• ISSN 1008-505X
  • CN 11-3996/S

秸秆和畜禽粪便对农田土壤氮初级转化和固持特征的影响

Gross N transformation and retention characteristics of cropland soil as affected by straw and livestock manure application

  • 摘要:
    目的 研究秸秆还田和畜禽粪便施用对农田土壤氮初级转化特征的影响,可以深入理解土壤中氮素的供应和保持机理,对于合理施用有机物料以培肥土壤具有重要意义。
    方法 采用室内培养试验的方法,供试土壤为农田黑土,供试有机物料为猪粪、鸡粪和玉米秸秆,以不添加有机物料处理为对照。采用15N同位素成对标记技术,在25°C和60%WHC水分条件下培养,在培养开始后的0、1、2、4、7天,破坏性取样测定土壤中的无机氮、有机氮含量及其15N丰度,并采用FLUAZ数值优化模型计算有机氮初级矿化速率、初级硝化速率、铵态氮固定速率和硝态氮固定速率。
    结果 猪粪、鸡粪和秸秆处理土壤有机氮初级矿化速率为N 7.86、N 6.23、N 6.79 mg/(kg∙d),分别较对照的N 2.12 mg/(kg∙d) 增加了2.71、1.94和2.20倍;氮初级固定速率为N 2.85、N 4.11、N 10.65 mg/(kg∙d),较对照的N 1.23 mg/(kg∙d) 增加了1.32、2.34和7.66倍。猪粪和鸡粪处理土壤有机氮初级矿化速率高于无机氮固定速率,表现为净氮矿化,秸秆处理土壤有机氮初级矿化速率小于无机氮固定速率,表现为净氮固定。土壤微生物对铵态氮的固定速率显著大于硝态氮,对无机氮固定总速率的贡献达到72%~99%。添加猪粪和鸡粪后铵态氮固定速率分别增加至对照处理的2.36倍和3.40倍,但是对硝态氮固定没有影响,添加秸秆同时显著促进了铵态氮和硝态氮的生物固定,其中铵态氮固定速率和硝态氮固定速率分别增加至对照处理的6.35和101倍。添加猪粪和鸡粪后土壤初级硝化速率分别增加至对照处理的2.13倍和1.35倍,而添加秸秆后土壤初级硝化速率降低至N 0.68 mg/(kg∙d)。添加猪粪和鸡粪处理土壤初级硝化速率与铵态氮固定速率之比 (GN/INH4) 大于1,分别为4.36和1.92,而秸秆处理土壤初级硝化速率与铵态氮固定速率之比 (0.09) 小于1。
    结论 秸秆虽然可以促进土壤有机氮的矿化,但同时也能显著促进微生物对无机氮的固定,由于对有机氮初级矿化率的促进程度小于无机氮固定速率,有利于无机氮的固持。施用猪粪和鸡粪土壤氮的初级矿化率高于无机氮,特别是铵态氮的生物固定率,表现为氮净矿化,且由于GN/INH4值大于1,可能导致硝态氮在土壤中的积累和向环境的扩散。

     

    Abstract:
    Objectives Studying the effects of straw and livestock manure application on the gross N transformation characteristics in cropland soil can provide a deep understanding of the mechanisms of N supply and retention in soil, which is of great significance for the rational application of organic materials to improve soil fertility.
    Methods Indoor incubation experiment was used for the research. The test soil was black soil, and the test organic materials were pig manure (PM), chicken manure (CM), and maize straw (MS), the treatment without organic materials addition was used as the control (CK). The soil was paired labelled with 15N isotope and incubated for one week at 25°C and 60% moisture. On the 0, 1, 2, 4, and 7 day of incubation, soil samples were collected for measurement of inorganic and organic nitrogen contents, and their 15N abundances. The rates of gross N mineralization, gross nitrification, NH4+ immobilization and NO3 immobilization were calculated using FLUAZ numerical optimization model.
    Results The gross N mineralization rate of PM, CM, and MS treatment was N 7.86, N 6.23, and N 6.79 mg/(kg∙d), which was 2.71, 1.94, and 2.20 golds higher than that of CK N 2.12 mg/(kg∙d). The gross N immobilization rate of PM, CM, and MS treatment was 2.85, 4.11, 10.65 mg N/(kg∙d), which was 1.32, 2.34, and 7.66 folds of that of CK N 1.23 mg/(kg∙d). The gross N mineralization rates of PM and CM treatments were greater than the gross N immobilization rates, leading to net N mineralization in soil, while the reverse was true for MS, leading to the net N immobilization in soil. The immobilization rate of NH4+ by soil microorganisms was significantly higher than that of NO3, contributing 72%–99% of total inorganic N immobilization rate. Livestock manure and maize straw showed different immobilization effect on soil inorganic N. Compared with CK, PM and CM were recorded 2.36 and 3.40 times higher NH4+ immobilization rates, but similar NO3 immobilization rates; MS was recorded 6.35 and 101 times higher NH4+ and NO3 immobilization rates. The gross nitrification rate of CK was N 5.78 mg/(kg∙d), PM and CM treatments increased that to 2.13 and 1.35 times higher, whereas MS treatment decreased that to N 0.68 mg/(kg∙d). The ratios of gross nitrification to NH4+ immobilization rate (GN/INH4 ratio) in PM and CM treatments were larger than 1, at 4.36 and 1.92, respectively, while the ratio in MS treatment was 0.09, less than 1.
    Conclusions Although straw can promote the mineralization of soil organic nitrogen, it also enhances the immobilization of inorganic nitrogen by microorganisms, resulting in a net immobilization of nitrogen in the soil. This is because the gross mineralization rate of organic nitrogen is lower than the immobilization rate of inorganic nitrogen, which favors the retention of inorganic nitrogen. When pig manure and chicken manure are applied, the gross mineralization rate of soil nitrogen exceeds the rate of inorganic nitrogen immobilization, particularly the biological immobilization rate of ammonium nitrogen, leading to net nitrogen mineralization. Moreover, due to the GN/INH4 ratio (ratio of gross nitrification rate to ammonium nitrogen immobilization rate) being greater than 1, potentially causing nitrate nitrogen accumulation in the soil and nitrogen diffusion from the soil into the environment.

     

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