    Hap 6‡Other5.24.31.54 (0.50-4.72)
    Gene copies588738
    Global likelihood ratio test§P = 0.970
    • ↵* Haplotype ORs and 95% CIs were calculated using conditional logistic regression modeling haplotype probabilities (matching factors: date of birth, sex, Hispanic status, and maternal race). Each haplotype is compared with all other haplotypes.

    • ↵† Group of haplotypes that contain the variant A allele at the G2677T/A locus (includes CAC, CAT, TAC, and TAT).

    • ↵‡ Group of rare haplotypes with frequencies <5% and not part of Hap 5 (includes CTC, CTT, TGT, and TTC).

    • ↵§ Global likelihood ratio test done over all haplotypes. Estimates of exact P values were computed using Monte Carlo methods with 10,000 permutations.

  • Table 4.

    Main effects for MDR1 diplotypes and indoor insecticide exposure and risk of childhood ALL

    Cases (n = 294)Controls (n = 369)OR (95% CI)*
    MDR1 diplotype
        Hap 1 (CGC)†
            Other/other111 (37.8)125 (33.9)1.00 (Reference)
            ≥One copy183 (62.3)244 (66.1)0.88 (0.63-1.21)
        Hap 4 (TTT)†
            Other/other108 (36.7)138 (37.4)1.00 (Reference)
            ≥One copy186 (63.2)231 (62.6)1.03 (0.74-1.44)
        Indoor insecticide exposure‡
            No54 (18.4)92 (24.9)1.00 (Reference)
            Yes240 (81.6)277 (75.1)1.65 (1.10-2.47)
    • ↵* ORs and 95% CIs were calculated using conditional logistic regression (matching factors: date of birth, sex, Hispanic status, and maternal race). The analysis of indoor insecticide exposure was additionally adjusted for household income.

    • ↵† The order of the MDR1 SNP loci in the haplotypes is C1236T, G2677T/A, and C3435T.

    • ↵‡ Indoor insecticide exposure anytime from 1 y before child's birth through the first 3 y of life. Exposure(s) occurring within the year before diagnosis for cases and corresponding date for controls was discarded for the analyses.

  • Table 5.

    Analysis of interaction between common MDR1 haplotypes, indoor insecticide exposure, and risk of childhood ALL

    HaplotypePesticideCasesControlsOR (95% CI)*P
    Hap CGC × Indoor insecticide
        −No19 (6.5)39 (10.6)1.00 (Reference)
        −Yes92 (31.3)86 (23.3)3.03 (1.54-6.00)
        +No35 (11.9)53 (14.4)1.87 (0.90-3.91)
        +Yes148 (50.3)191 (51.8)2.09 (1.12-3.91)
    Interaction†0.37 (0.15-0.88)0.025
    Hap TTT × Indoor insecticide
        −No18 (6.1)29 (7.9)1.00 (Reference)
        −Yes90 (30.6)109 (29.5)1.46 (0.73-2.90)
        +No36 (12.2)63 (17.1)0.95 (0.46-1.99)
        +Yes150 (51.0)168 (45.5)1.68 (0.86-3.27)
    Interaction†1.21 (0.53-2.74)0.649
    • ↵* ORs and 95% CIs were calculated using conditional logistic regression (matching factors: date of birth, sex, Hispanic status, and maternal race) adjusting for household income.

    • ↵† Interaction OR (ORInteraction) based on the multiplicative model of interaction defined as the ratio of the joint effect of the MDR1 haplotype and indoor insecticide exposure and product of the individual effects [ORInteraction = ORGE / (ORGE′ × ORG′E)].

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Cancer Epidemiology Biomarkers & Prevention: 16 (6)
June 2007
Volume 16, Issue 6
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MDR1 Gene Variants, Indoor Insecticide Exposure, and the Risk of Childhood Acute Lymphoblastic Leukemia
Kevin Y. Urayama, John K. Wiencke, Patricia A. Buffler, Anand P. Chokkalingam, Catherine Metayer and Joseph L. Wiemels
Cancer Epidemiol Biomarkers Prev June 1 2007 (16) (6) 1172-1177; DOI: 10.1158/1055-9965.EPI-07-0007

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MDR1 Gene Variants, Indoor Insecticide Exposure, and the Risk of Childhood Acute Lymphoblastic Leukemia
Kevin Y. Urayama, John K. Wiencke, Patricia A. Buffler, Anand P. Chokkalingam, Catherine Metayer and Joseph L. Wiemels
Cancer Epidemiol Biomarkers Prev June 1 2007 (16) (6) 1172-1177; DOI: 10.1158/1055-9965.EPI-07-0007
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