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首页> 外文期刊>Soil Biology & Biochemistry >Changes in microbial biomass, CH4 and CO2 emissions, and soil carbon content by fly ash co-applied with organic inputs with contrasting substrate quality under changing water regimes.
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Changes in microbial biomass, CH4 and CO2 emissions, and soil carbon content by fly ash co-applied with organic inputs with contrasting substrate quality under changing water regimes.

机译:粉煤灰中微生物量,CH 4 和CO 2 的排放量以及土壤碳含量的变化与有机物投入共同作用,在不同水质条件下底物质量形成对比。

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摘要

Application of fine-textured and Ca-rich fly ash may be helpful in enhancing soil carbon content via protecting soil organic C (SOC) by organo-mineral complexation and via reducing CO2 emission by carbonation (e.g. formation of CaCO3). However, very limited information is available on the effects of fly ash application on gases loss of C and soil C content. In this study, to estimate the potential use of fly ash as a soil amendment for SOC enhancement purposes, the effects of fly ash application (0, 5, and 10 w/w %) on microbial biomass C (MBC), CH4 and CO2 emissions, and on soil C content were investigated. A 60-days incubation experiment was conducted with an acidic soil in the presence of organic input (pig manure compost, PMC; hairy vetch, HV) with contrasting substrate quality under changing water regime from water-logged to unsaturated via a transition period. Fly ash application did not affect MBC under water-unsaturated conditions, but reduced (P<0.01) microbial growth under water-logged conditions, probably due to the increased solubility of a certain toxic element such as arsenic under the anaerobic conditions. Across the 60 days of incubation, the CO2 emission was reduced by fly ash regardless of organic input by 20.5-41.3%; meanwhile, a decline of CH4 emission by fly ash application was significant (P<0.05) only in the HV treatment. Overall, fly ash application slowed down gases C loss and increased soil C content, probably due to the retardation of CH4 and CO2 emission as well as the addition of C contained in the fly ash. Biochemical (inhibition of microbial activity), chemical (formation of CaCO3 via carbonation), and physical (restriction of gas diffusion) mechanisms were suggested for the fly ash effects.
机译:施用质地细巧且富含Ca的粉煤灰,可能有助于通过有机矿物络合保护土壤有机碳(SOC),以及通过碳化作用减少CO 2 的排放,从而提高土壤碳含量。的CaCO 3 )。但是,关于粉煤灰的施用对碳的气体损失和土壤碳含量的影响的信息非常有限。在这项研究中,为了评估粉煤灰作为土壤改良剂以增强SOC的潜在用途,粉煤灰施用量(0、5和10 w / w%)对微生物生物量C(MBC)的影响,CH 4 和CO 2 的排放以及土壤中的碳含量。在有机输入物(猪粪堆肥,PMC;多毛v子,HV)存在下,在酸性土壤上进行了60天的温育实验,对比了在从过渡期到浸水到不饱和的水域变化下,基质质量​​的差异。粉煤灰的施用在水不饱和条件下不影响MBC,但在水淹条件下微生物生长减少(P <0.01),这可能是由于某些有毒元素(如砷)在厌氧条件下的溶解度增加所致。在整个培养的60天中,无论有机物投入如何,粉煤灰均将CO 2 排放量降低了20.5-41.3%。同时,仅在HV处理中,粉煤灰施用CH 4 的排放量下降显着(P <0.05)。总体而言,粉煤灰的施用减缓了气体C的流失并增加了土壤C的含量,这可能是由于CH 4 和CO 2 的排放受阻以及添加了C所致在粉煤灰中。提出了粉煤灰效应的生化机制(抑制微生物活性),化学机制(通过碳酸化形成CaCO 3 )和物理机制(限制气体扩散)。

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