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Initial results from a long-term, multi-site field study of the effects on soil fertility and microbial activity of sludge cakes containing heavy metals

机译:长期,多地点实地研究对含重金属污泥饼对土壤肥力和微生物活性影响的初步结果

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In a long-term study of the effects on soil fertility and microbial activity of heavy metals contained in sewage sludges, metal-rich sludge cakes each with high Zn, Cu or Cd concentrations were applied annually for 4 years (1994-1997) to nine sites throughout Britain. These sites were selected to represent agricultural soils with a range of physical and chemical properties, typical of those likely to be amended with sewage sludge. The aim was to establish individual total Zn (approx. 60-150 mg kg~(-1)), total Cu (approx. 15-200 mg kg~(-1)) and total Cd (approx. 0.2-4 mg kg~(-1)) metal dose-response treatments at each site. Sludges with low metal concentrations were added to all treatments to achieve as constant an addition of organic matter as possible. Across the nine sites, soil pH was the single most important factor controlling Zn (P 0.001; r2 = 92%) and Cd extracted with 1 M NH_4NO_3 (P 0.001; r = 72%), and total iron content the most important factor controlling Cu extracted with 1 M NH_4NO_3 (P 0.001; r~2 = 64%). There were also positive relationships (P 0.001) between soil organic carbon (C) concentrations and soil biomass C and respiration rates across the nine sites. Oxidation of sludge C following land application resulted in approximately 45% of the digested sludge cake C and approximately 64% of the 'raw' sludge cake C being lost by the end of the 4-year application period. The sludge cake applications generally increased soil microbial biomass C and soil respiration rates, whilst most probable numbers of clover Rhi:obium were generally unchanged. Overall, there was no evidence that the metal applications were damaging soil microbial activity in the short term after the cessation of sludge cake addition.
机译:在对污水污泥中重金属对土壤肥力和微生物活性的影响的长期研究中,每年施用4年(1994-1997年)的高含锌污泥饼(锌,铜或镉的含量为9到9)英国各地。选择这些地点是为了代表具有各种物理和化学特性的农业土壤,典型的土壤可能会被污水污泥修正。目的是建立单独的总Zn(约60-150 mg kg〜(-1)),总Cu(约15-200 mg kg〜(-1))和Cd(约0.2-4 mg kg) 〜(-1))在每个位置进行金属剂量反应治疗。将低金属浓度的污泥添加到所有处理中,以尽可能恒定地添加有机物。在这9个地点中,土壤pH值是控制Zn(P <0.001; r2 = 92%)和用1 M NH_4NO_3萃取Cd的最重要因素(P <0.001; r = 72%),总铁含量是最重要的控制用1 M NH_4NO_3提取的Cu的因子(P <0.001; r〜2 = 64%)。在这9个地点中,土壤有机碳(C)浓度与土壤生物量C和呼吸速率之间也存在正相关关系(P <0.001)。土地施用后污泥C的氧化导致大约45%的消化污泥饼C和大约64%的“原始”污泥饼C在4年施用期结束时流失。污泥饼的施用通常会增加土壤微生物生物量C和土壤呼吸速率,而三叶草Rhi:ob的最可能数量通常保持不变。总体而言,没有证据表明在停止添加污泥饼后短期内金属施用会损害土壤微生物活性。

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