农药暴露与幼儿肌酐变化。

M K O'Rourke, P S Lizardi, S P Rogan, N C Freeman, A Aguirre, C G Saint
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引用次数: 101

摘要

接触农药对幼儿的影响可能不同;他们住在离地面更近的地方,相对于体重,他们摄入的食物量比大一点的儿童或成人要大。我们正在使用有机磷酸酯(OP)尿液生物标志物筛选(气相色谱火焰光度检测,GC/FPD)来评估生活在重度农业边境(美墨)社区的154名<或= 6岁儿童的农药暴露情况。筛选检测二乙基磷酸盐(DEPs)和二甲基磷酸盐(dmp)超过1000个非职业暴露个体的参考范围(DL=25微克/克肌酐,Cr)。33%的受试者检测到至少一种代谢物;许多样品含有多种生物标志物。5%的受试者检测到DEP。经常测量DMP和DMTP(分别为25%和26%)。作为尿液稀释的指标,生物标志物的浓度由人体对铬的代谢来调节。单独检查铬浓度以评估其对内剂量测量的影响。不同季节Cr浓度差异显著(K-W=0.83, P=0.022)。根据Mann-Whitney U=1070.5, z=-2.041,秋、春(P=0.038)和夏、秋(P=0.041) Cr浓度存在显著差异(P=0.041)。我们对NHANES III数据的分析没有反映6岁儿童的季节性Cr差异。年龄较小的儿童不包括在内。对代谢物浓度最高的儿童计算吸收日剂量(ADD)估计值。假设一种给定的代谢物全部由一种农药代谢,计算结果是理论值。对几种适宜的农药进行了评价。对于水平最高的儿童,几乎所有的add都超过了RfD。虽然实际代谢物浓度明显下降,但ADD仍超过rfd的第95百分位。尿OP筛查在鉴别非典型内给药者方面是有效的。日铬产量是ADD计算中的一个重要组成部分。铬的可变性产生了独立于暴露的内剂量测量和ADD估计的差异。需要检查幼儿中铬的可变性,在评估儿童经调整的铬内剂量时应谨慎。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Pesticide exposure and creatinine variation among young children.

Pesticide exposure may differentially impact young children; they live closer to the ground and take in greater amounts of food relative to body mass than older children or adults. We are using an organophosphate (OP) urinary biomarker screen (gas chromatography with flame photometric detection, GC/FPD) to evaluate pesticide exposure among 154 children < or = 6 years of age living in a heavily farmed border (US-Mexico) community. The screen detects diethylphosphates (DEPs) and dimethylphosphates (DMPs) above a reference range of 1000 non-occupationally exposed individuals (DL=25 microg/g creatinine, Cr). At least one metabolite was detected for 33% of the subjects; many samples contained multiple biomarkers. DEP was detected in 5% of the subjects. DMP and DMTP were frequently measured (25% and 26%, respectively). Biomarker concentrations are adjusted by the body's metabolism of Cr as an indicator of urine dilution. Cr concentrations were examined separately to evaluate their effect on internal dose measures. Cr concentrations were significantly different by season (K-W=0.83, P=0.022). Significant differences exist between the autumn:spring (P=0.038) Cr concentrations and between summer:autumn (P=0.041) Cr concentrations based on Mann-Whitney U=1070.5, z=-2.041, (P=0.041). Our analysis of NHANES III data did not reflect seasonal Cr differences for 6 year olds. No younger children were included. Absorbed daily dose (ADD) estimates were calculated for children with the highest concentrations of metabolite. Calculations are theoretical values assuming that the entirety of a given metabolite was metabolized from a single pesticide. Several class appropriate pesticides were evaluated. For the children with the highest levels, almost all estimated ADDs exceeded the RfD. Although the actual metabolite concentrations dropped appreciably, ADD were still exceeded RfDs at the 95th percentile. The urinary OP screen was effective in identifying subjects with atypical internal doses. Daily Cr yield is a critical component in ADD calculations. Cr variability produces differences in internal dose measurement and estimates of ADD independent of exposure. Cr variability among young children needs to be examined, and caution should be applied when evaluating Cr adjusted internal doses for children.

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