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长期使用未经处理的污水灌溉会加速土壤中药物的消散吗?

Does long-term irrigation with untreated wastewater accelerate the dissipation of pharmaceuticals in soil?

机构信息

Institute of Crop Science and Resource Conservation - Soil Science and Soil Ecology, University of Bonn , Bonn, Germany.

出版信息

Environ Sci Technol. 2014 May 6;48(9):4963-70. doi: 10.1021/es501180x. Epub 2014 Apr 16.

DOI:10.1021/es501180x
PMID:24702276
Abstract

Long-term irrigation with untreated wastewater may increase soil microbial adaptation to pollution load and lead to enhanced natural attenuation. We hypothesized that long-term wastewater irrigation accelerates the dissipation of pharmaceuticals. To test our hypothesis we performed an incubation experiment with soils from the Mezquital Valley, Mexico that were irrigated for 0, 14, or 100 years. The results showed that the dissipation half-lives (DT50) of diclofenac (<0.1-1.4 days), bezafibrate (<0.1-4.8 days), sulfamethoxazole (2-33 days), naproxen (6-19 days), carbamazepine (355-1,624 days), and ciprofloxacin were not affected by wastewater irrigation. Trimethoprim dissipation was even slower in soils irrigated for 100 years (DT50: 45-72 days) than in nonirrigated soils (DT50: 12-16 days), was negatively correlated with soil organic matter content and soil-water distribution coefficients, and was inhibited in sterilized soils. Applying a kinetic fate model indicated that long-term irrigation enhanced sequestration of cationic or uncharged trimethoprim and uncharged carbamazepine, but did not affect sequestration of fast-dissipating zwitterions or negatively charged pharmaceuticals. We conclude that microbial adaptation processes play a minor role for pharmaceutical dissipation in wastewater-irrigated soils, while organic matter accumulation in these soils can retard trimethoprim and carbamazepine dissipation.

摘要

长期使用未经处理的污水灌溉可能会增加土壤微生物对污染负荷的适应性,从而导致自然衰减增强。我们假设长期污水灌溉会加速药物的消散。为了验证我们的假设,我们进行了一项在墨西哥梅斯基特山谷的土壤中进行的培养实验,这些土壤分别经过 0 年、14 年或 100 年的灌溉。结果表明,药物的半衰期(DT50)不受污水灌溉的影响,其中包括双氯芬酸(<0.1-1.4 天)、非诺贝特(<0.1-4.8 天)、磺胺甲恶唑(2-33 天)、萘普生(6-19 天)、卡马西平(355-1624 天)和环丙沙星。在经过 100 年灌溉的土壤中,甲氧苄啶的消解甚至更慢(DT50:45-72 天),而不是在未灌溉的土壤中(DT50:12-16 天),这与土壤有机质含量和土壤水分分布系数呈负相关,并且在灭菌土壤中受到抑制。应用动力学命运模型表明,长期灌溉增强了阳离子或非离子型甲氧苄啶和非离子型卡马西平的固定,而不会影响快速消散的两性离子或带负电荷的药物的固定。我们得出结论,微生物适应过程在污水灌溉土壤中对药物的消解作用较小,而这些土壤中有机物质的积累会减缓甲氧苄啶和卡马西平的消解。

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