Biomonitoring of 2,4-dichlorophenoxyacetic acid exposure and dose in farm families

被引:45
作者
Alexander, Bruce H.
Mandel, Jack S.
Baker, Beth A.
Bums, Carol J.
Bartels, Michael J.
Acquavella, John F.
Gustin, Christophe
机构
[1] Univ Minnesota, Sch Publ Hlth, Div Environm Hlth Sci, Minneapolis, MN 55455 USA
[2] Emory Univ, Rollins Sch Publ Hlth, Atlanta, GA 30322 USA
[3] Univ Minnesota, Sch Med, Minneapolis, MN 55455 USA
[4] Dow Chem Co USA, Midland, MI 48674 USA
[5] Monsanto Co, St Louis, MO USA
[6] Amgen Inc, Thousand Oaks, CA USA
关键词
2,4-D; biomonitoring; epidemiologic studies; herbicide; pesticide exposure;
D O I
10.1289/ehp.8869
中图分类号
X [环境科学、安全科学];
学科分类号
08 [工学]; 0830 [环境科学与工程];
摘要
OBJECTIVE: We estimated 2,4-dichlorophenoxyacetic acid (2,4-D) exposure and systemic dose in farm family members following an application of 2,4-D on their farm. METHODS: Farm families were recruited from licensed applicators in Minnesota and South Carolina. Eligible family members collected all urine during five 24-hr intervals, 1 day before through 3 days after an application of 2,4-D. Exposure profiles were characterized with 24-hr urine 2,4-D concentrations, which then were related to potential predictors of exposure. Systemic dose was estimated using the urine collections from the application day through the third day after application. RESULTS: Median urine 2,4-D concentrations at baseline and day after application were 2.1 and 73.1 mu g/L for applicators, below the limit of detection, and 1.2 mu g/L for spouses, and 1.5 and 2.9 mu g/L for children. The younger children (4-11 years of age) had higher median post-application concentrations than the older children (>= 12 years of age) (6.5 vs. 1.9 mu g/L). The geometric mean systemic doses (micrograms per kilogram body weight) were 2.46 (applicators), 0.8 (spouses), 0.22 (all children), 0.32 (children 4-11 years of age), and 0.12 (children a 12 years of age). Exposure to the spouses and children was primarily determined by direct contact with the application process and the number of acres treated. Multivariate models identified glove use, repairing equipment, and number of acres treated as predictors of exposure in the applicators. CONCLUSIONS: We observed considerable heterogeneity of 2,4-D exposure among farm family members, primarily attributable to level of contact with the application process. Awareness of this variability and the actual magnitude of exposures are important for developing exposure and risk characterizations in 2,4-D-exposed agricultural populations.
引用
收藏
页码:370 / 376
页数:7
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