FG Zellbiologie und Angewandte Botanik, Fachbereich Biologie, Philipps-Universität Marburg, Karl-von-Frisch-Strasse, D-35032, Marburg, Germany.
Environ Sci Pollut Res Int. 1998;5(1):28-36. doi: 10.1007/BF02986371.
Legume root nodules are the site of biological nitrogen fixation in the Rhizobium-legume symbiosis. Nodules are structures unique to this symbiosis and they are morphologically as well as physiologically distinct from other plant organs. Organic substances affecting the macro- or microsymbionts vitality, such as PAHs (WETZEL: et al., 1991), reduce nodulation even before visible damage to the plant can be detected. We present data that the formation of nodules (nodulation) may also serve for ecotoxicological evaluation of heavy metals in different binding states. Tests were performed in petri dishes with alfalfa (lucerne) seedlings inoculated with Rhizobium meliloti. Cultivation took place in growth cabinets with carefully standardized and documented growth conditions. Data from stressed plants was recorded after 14 days of cultivation on contaminated substrate. A dose responsive decrease in nodulation was found after application of cadmium acetate, cadmium iodide, cadmium chloride, sodium salts of arsenate and arsenite, arsenic pentoxide, and lead nitrate, whereas lead acetate showed no effect up to a concentration of 3 microM. The dose response curves were used to calculate EC10, EC50 and EC90 values. EC50 values for cadmium compounds range from 1.5 to 9.5 pM. Testing different arsenic compounds results in EC50 from 2.6 to 20.1 microM. EC50 of lead nitrate is 2.2 microM. The sensitivity, reproducibility and reliability of this test system is discussed compared to established biotests.
豆科植物的根瘤是根瘤菌与豆科植物共生体中生物固氮的场所。根瘤是这种共生体特有的结构,在形态和生理上与其他植物器官明显不同。影响宏观或微观共生体活力的有机物质,如多环芳烃(WETZEL 等人,1991),甚至在植物出现可见损伤之前就会降低结瘤率。我们提供的数据表明,根瘤(结瘤)的形成也可用于评价不同结合态重金属的生态毒性。试验在接种根瘤菌的苜蓿(三叶草)幼苗的培养皿中进行。在精心标准化和记录生长条件的培养箱中进行培养。在受污染基质上培养 14 天后,记录胁迫植物的数据。在施加醋酸镉、碘化镉、氯化镉、砷酸钠和亚砷酸钠、五氧化二砷和硝酸铅后,发现结瘤率呈剂量反应性下降,而醋酸铅在 3 microM 浓度下没有效果。根据剂量反应曲线计算出 EC10、EC50 和 EC90 值。镉化合物的 EC50 值范围为 1.5 至 9.5 pM。测试不同的砷化合物导致 EC50 值在 2.6 至 20.1 microM 之间。硝酸铅的 EC50 值为 2.2 microM。与已建立的生物测试相比,讨论了该测试系统的灵敏度、重现性和可靠性。