有机碳源质量对农田土壤反硝化产物特征的影响机制
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土壤与农业可持续发展国家重点实验室(中国科学院南京土壤研究所)

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Mechanisms of Gaseous Nitrogen Emissions from Denitrification in Agricultural Soils as Affected by Organic Material Quality
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State Key Laboratory of Soil and Sustainable Agriculture,Institute of Soil Science,Chinese Academy of Sciences

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    摘要:

    反硝化过程受碳源数量和质量特征共同影响。为揭示不同质量有机碳源对农田土壤反硝化N2O和N2排放及N2O/(N2O+N2)比值的影响机制,本研究以太湖地区的稻-麦轮作农田(稻田)、设施蔬菜地(菜地)土壤为对象,施用不同碳氮比的小麦(WS)、水稻(RS)和玉米秸秆(MS)及其对应生物质炭(WSB、RSB和MSB);并设置相应的秸秆和生物质炭淋洗液处理(LWS、LRS、LMS、LWSB、LRSB和LMSB),利用Robot自动气体分析系统、qPCR以及傅里叶变换离子回旋共振质谱(FT-ICR MS)分别解析土壤气态氮排放及N2O/(N2O+N2)比值、反硝化功能基因丰度及淋洗液溶解性有机质(DOM)分子组成特征。结果表明,在稻田土壤中,秸秆和生物质炭施用提高了nirS和nirK基因丰度,显著增加N2O排放及N2O/(N2O+N2)比值。秸秆和生物质炭的淋洗液同样促进N2O排放,其中LMS处理增幅最高,达242.4%;秸秆及其淋洗液施用后(nirS+nirK)/nosZ比值显著高于生物质炭处理,导致更高的N2O/(N2O+N2)比值。在菜地土壤中,秸秆和生物质炭施用显著增强N2O排放,该效应在淋洗液处理下更为显著。其中LWS处理的N2O累积排放量最高,达268.57 mg·kg?1,N2O/(N2O+N2)比值为0.87,这主要是由于高NO3?-N背景下nosZ基因丰度降低,削弱了N2O还原潜力。FT-ICR MS分析表明,秸秆淋洗液DOM以木质素类和稠环芳烃类等难降解组分为主,在LWS、LRS和LMS中的相对丰度之和分别为88.43%、86.90%和85.03%;难降解组分丰度和芳香性指数(AImod)的升高显著(P < 0.05)提高了N2O排放和N2O/(N2O+N2)比值。生物质炭淋洗液DOM中脂类和蛋白质/氨基糖类等易降解组分占主导,其中蛋白质/氨基糖类化合物的相对丰度与N2累积排放量呈显著正相关(P < 0.05)。综上,有机碳源的质量特征是调控农田土壤反硝化气态产物分配的关键因素。农田有机物料管理应关注碳源化学组成优化,并协同调控pH与NO3?-N水平,在实现高NO3?-N去除率的同时降低N2O/(N2O+N2)比值,促进反硝化产物向N2转化,从而推动农田活性氮减排与氮素良性循环。

    Abstract:

    【Objective】Denitrification in agricultural soils is jointly regulated by the quantity and quality of organic carbon materials. This study aimed to reveal how organic materials of different quality affect denitrification-derived gaseous nitrogen (N) emissions and the N2O/(N2O+N2) product ratio in typical agricultural soils, and to elucidate the underlying mechanisms. 【Method】Paddy soil from a rice–wheat rotation field and greenhouse vegetable soil in the Taihu Lake region were collected as test soils, to which six types of exogenous organic carbon with contrasting C/N ratios were applied. The treatments include wheat (WS), rice (RS) and maize straw (MS) and their corresponding biochars (WSB, RSB, and MSB). In parallel, the respective straw- and biochar-derived leachates (LWS, LRS, LMS, LWSB, LRSB, and LMSB) were added, and a Robot automatic gas analysis system, qPCR and Fourier transform ion cyclotron resonance mass spectrometry (FT-ICR MS) were employed to quantify gaseous N emissions and the N2O/(N2O+N2) product ratio, denitrification functional genes, and the molecular composition of dissolved organic matter (DOM) in the leachates.【Result】The results showed that, in paddy soil, both straw and biochar increased the abundances of nirS and nirK, leading to significantly higher cumulative N2O emissions and N2O/(N2O+N2) ratios. Their leachates similarly enhanced N2O production, with LMS showing the greatest increase of 242.4%. Straw and its leachates exhibited substantially higher (nirS+nirK)/nosZ ratios than biochar and its leachates, corresponding to higher N2O/(N2O+N2) ratios. In vegetable soil, straw and biochar also increased N2O emissions, and this effect was further pronounced when their leachates were applied. The LWS treatment showed the greatest cumulative N2O emission (268.57 mg kg?1) and an N2O/(N2O+N2) ratio of 0.87, attributable to high background NO3?-N, which suppressed nosZ abundance and N2O reduction. FT-ICR MS revealed that straw-leached dissolved organic matter (DOM) was dominated by recalcitrant lignin-like and condensed aromatic compounds, which accounted for 88.43%, 86.90% and 85.03% of the DOM molecular abundance in LWS, LRS and LMS, respectively. The increase in relative abundance of condensed aromatics and the aromaticity index (AImod) significantly (P < 0.05) increased both N2O emissions and the N2O/(N2O+N2) ratio. In contrast, biochar-leached DOM contained more labile lipid-like and protein/amino sugar-like compounds, and the relative abundance of protein/amino sugar molecules was positively associated with cumulative N2 emission (P < 0.05). 【Conclusion】In summary, the qualitative properties of organic carbon inputs are a key determinant of denitrification rates and the partitioning of gaseous N products in agricultural soils. Therefore, optimizing organic material inputs to regulate the chemical composition of soil organic carbon, together with coordinated control of pH and NO3?-N levels, is critical for achieving high NO3?-N removal efficiency while minimizing the N2O/(N2O+N2) ratio. This, in turn, promotes the conversion of denitrification end-products toward N2, thereby facilitating reactive N mitigation and sustainable N cycling in agroecosystems.

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余恒,魏志军,马小芳,张雨蒙,颜晓元,单军.有机碳源质量对农田土壤反硝化产物特征的影响机制[J].土壤学报,DOI:10.11766/trxb202512020572,[待发表]
YU Heng, WEI Zhijun, MA Xiaofang, ZHANG Yumeng, YAN Xiaoyuan, SHAN Jun. Mechanisms of Gaseous Nitrogen Emissions from Denitrification in Agricultural Soils as Affected by Organic Material Quality[J]. Acta Pedologica Sinica, DOI:10.11766/trxb202512020572,[In Press]

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  • 收稿日期:2025-12-02
  • 最后修改日期:2026-06-04
  • 录用日期:2026-09-03
  • 在线发布日期: 2026-09-03
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