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Leaf litter C and N cycling from a deciduous permanent crop

机译:落叶永久性作物的凋落物C和N循环

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Our understanding of leaf litter carbon (C) and nitrogen (N) cycling and its effects on N management of deciduous permanent crops is limited. In a 30-day laboratory incubation, we compared soil respiration and changes in mineral N [ammonium (NH4+-N) + nitrate (NO3--N)], microbial biomass nitrogen (MBN), total organic carbon (TOC) and total non-extractable organic nitrogen (TON) between a control soil at N-15 natural abundance (N-15=1.08 parts per thousand) without leaf litter and a treatment with the same soil, but with almond (Prunus dulcis (Mill.) D.A. Webb) leaf litter that was also enriched in N-15 (N-15=213 parts per thousand). Furthermore, a two-end member isotope mixing model was used to identify the source of N in mineral N, MBN and TON pools as either soil or leaf litter. Over 30d, control and treatment TOC pools decreased while the TON pool increased for the treatment and decreased for the control. Greater soil respiration and significantly lower (p0.05) mineral N from 3 to 15d and significantly greater MBN from 10 to 30d were observed for the treatment compared to the control. After 30d, soil-sourced mineral N was significantly greater for the treatment compared to the control. Combined mineral N and MBN pools derived from leaf litter followed a positive linear trend (R-2=0.75) at a rate of 1.39 g N g(-1) soil day(-1). These results suggest early-stage decomposition of leaf litter leads to N immobilization followed by greater N mineralization during later stages of decomposition. Direct observations of leaf litter C and N cycling assists with quantifying soil N retention and availability in orchard N budgets.
机译:我们对叶片凋落物碳(C)和氮(N)循环及其对落叶永久性作物氮素管理的影响的理解是有限的。在为期30天的实验室孵化中,我们比较了土壤呼吸和矿物质氮[铵(NH4 + -N)+硝酸盐(NO3--N)],微生物生物量氮(MBN),总有机碳(TOC)和总氮的变化。在没有叶子凋落物的N-15自然丰度(N-15 = 1.08千份)的对照土壤与用相同土壤但用杏仁(李子(DA)Webb)处理的土壤中可提取的有机氮(TON) )的叶子凋落物也富含N-15(N-15 =千分之213)。此外,使用两端成员同位素混合模型来确定矿物质N,MBN和TON池中的N来源是土壤还是叶子凋落物。在30天以上,对照和治疗的TOC池减少,而治疗的TON池增加,而对照的TOC池减少。与对照组相比,处理后的土壤呼吸更大,从3到15d显着降低(p <0.05)矿质N,从10到30d显着提高MBN。 30天后,与对照相比,处理的土壤来源矿物质氮显着更大。源自叶片凋落物的N和MBN矿物质组合池以1.39 g N g(-1)土壤日(-1)的速率呈线性正趋势(R-2 = 0.75)。这些结果表明,叶片凋落物的早期分解导致固氮作用,随后在分解的后期产生更大的氮矿化作用。对叶子凋落物C和N循环的直接观察有助于量化果园N预算中土壤氮的保留和有效性。

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