• ISSN 1008-505X
  • CN 11-3996/S

不同秸秆还田方式下复合菌剂M44对寒旱区秸秆的促腐机制及培肥效应

Mechanisms of microbial agent M44 for enhancing straw decomposition and soil fertility under different straw returning methods in a cold and arid region

  • 摘要:
    目的 为破解寒旱区还田秸秆腐解问题,通常采用低温高效降解微生物菌剂来促进秸秆的高效腐解。探究不同秸秆还田方式配施菌剂M44对田间秸秆的促腐效果及作用机制,为秸秆促腐菌剂科学施用提供理论依据和技术支持。
    方法 采用改进的尼龙网袋秸秆还田原位微区降解试验方法进行研究。首先在田间进行裂区设计,主区为深翻秸秆还田(DPR)、深松混拌秸秆还田(SSR)、免耕覆盖秸秆还田(NTR),副区为施用菌剂(M44)和不施用菌剂(CK)。将20 g秸秆、1 kg土壤和0.04 g M44菌剂混合均匀,装入尼龙网袋中,埋入本小区,每个小区埋入5个尼龙袋,总培养时间为320 天。周期性取样测定秸秆降解率、养分释放率和土壤胞外酶活性及土壤养分含量等指标。
    结果 相比于不施菌剂对照,施用菌剂M44分别显著提高了秸秆降解率、木质纤维素降解率、养分释放率2.33~9.81、3.10~14.81和3.55~18.59个百分点,培养0~185天的秸秆降解效率的每日增幅高达28.40%~71.83%;各时期施用菌剂M44处理土壤脲酶、蔗糖酶、碱性磷酸酶、过氧化氢酶活性分别平均提高了0.39、0.33、0.28、0.35 mg/(g·d),β-木糖苷酶、β-葡萄糖苷酶、乙酰氨基葡萄糖苷酶活性平均分别提高了11.79、18.28、3.12 nmol/(g·h) (P<0.05)。DPR+M44和SSR+M44的促腐培肥效果优于NRT+M44,秸秆降解率分别提高了10.66~25.60和8.69~26.08个百分点,秸秆碳、氮和磷素释放率分别提高了3.55~18.59、6.35~7.58和6.99~11.36个百分点 (P<0.05)。Mantel检验结果表明,土壤蔗糖酶、碱性磷酸酶、β-1,4-木糖苷酶活性与秸秆降解和秸秆养分释放呈显著正相关 (P<0.05)。结构方程模型分析显示,土壤脲酶、碱性磷酸酶和亮氨酸氨基肽酶可直接促进秸秆腐解。进一步路径分析表明,土壤胞外酶活性通过直接促进秸秆腐解,间接介导秸秆养分释放,秸秆养分释放也可由土壤脲酶、β-1,4-木糖苷酶直接驱动,而秸秆养分释放可提高土壤养分水平。
    结论 各种秸秆还田方式下,施用菌剂M44均可促进秸秆降解,缩短秸秆降解时间,提高秸秆养分释放率,增加土壤酶活性和养分含量,且在深翻秸秆还田和深松混拌秸秆还田方式下效果更佳。

     

    Abstract:
    Objectives To resolve the challenge of straw decomposition in cold and arid regions, microbial agents with both low - temperature tolerance and high efficiency are commonly used to promote the efficient decomposition of straw. We investigated the mechanism of microbial agents M44 on accelerating straw decomposition under different straw returning methods.
    Methods A split-plot design was adopted in a field experiment, the main plots included deep plowing with straw return (DPR), subsoiling with straw mixing return (SSR), and no-tillage with straw mulching return (NTR), and the subplots were with or without application of microbial agent M44 (CK, and M44). At the same time, 20 g of straw, 1 kg of soil from the treated plots, and 0.04 g of M44 microbial agent were thoroughly mixed, placed into nylon mesh bags, and buried in the corresponding plots, with a total incubation period of 320 days. Periodically, samples were collected to determine indices such as straw degradation rate, nutrient release rate, soil extracellular enzyme activity, and soil nutrient content.
    Results Compared with the CKs, the M44 treatments significantly increased the average straw degradation rate, lignocellulose degradation rate, and nutrient release rate by 2.33−9.81, 3.10−14.81, and 3.55−18.59 percentage points, respectively. And the enhancement of straw degradation efficiency during 0−185 days were as high as 28.40%−71.83% per day. Compared with the CKs, the M44 treatments increased the activities of soil urease, sucrase, alkaline phosphatase, and catalase by average of 0.39, 0.33, 0.28, and 0.35 mg/(g·d), respectively. they also enhanced the activities of soil β-1,4-xylosidase, β-1,4-glucosidase, and N-acetylglucosaminidase by an average of 11.79, 18.28, and 3.12 nmol/(g·h) throughout the whole incubation period, respectively (P<0.05). The straw decomposition and soil fertility improvement effects of DPR+M44 and SSR+M44 were superior to those of NRT+M44, as evidenced by a higher straw degradation rate (10.66−25.60 and 8.69−26.08 percentage points) and release rates of straw carbon, nitrogen, and phosphorus (3.55−18.59, 6.35−7.58, and 6.99−11.36 percentage points) (P<0.05). Structural equation modeling analysis revealed that urease, alkaline phosphatase, and leucine aminopeptidase directly promoted straw degradation. Further path analysis indicated that soil extracellular enzyme activities indirectly mediated straw nutrient release by directly accelerating straw degradation. Additionally, straw nutrient release was directly driven by soil urease and β-1,4-xylosidase, while nutrient release from straw enhanced soil nutrient levels.
    Conclusion Under various straw return methods, the application of microbial agent M44 can accelerate straw degradation, shorten the degradation time, enhance the nutrient release rate from straw, increase soil enzyme activities and nutrient contents, with even more pronounced effects observed under deep plowing with straw return and subsoiling with straw mixing return methods.

     

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