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Decomposition of heavy metal contaminated nettles (Urtica dioica L.) in soils subjected to heavy metal pollution by river sediments

机译:河流沉积物对重金属污染荨麻(Urtica dioica L.)的土壤分解

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Two incubation experiments were conducted to evaluate differences in the microbial use of non-contaminated and heavy metal contaminated nettle (Urtica dioica L.) shoot residues in three soils subjected to heavy metal pollution (Zn, Pb, Cu, and Cd) by river sediments. The microbial use of shoot residues was monitored by changes in microbial biomass C, biomass N, biomass P, ergosterol, N mineralisation, CO2 production and O-2 consumption rates. Microbial biomass C, N, and P were estimated by fumigation extraction. In the non-amended soils, the mean microbial biomass C to soil organic C ratio decreased from 2.3% in the low metal soil to 1.1% in the high metal soils. In the 42-d incubation experiment, the addition of 2% nettle residues resulted in markedly increased contents of microbial biomass P (+240%), biomass C (+270%), biomass N (+310%), and ergosterol (+360%). The relative increase in the four microbial properties was similar for the three soils and did not show any clear heavy metal effect. The contents of microbial biomass C, N and P and ergosterol contents declined approximately by 30% during the incubation as in the non-amended soils. The ratios microbial biomass C to N, microbial biomass C to P, and ergosterol to microbial biomass C remained constant at 5.2, 26, and 0.5%, respectively. In the 6-d incubation experiment, the respiratory quotient CO2/O-2 increased from 0.74 in the low metal soil to 1.58 in the high metal soil in the non-amended soils. In the treatments amended with 4% nettle residues, the respiratory quotient was constant at 1.13, without any effects of the three soils or the two nettle treatments. Contaminated nettle residues led generally to significantly lower N mineralisation, CO2 production and O-2 consumption rates than non-contaminated nettle residues. However, the absolute differences were small. (c) 2006 Elsevier Ltd. All rights reserved.
机译:进行了两个温育实验,以评估在三种沉积物受到河流沉积物重金属污染(Zn,Pb,Cu和Cd)的三种土壤中,无污染和重金属污染的荨麻(Urtica dioica L.)枝条残留在微生物利用上的差异。 。通过微生物生物量C,生物量N,生物量P,麦角固醇,氮矿化,CO2产生和O-2消耗率的变化来监测芽残留物的微生物利用。通过熏蒸提取估算微生物的生物量C,N和P。在未改良土壤中,平均微生物生物量碳与土壤有机碳的比率从低金属土壤的2.3%降至高金属土壤的1.1%。在42天的温育实验中,添加2%的荨麻残留物导致微生物生物量P(+ 240%),生物量C(+ 270%),生物量N(+ 310%)和麦角固醇(+ 360%)。三种土壤的四种微生物特性的相对增加是相似的,并且没有显示任何明显的重金属效应。像在未改良的土壤中一样,在孵化过程中微生物生物量碳,氮和磷的含量以及麦角固醇的含量下降了约30%。微生物生物量C与N的比率,微生物生物量C与P的比率以及麦角固醇与微生物生物量C的比率分别保持恒定,分别为5.2%,26%和0.5%。在6天的温育实验中,呼吸商CO2 / O-2从低金属土壤中的0.74增加到非改良土壤中高金属土壤中的1.58。在用4%荨麻残留物修正的处理中,呼吸商恒定为1.13,而三种土壤或两种荨麻处理均无影响。受污染的荨麻残留物通常比未受污染的荨麻残留物显着降低氮矿化,CO2产生和O-2消耗率。但是,绝对差异很小。 (c)2006 Elsevier Ltd.保留所有权利。

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