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利用化学和生态毒理学工具研究葡萄牙圣多明戈废弃矿区的砷、铜、铅和锌(生物)有效性。

A study on As, Cu, Pb and Zn (bio)availability in an abandoned mine area (São Domingos, Portugal) using chemical and ecotoxicological tools.

机构信息

DCTA, Escola Superior Agrária, Instituto Politécnico de Beja, Rua Pedro Soares, 7800-295, Beja, Portugal.

出版信息

Environ Sci Pollut Res Int. 2013 Sep;20(9):6539-50. doi: 10.1007/s11356-013-1649-2. Epub 2013 Apr 23.

Abstract

The aim of this study was to relate the results obtained by chemical methods, used to assess environmental (bio)availability, with the ecotoxic response and bioaccumulation of trace elements (TE) by the earthworm Eisenia fetida exposed to field-contaminated, metal-polluted soils from a sulphide mine. The extracting solution 0.5 M NH4CH3COO, 0.5 M CH3COOH and 0.02 M EDTA (pH 4.7), was able to predict environmental bioavailability of TE to E. fetida. However, the toxicological bioavailability could not be predicted from the results of the chemical extractions or from the bioaccumulation results: E. fetida reproduction was higher in soils where environmental bioavailability of TE and bioaccumulation values were also higher. In this study, the toxic response of the organism seemed to be more influenced by the overall nutritional status of the soil (e.g. pH, organic matter, plant nutrient availability and cation exchange capacity) than by its TE contamination. In the case of anthropogenic multi-contaminated sites, the different soil characteristics exert an important and confounding influence in the toxic response and the relationship between different bioavailable fractions cannot be easily established, emphasising the need to combine results from chemical methods with those from bioassays when evaluating the bioavailability of TE in these soils.

摘要

本研究旨在将用于评估环境(生物)有效性的化学方法的结果与蚯蚓(Eisenia fetida)暴露于来自硫化物矿的受污染、金属污染土壤中的痕量元素(TE)的生态毒性反应和生物累积联系起来。提取溶液 0.5 M NH4CH3COO、0.5 M CH3COOH 和 0.02 M EDTA(pH 4.7)能够预测 TE 对 E. fetida 的环境生物有效性。然而,毒理学生物有效性不能从化学提取的结果或生物累积的结果来预测:E. fetida 的繁殖在 TE 的环境生物有效性和生物累积值也较高的土壤中更高。在这项研究中,生物体的毒性反应似乎更多地受到土壤整体营养状况的影响(例如 pH 值、有机质、植物养分的可用性和阳离子交换能力),而不是其 TE 污染。在人为多污染地点的情况下,不同的土壤特性会对毒性反应产生重要且复杂的影响,并且不同生物可利用分数之间的关系不能轻易建立,这强调了在评估这些土壤中 TE 的生物有效性时,需要将化学方法的结果与生物测定的结果结合起来。

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