使用体外雌激素介导的转录激活试验(T47D-KBluc),对家畜和污水处理废水中发现的环境雌激素混合物进行建模。

Dieldrich S. Bermudez, L. Earl Gray, Vickie S. Wilson
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引用次数: 28

摘要

人们越来越关注鱼类、野生动物和人类接触受雌激素污染的水源及其对生殖健康的潜在影响。环境雌激素可以来自各种来源,包括集中的动物饲养场(CAFO)、城市废物、农业和工业废水。美国环保署的饮用水污染物候选清单3 (CCL3)包括几种雌激素化合物。虽然这些污染物目前不受任何拟议或颁布的国家初级饮用水条例的约束,但已知或预计会在公共供水系统中出现,未来可能需要根据《安全饮用水法》进行管制。使用体外转录激活试验,本研究评估了CCL3的雌激素,包括单独的雌激素和七种雌激素混合物(固定射线设计),在广泛的浓度范围内,包括环境相关浓度。各雌激素的Log EC50和Hillslope值分别为:雌酮,−11.92,1.283;雌二醇-17α,−9.61,1.486;雌二醇-17β, 11.77, 1.494;雌三醇,−11.14,1.074;炔雌醇-17α,−12.63,1.562;Mestranol, - 11.08, 0.809, Equilin, - 11.48, 0.946。此外,还测试了反映猪、家禽和乳制品CAFO废水中发现的主要雌激素的混合物(固定比例射线设计),以及激素替代疗法和/或口服避孕药中发现的雌激素的三元混合物(4 × 4 × 4因子设计)。采用浓度添加(CA)模型和雌激素等效(EEQ)模型评价混合物的可加性。对于每一项混合物研究,都测试了广泛的浓度范围,高于或低于环境相关浓度。结果表明,对于任何混合物,观测数据与CA或EEQ预测都没有一致的变化。因此,无论是CA还是EEQ模型都应该是雌激素混合物建模的有用预测因子。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Modelling defined mixtures of environmental oestrogens found in domestic animal and sewage treatment effluents using an in vitro oestrogen-mediated transcriptional activation assay (T47D-KBluc)

Modelling defined mixtures of environmental oestrogens found in domestic animal and sewage treatment effluents using an in vitro oestrogen-mediated transcriptional activation assay (T47D-KBluc)

There is growing concern of exposure of fish, wildlife and humans to water sources contaminated with oestrogens and the potential impact on reproductive health. Environmental oestrogens can come from various sources including concentrated animal feedlot operations (CAFO), municipal waste, agricultural and industrial effluents. US EPA’s drinking water contaminant candidate list 3 (CCL3) includes several oestrogenic compounds. Although these contaminants are currently not subject to any proposed or promulgated national primary drinking water regulations, they are known or anticipated to occur in public water systems and may require future regulation under the Safe Drinking Water Act. Using an in vitro transcriptional activation assay, this study evaluated oestrogens from CCL3 both individually and as a seven oestrogen mixture (fixed ray design) over a broad range of concentrations, including environmentally relevant concentrations. Log EC50 and Hillslope values for individual oestrogens were as follows: estrone, −11.92, 1.283; estradiol-17α, −9.61, 1.486; estradiol-17β, 11.77, 1.494; estriol, −11.14, 1.074; ethinyl estradiol-17α, −12.63, 1.562; Mestranol, −11.08, 0.809 and Equilin, −11.48, 0.946. In addition, mixtures that mirrored the primary oestrogens found in swine, poultry and dairy CAFO effluent (fixed-ratio ray design), and a ternary mixture (4 × 4 × 4 factorial design) of oestrogens found in hormone replacement therapy and/or oral contraceptives were tested. Mixtures were evaluated for additivity using both the concentration addition (CA) model and oestrogen equivalence (EEQ) model. For each of the mixture studies, a broad range of concentrations were tested, both above and below environmentally relevant concentrations. Results show that the observed data did not vary consistently from either the CA or EEQ predictions for any mixture. Therefore, either the CA or EEQ model should be useful predictors for modelling oestrogen mixtures.

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