Department of Microbial Ecology, Lund University, S-223 62 Lund, Sweden.
Appl Environ Microbiol. 1994 Jul;60(7):2238-47. doi: 10.1128/aem.60.7.2238-2247.1994.
A thymidine incorporation technique was used to determine the tolerance of a soil bacterial community to Cu, Cd, Zn, Ni, and Pb. An agricultural soil was artificially contaminated in our laboratory with individual metals at three different concentrations, and the results were compared with the results obtained by using the plate count technique. Thymidine incorporation was found to be a simple and rapid method for measuring tolerance. Data obtained by this technique were very reproducible. A linear relationship was found between changes in community tolerance levels obtained by the thymidine incorporation and plate count techniques (r = 0.732, P < 0.001). An increase in tolerance to the metal added to soil was observed for the bacterial community obtained from each polluted soil compared with the community obtained from unpolluted soil. The only exception was when Pb was added; no indication of Pb tolerance was found. An increase in the tolerance to metals other than the metal originally added to soil was also observed, indicating that there was multiple heavy metal tolerance at the community level. Thus, Cu pollution, in addition to increasing tolerance to Cu, also induced tolerance to Zn, Cd, and Ni. Zn and Cd pollution increased community tolerance to all five metals. Ni amendment increased tolerance to Ni the most but also increased community tolerance to Zn and, to lesser degrees, increased community tolerance to Pb and Cd. In soils polluted with Pb increased tolerance to other metals was found in the following order: Ni > Cd > Zn > Cu. We found significant positive relationships between changes in Cd, Zn, and Pb tolerance and, to a lesser degree, between changes in Pb and Ni tolerance when all metals and amendment levels were compared. The magnitude of the increase in heavy metal tolerance was found to be linearly related to the logarithm of the metal concentration added to the soil. Threshold tolerance concentrations were estimated from these linear relationships, and changes in tolerance could be detected at levels of soil contamination similar to those reported previously to result in changes in the phospholipid fatty acid pattern (A. Frostegård, A. Tunlid, and E. Bååth, Appl. Environ. Microbiol. 59: 3605-3617, 1993).
采用胸腺嘧啶核苷掺入技术来测定土壤细菌群落对 Cu、Cd、Zn、Ni 和 Pb 的耐受能力。我们在实验室中用单独的金属以三种不同浓度人工污染农业土壤,并将结果与平板计数技术获得的结果进行了比较。结果表明,胸腺嘧啶核苷掺入法是一种简单、快速的测量耐受能力的方法。该技术获得的数据具有很好的重现性。用该技术获得的群落耐受能力变化数据与平板计数技术获得的数据之间存在线性关系(r=0.732,P<0.001)。与未污染土壤中获得的群落相比,从受污染土壤中获得的细菌群落对添加到土壤中的金属的耐受能力都有所增加。唯一的例外是添加 Pb 时,没有发现对 Pb 的耐受。还观察到对添加到土壤中的除原始金属以外的其他金属的耐受能力增加,表明在群落水平上存在多种重金属耐受能力。因此,Cu 污染除了增加对 Cu 的耐受能力外,还诱导了对 Zn、Cd 和 Ni 的耐受能力。Zn 和 Cd 污染增加了群落对所有五种金属的耐受能力。Ni 处理对 Ni 的增加最大,但也增加了群落对 Zn 的耐受能力,并且在较小程度上增加了对 Pb 和 Cd 的耐受能力。在受 Pb 污染的土壤中,发现其他金属的耐受能力增加的顺序为:Ni>Cd>Zn>Cu。当比较所有金属和添加水平时,我们发现 Cd、Zn 和 Pb 耐受能力的变化之间存在显著的正相关关系,在较小程度上,Pb 和 Ni 耐受能力的变化之间也存在显著的正相关关系。重金属耐受能力的增加幅度与添加到土壤中的金属浓度的对数呈线性关系。从这些线性关系中估计出了阈值耐受浓度,并可以在与先前报道的导致磷脂脂肪酸模式发生变化的土壤污染水平相似的水平上检测到耐受能力的变化(A. Frostegård、A. Tunlid 和 E. Bååth,Appl. Environ. Microbiol. 59: 3605-3617,1993)。