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Biochemical parameters and bacterial species richness in soils contaminated by sludge-borne metals and remediated with inorganic soil amendments

机译:被污泥传播的金属污染并用无机土壤改良剂修复的土壤中的生化参数和细菌物种丰富度

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The effectiveness of two amendments for the in situ remediation of a Cd- and Ni-contaminated soil in the Louis Fargue long-term field experiment was assessed. In April 1995, one replicate plot (S1) was amended with 5% w/w of beringite (B), a coal fly ash (treatment S1 + B), and a second plot with 1% w/w zerovalent-Fe iron grit (SS) (treatment S1+SS), with the aim of increasing metal sorption and attenuating metal impacts. Long-term responses of daily respiration rates, microbial biomass, bacterial species richness and the activities of key soil enzymes (acid and alkaline phosphatase, arylsulfatase, β-glucosidase, urease and protease activities) were studied in relation to soil metal extractability. Seven years after initial amendments, the labile fractions of Cd and Ni in both the S1 + B and S1+SS soils were reduced to various extents depending on the metal and fractions considered. The soil microbial biomass and respiration rate were not affected by metal contamination and amendments in the S1 + B and S1+SS soils, whereas the activity of different soil enzymes was restored. The SS treatment was more effective in reducing labile pools of Cd and Ni and led to a greater recovery of soil enzyme activities than the B treatment. Bacterial species richness in the S1 soil did not alter with either treatment. It was concluded that monitoring of the composition and activity of the soil microbial community is important in evaluating the effectiveness of soil remediation practices.
机译:评估了两种改良剂在路易·法格(Louis Fargue)长期野外实验中原位修复Cd和Ni污染土壤的有效性。 1995年4月,对一个重复样区(S1)进行了修改,其中添加了5%w / w的针脚石(B),一种粉煤灰(处理S1 + B),第二个样地使用了1%w / w的零价铁砂粒(SS)(处理S1 + SS),目的是增加金属的吸附并减轻金属的撞击。研究了日呼吸速率,微生物生物量,细菌物种丰富度以及关键土壤酶(酸和碱性磷酸酶,芳基硫酸酯酶,β-葡萄糖苷酶,脲酶和蛋白酶活性)与土壤金属可提取性的长期响应。初步修正后的七年,根据所考虑的金属和分数,S1 + B和S1 + SS土壤中Cd和Ni的不稳定分数均有不同程度的降低。土壤微生物生物量和呼吸速率不受金属污染和S1 + B和S1 + SS土壤改良剂的影响,而不同土壤酶的活性得以恢复。与B处理相比,SS处理在减少不稳定的Cd和Ni沉积方面更有效,并且导致土壤酶活性的恢复更大。两种处理均未改变S1土壤中细菌的丰富度。结论是,监测土壤微生物群落的组成和活性对于评估土壤修复措施的有效性很重要。

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