Cemagref, UR HBAN, Parc de Tourvoie-BP 44, F-92163 Antony, France.
Environ Toxicol. 2010 Oct;25(5):468-78. doi: 10.1002/tox.20591.
It is often difficult to evaluate the level of contamination in small urban rivers because pollution is mainly diffuse, with low levels of numerous substances. The use of a coupled approach using both chemical and biological measurements may provide an integrated evaluation of the impact of micro-pollution on the river. Zebra mussels were transplanted along a metal and organic pollution gradient in spring 2008. For two months, mussels and water samples were collected from two sites every two weeks and analyzed for metal and PAH content as well as water physicochemical parameters. Diffusive gradients in thin film (DGT) were also used to assess levels of labile metals. Exposure of mussels to contaminants and potential impact were evaluated using physiological indices and various biomarkers including condition index (CI), defense mechanisms (glutathione-S-transferase: GST), digestive enzymes (amylase and cellulase) and genotoxicity (micronucleus test: MN and comet assay: CA). For most contaminants, the water contamination was significantly higher downstream. Bioaccumulation in zebra mussels was related to water contamination in the framework of the biodynamic model, which allowed us to take into account the biological dilution that was caused by the growth of soft tissue downstream. Thus, metal influxes were on average two times higher downstream than upstream in particular for Zn, Cr, Cu and Cd. Significant differences in condition index were observed (final CI was 0.42 ± 0.03 downstream and 0.31 ± 0.03 upstream) reflecting a better food availability downstream. Moreover a significant decrease of GST activity and digestive enzymes activity in the cristalline style was observed downstream. Interpreting this decrease requires considering not only micro-pollution but also the trophic status related to the water's physicochemistry. The MN test and the CA on gill cells highlighted genotoxicity in mussels transplanted downstream compared to upstream.
由于污染主要是扩散的,且存在许多低浓度的物质,因此评估小型城市河流的污染程度通常较为困难。采用化学和生物测量相结合的方法可以对微污染对河流的影响进行综合评估。2008 年春季,斑马贻贝被移植到一条存在金属和有机污染梯度的河流中。两个月内,每隔两周从两个地点采集贻贝和水样,分析金属和 PAH 含量以及水的理化参数。还使用扩散梯度薄膜(DGT)来评估可利用金属的水平。通过生理指标和各种生物标志物(包括条件指数(CI)、防御机制(谷胱甘肽 S-转移酶:GST)、消化酶(淀粉酶和纤维素酶)和遗传毒性(微核试验:MN 和彗星试验:CA)来评估贻贝对污染物的暴露和潜在影响。对于大多数污染物,下游的水污染明显更高。斑马贻贝的生物积累与水污染物在生物动力学模型框架内有关,该模型允许我们考虑因下游软组织生长而导致的生物稀释。因此,与上游相比,金属流入量下游平均高出两倍,尤其是对于 Zn、Cr、Cu 和 Cd。下游的条件指数存在显著差异(最终 CI 为 0.42 ± 0.03,上游为 0.31 ± 0.03),这反映了下游食物供应更充足。此外,下游的 GST 活性和晶状结构中的消化酶活性显著下降。下游的 GST 活性和晶状结构中的消化酶活性显著下降。解释这种下降不仅需要考虑微污染,还需要考虑与水的理化性质相关的营养状况。下游贻贝的 MN 试验和 CA 试验都强调了遗传毒性。