Fenske Christiane, Daeschlein Georg, Günther Burkhart, Knauer Angelika, Rudolph Peter, Schwahn Christian, Adrian Vera, von Woedtke Thomas, Rossberg Harald, Jülich Wolf-Dieter, Kramer Axel
Department of Chemistry and Biochemistry, Ernst Moritz Arndt University, Greifswald, Germany.
Int J Hyg Environ Health. 2006 May;209(3):275-84. doi: 10.1016/j.ijheh.2005.12.004. Epub 2006 Feb 3.
To test the effects of heavy metals in river water, we compared the sensitivity of seven different biological test methods, using bacteria (Vibrio fischeri), human FL cells, protozoans (Paramecium spp.), nematodes (Rhabditis oxycerca), aquatic plants (Lemna minor), and fishes (Leuciscus idus melanotus). As test substance we used a representative mixture of 3.0 microg/l As, 2.5 microg/l Pb, 0.8 microg/l Cd, 1.7 microg/l Cr, 3.9 microg/l Cu, 6.7 microg/l Ni, 0.4 microg/l Hg, and 23.0 microg/l Zn, imitating the detectable heavy metal contamination of the Odra estuary (NE Germany/NW Poland). This mixture was defined as normal concentration (NC). Most sensitive was the test with L. minor (exposure time 10 d). The plants already showed phytotoxic effects at the heavy metal concentration found in the Odra estuary. Test systems with human cells, protozoans, and nematodes (exposure time 1-7 d) reacted at concentrations 85-100 times above the NC. Fish toxicity (exposure time 2 d) occurred from 130-fold concentration upwards. In contrast, the standard test carried out with luminescent bacteria (exposure time 30 min) was affected only at > 1000-fold concentrations. This test is therefore not suitable as an early warning system to detect ecological risks. Even the NC of heavy metals measured in the Odra estuary inhibits cells and the growth of aquatic plants. Of the single heavy metals tested, copper produced the strongest effects. Therefore, the reduction of heavy metal emissions, especially of copper-which can amplify the toxicity of other heavy metals-should be a task of highest priority.
为了测试河水中重金属的影响,我们比较了七种不同生物测试方法的敏感性,使用了细菌(费氏弧菌)、人类FL细胞、原生动物(草履虫属)、线虫(尖尾小杆线虫)、水生植物(浮萍)和鱼类(黑背雅罗鱼)。作为测试物质,我们使用了一种代表性混合物,其中含有3.0微克/升的砷、2.5微克/升的铅、0.8微克/升的镉、1.7微克/升的铬、3.9微克/升的铜、6.7微克/升的镍、0.4微克/升的汞和23.0微克/升的锌,模拟奥得河河口(德国东北部/波兰西北部)可检测到的重金属污染。这种混合物被定义为正常浓度(NC)。最敏感的是浮萍测试(暴露时间10天)。这些植物在奥得河河口发现的重金属浓度下就已经表现出植物毒性效应。使用人类细胞、原生动物和线虫的测试系统(暴露时间1 - 7天)在高于NC浓度85 - 100倍时产生反应。鱼类毒性(暴露时间2天)从高于NC浓度130倍时开始出现。相比之下,用发光细菌进行的标准测试(暴露时间30分钟)仅在浓度高于1000倍时受到影响。因此,该测试不适用于检测生态风险的早期预警系统。即使是在奥得河河口测量的重金属NC也会抑制细胞和水生植物的生长。在所测试的单一重金属中,铜产生的影响最强。因此,减少重金属排放,尤其是铜的排放(铜可增强其他重金属的毒性)应是最优先的任务。