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基于暴露后摄食的河口泥螺现场毒性测定。

An estuarine mudsnail in situ toxicity assay based on postexposure feeding.

机构信息

IMAR-Instituto do Mar, Department of Life Sciences, University of Coimbra, Coimbra, Portugal.

出版信息

Environ Toxicol Chem. 2011 Aug;30(8):1935-42. doi: 10.1002/etc.585. Epub 2011 Jun 3.

DOI:10.1002/etc.585
PMID:21590798
Abstract

In situ assays provide more realistic exposure scenarios than laboratory assays, which is particularly pertinent for estuaries because exposure conditions are difficult to simulate. Traditionally, sublethal toxicity testing endpoints, such as growth, emergence, and reproduction, imply time-delayed extrapolations from individuals to populations, communities, and ecosystems. Sublethal responses mechanistically linked to ecosystem functions have been largely neglected. Feeding is an unequivocal ecologically meaningful response because its impairment has direct and immediate effects on ecosystems, by hampering key functions such as organic matter decomposition, long before its effects at the individual level have consequences at successively higher levels of biological organization. The ultimate goal of the present study was to widen the range of ecosystem functions for estuarine quality assessments. Specifically, a short-term in situ assay based on the postexposure feeding of the mudsnail Hydrobia ulvae is presented. Methodologies to quantify precisely postexposure egestion as a surrogate of feeding were achieved. A multiple regression model from laboratory experiments was successfully applied to an in situ assay at reference (Mira River) and contaminated Portuguese estuaries (Sado River) for predicting reference results and allowing unraveling confounding factors during exposure (temperature, salinity, sediment grain size). Sensitivity comparisons of postexposure feeding with survival and growth, after Cu exposure, were carried out and used for a first preliminary appraisal of the relative consequences of ecosystem-level immediate effects.

摘要

原位测定法提供了比实验室测定法更符合实际的暴露情景,这对于河口尤为相关,因为很难模拟暴露条件。传统上,亚致死毒性测试终点,如生长、出现和繁殖,意味着从个体到种群、群落和生态系统的时间延迟推断。与生态系统功能有机械联系的亚致死反应在很大程度上被忽视了。摄食是一种明确的具有生态意义的反应,因为它的损害会直接和立即对生态系统产生影响,通过阻碍关键功能,如有机物分解,而在其对个体水平的影响在生物组织的更高层次上产生后果之前。本研究的最终目标是拓宽评估河口质量的生态系统功能范围。具体来说,提出了一种基于泥螺 Hydrobia ulvae 暴露后摄食的短期原位测定法。精确量化暴露后排粪作为摄食替代物的方法已经实现。从实验室实验中得出的多元回归模型成功应用于参考(米拉河)和受污染的葡萄牙河口(萨多河)的原位测定法,以预测参考结果,并在暴露期间(温度、盐度、沉积物粒度)揭示混杂因素。对铜暴露后暴露后摄食与生存和生长的敏感性进行了比较,并用于对生态系统水平即时影响的相对后果进行初步评估。

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