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首页> 外文期刊>Soil Biology & Biochemistry >Frequent addition of wheat straw residues to soil enhances carbon mineralization rate
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Frequent addition of wheat straw residues to soil enhances carbon mineralization rate

机译:经常向土壤中添加小麦秸秆残留物可提高碳矿化率

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In many ecosystems, residues are added frequently to soil, in the form of root turnover and litter fall. However, in most studies on residue decomposition, residues are added once and there are few studies that have investigated the effect of frequent residue addition on C mineralization and N dynamics. To close this knowledge gap, we mixed mature wheat residue (C/N 122) into soil at a total rate of 2% w/w once at the start (R1x), every 16 days (R4x), every 8 days (R8x) or every 4 days (R16x). Un-amended soil served as control. All treatments were mixed every 4 days. Soil respiration was measured continuously over the 80-day incubation. Inorganic N, K2SO4-extractable C and N, chloroform-labile C and N (as an estimate of microbial biomass C and N), soil pH and microbial community composition were assessed every 16 days. Increasing frequency of residue addition increased C mineralization per g residue. Compared to R1x, cumulative respiration per g residue at the end of the incubation (day 80) was increased by 57, 82 and 92% in R4x, R8x and R16x, respectively. The largest differences in soil respiration per g residue occurred in the first 30 days. Despite large increases in cumulative respiration, frequent residue addition did not affect inorganic N or K2SO4-extractable N concentrations, chloroform-labile C and N or soil pH. Compared to the control, all residue treatments resulted in increases in chloroform-labile C and N and soil pH but decreased inorganic and K2SO4-extractable N. Microbial community composition was affected by residue addition, however there were no consistent differences among residue treatments. It is concluded that experiments with single residue additions may underestimate residue decomposition rates in the field. The increased C mineralization caused by frequent residue additions does not appear to be due to an increased microbial biomass or changes in microbial community composition, but rather to increased C mineralization per unit biomass.
机译:在许多生态系统中,残留物经常以根周转和凋落物的形式添加到土壤中。然而,在大多数关于残留物分解的研究中,仅添加一次残留物,很少有研究调查频繁添加残留物对碳矿化和氮动力学的影响。为了弥补这一知识鸿沟,我们在开始时(R1x),每16天(R4x),每8天(R8x)以2%w / w的总比率将成熟小麦残渣(C / N 122)混合到土壤中。或每4天(R16x)。未改良的土壤作为对照。每4天混合所有治疗。在培养80天的过程中连续测量土壤呼吸。每16天评估一次无机N,可通过K2SO4萃取的C和N,对氯仿不稳定的C和N(作为估计微生物生物量C和N),土壤pH值和微生物群落组成的指标。残渣添加频率的增加增加了每克残渣的C矿化度。与R1x相比,R4x,R8x和R16x在培养结束(第80天)时每g残留的累积呼吸分别增加了57%,82%和92%。每克残留物的土壤呼吸最大差异发生在前30天。尽管累积呼吸量大大增加,但频繁添加残留物不会影响无机氮或K2SO4可提取的氮浓度,对氯仿不稳定的C和N或土壤pH值。与对照相比,所有残留物处理均增加了对氯仿不稳定的C和N以及土壤pH值,但降低了无机和K2SO4可提取的N。微生物群落组成受残留物添加的影响,但是残留物处理之间没有一致的差异。结论是添加单一残留物的实验可能会低估该领域的残留物分解率。频繁添加残留物引起的碳矿化增加似乎不是由于微生物生物量增加或微生物群落组成的变化,而是由于每单位生物量碳矿化增加。

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