Rusiecki Jennifer A, De Roos Anneclaire, Lee Won Jin, Dosemeci Mustafa, Lubin Jay H, Hoppin Jane A, Blair Aaron, Alavanja Michael C R
Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, Department of Health and Human Services, Rockville, MD 20892-7240, USA.
J Natl Cancer Inst. 2004 Sep 15;96(18):1375-82. doi: 10.1093/jnci/djh264.
Atrazine is the most heavily applied agricultural pesticide for crop production in the United States. Both animal and human studies have suggested that atrazine is possibly carcinogenic, but results have been mixed. We evaluated cancer incidence in atrazine-exposed pesticide applicators among 53,943 participants in the Agricultural Health Study, a prospective cohort study of licensed pesticide applicators in Iowa and North Carolina.
We obtained detailed pesticide exposure information using a self-administered questionnaire completed at the time of enrollment (1993-1997). Cancer incidence was followed through December 31, 2001. We used adjusted Poisson regression to calculate rate ratios (RRs) and 95% confidence intervals (CIs) of multiple types of cancer among atrazine exposed applicators. P(trend) values were calculated using atrazine exposure as a continuous variable, and all statistical tests were two-sided. Two exposure metrics were used: quartiles of lifetime days of exposure and quartiles of intensity-weighted lifetime days of exposure.
36,513 (68%) applicators reported ever using atrazine; exposure was not associated with overall cancer incidence. Comparisons of cancer incidence in applicators with the highest atrazine exposure and those with the lowest exposure, assessed by lifetime days (RR(LD)) and intensity-weighted lifetime days (RR(IWLD)) of exposure yielded the following results: prostate cancer, RR(LD) = 0.88, 95% CI = 0.63 to 1.23, P(trend) =.26, and RR(IWLD) = 0.89, 95% CI = 0.63 to 1.25, P(trend) =.35; lung cancer, RR(LD) = 1.91, 95% CI = 0.93 to 3.94, P(trend) =.08, and RR(IWLD) = 1.37, 95% CI = 0.65 to 2.86, P(trend) =.19; bladder cancer, RR(LD) = 3.06, 95% CI = 0.86 to 10.81, P(trend) =.18, and RR(IWLD) = 0.85, 95% CI = 0.24 to 2.94, P(trend) =.71; non-Hodgkin lymphoma, RR(LD) = 1.61, 95% CI = 0.62 to 4.16, P(trend) =.35, and RR(IWLD) = 1.75, 95% CI = 0.73 to 4.20, P(trend) =.14; and multiple myeloma, RR(LD) = 1.60, 95% CI = 0.37 to 7.01, P(trend) =.41, and RR(IWLD) = 2.17, 95% CI = 0.45 to 10.32, P(trend) =.21.
Our analyses did not find any clear associations between atrazine exposure and any cancer analyzed. However, further studies are warranted for tumor types in which there was a suggestion of trend (lung, bladder, non-Hodgkin lymphoma, and multiple myeloma).
阿特拉津是美国农业生产中使用最广泛的农药。动物和人体研究均表明阿特拉津可能具有致癌性,但结果不一。我们在农业健康研究的53943名参与者中评估了接触阿特拉津的农药施用者的癌症发病率,该研究是对爱荷华州和北卡罗来纳州持牌农药施用者进行的一项前瞻性队列研究。
我们通过在入组时(1993 - 1997年)填写的一份自填式问卷获取了详细的农药接触信息。随访癌症发病率至2001年12月31日。我们使用校正的泊松回归来计算接触阿特拉津的施用者中多种癌症类型的发病率比(RRs)和95%置信区间(CIs)。P(趋势)值使用阿特拉津接触作为连续变量进行计算,所有统计检验均为双侧检验。使用了两种接触指标:终生接触天数的四分位数和强度加权终生接触天数的四分位数。
36513名(68%)施用者报告曾使用过阿特拉津;接触与总体癌症发病率无关。通过接触的终生天数(RR(LD))和强度加权终生天数(RR(IWLD))评估,比较阿特拉津接触量最高和最低的施用者的癌症发病率,结果如下:前列腺癌,RR(LD) = 0.88,95% CI = 0.63至1.23,P(趋势)= 0.26,RR(IWLD) = 0.89,95% CI = 0.63至1.25,P(趋势)= 0.35;肺癌,RR(LD) = 1.91,95% CI = 0.93至3.94,P(趋势)= 0.08,RR(IWLD) = 1.37,95% CI = 0.65至2.86,P(趋势)= 0.19;膀胱癌,RR(LD) = 3.06,95% CI = 0.86至10.81,P(趋势)= 0.18,RR(IWLD) = 0.85,95% CI = 0.24至2.94,P(趋势)= 0.71;非霍奇金淋巴瘤,RR(LD) = 1.61,95% CI = 0.62至4.16,P(趋势)= 0.35,RR(IWLD) = 1.75,95% CI = 0.73至4.20,P(趋势)= 0.14;多发性骨髓瘤,RR(LD) = 1.60,95% CI = 0.37至7.01,P(趋势)= 0.41,RR(IWLD) = 2.17,9�% CI = 0.45至10.32,P(趋势)= 0.21。
我们的分析未发现阿特拉津接触与所分析的任何癌症之间存在明确关联。然而,对于有趋势提示的肿瘤类型(肺癌、膀胱癌、非霍奇金淋巴瘤和多发性骨髓瘤),有必要进行进一步研究。