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Long term effects of heavy metal enriched sewage sludge disposal in agriculture on soil biota.

机译:农业中重金属富集的污水污泥处置对土壤生物的长期影响。

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Long term effects of heavy metal pollution caused by decennial sewage sludge disposal (12 t ha-1 yr1) from 1980 to 1990 on soil biota of an experimental field in Northern Germany were investigated 16 years after the last sludge application. The plots still exist to date as permanent pasture. The consequences of the soil treatment were shown by means of heavy metal concentrations of soil and earthworms. Additional effects on soil micro-organisms by enzyme activities were investigated. The disposal of heavy metal enriched sewage sludge caused increased soil heavy metal concentrations compared to mineral fertilised control plots. The increased soil heavy metal concentration was transferred to soil organisms. The earthworm biomass from the sewage sludge treated plots bore increased heavy metal concentrations. Cadmium showed the highest transfer factor from soil to earthworms. The amount of transfer into biomass is specific for each element and depends on heavy metal soil concentration. Despite the higher heavy metal concentration of earthworm biomass, the number of earthworms was increased in soil of the sewage sludge treated plots which is attributed to the enhanced soil organic matter (SOM) concentration. The number of earthworms did not correlate significantly with SOM but the weight of earthworms did. The microbial activities of dehydrogenase and alkaline phosphatase enzymes were reduced in soil of the sewage sludge treated plots compared to the control plots. The enzyme activities of cellulase and protease however were enhanced by the application of heavy metal enriched sewage sludge compared to the control plots. One the one hand sewage sludge addition enhanced soil organic matter concentration; on the other hand its microbial decomposition was retarded by toxic effects of heavy metals due to reduced enzyme activities.
机译:1980年至1990年,十年来污泥处置(12 t ha -1 yr 1 )引起的重金属污染对德国北部一个试验场的土壤生物区系的长期影响在最后一次污泥施用后16年进行了调查。迄今为止,这些土地仍作为永久性牧场存在。土壤处理的后果通过土壤和earth中重金属的浓度来显示。研究了酶活性对土壤微生物的其他影响。与矿物施肥控制区相比,富含重金属的污水污泥的处理导致土壤重金属浓度增加。增加的土壤重金属浓度转移到土壤生物中。来自污水污泥处理区的worm生物质的重金属浓度增加。镉显示出从土壤到earth的最高转移因子。转移到生物质中的量对于每种元素都是特定的,并取决于重金属土壤的浓度。尽管of生物质的重金属浓度较高,但污水污泥处理区土壤中worm的数量有所增加,这归因于土壤有机质(SOM)浓度的提高。 S的数量与SOM没有显着相关,但but的重量却有。与对照样区相比,污水污泥处理区的土壤中脱氢酶和碱性磷酸酶的微生物活性降低。然而,与对照样地相比,施用富含重金属的污水污泥可增强纤维素酶和蛋白酶的酶活性。一方面污泥的添加提高了土壤有机质的浓度;另一方面另一方面,由于酶活性降低,重金属的毒性作用阻碍了其微生物的分解。

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