• ISSN 1008-505X
  • CN 11-3996/S

有机肥替代化肥氮配施生物炭提高砂质潮土氮磷库容量及供应强度

Manure substitution combined with biochar enhances soil nitrogen and phosphorus pool capacity and supply potential in sandy fluvo-aquic soil

  • 摘要:
    目的 砂质潮土存在结构性差、矿化作用强、保水保肥能力弱等突出问题。探究生物炭、有机肥及其配施对砂质潮土不同深度土壤氮、磷组分及其转化的影响,为砂质潮土障碍消减和地力提升提供理论与技术支撑。
    方法 于2021年10月在河南省新乡县朗公庙镇开展小麦−玉米轮作定位试验。冬小麦季设置常规化肥(CK),以及在此基础上一次性施用生物炭(T1,15 t/hm2)、每年施用生物炭(T2,12 t/hm2),有机肥替代化肥氮20% (J1)、40% (J2),J1和J2基础上每年配施生物炭12 t/hm2 (TJ1、TJ2) ,共7个处理。于2024年6月(试验进行3年后)冬小麦收获期采集0—20 cm (表层)、20—40 cm (中层)和40—60 cm (下层)土壤,分析无机氮及酸解有机氮组分(酸解铵态氮、酸解氨基酸态氮、酸解氨基糖态氮、酸解未知态氮、非酸解氮)含量,活性磷(H2O-P、NaHCO3-Pi、NaHCO3-Po),中等活性磷(NaOH-Pi、NaOH-Po)和稳定态磷(HCl-P、Residual-P)含量,以及氮、磷素转化相关胞外酶活性。
    结果 T1处理各土层酸解有机氮组分含量与CK处理无显著差异,而T2处理较CK提高了表层土壤β-乙酰氨基葡萄糖苷酶活性,显著提高了表、中层土壤全氮含量33.3%~52.0%,增加了表层土壤酸解氨基酸态氮含量,并促进了表层土壤稳定态磷的积累。相比CK,J1和J2处理显著提高了表层土壤β-乙酰氨基葡萄糖苷酶和磷酸酶活性,提升了0—60 cm土层全氮和有效态氮、磷含量,显著提高了表层土壤酸解氨基酸态氮含量、中层土壤酸解铵态氮含量,使表层土壤活性磷含量提高31.1%~89.9%,中层土壤活性磷和中等活性磷含量分别提高29.6%~117.7%和51.0%~114.2%。相较T2、J1和J2处理,TJ1和TJ2处理进一步提高了各土层氮、磷转化相关酶活性,尤其显著提高表层土壤无机氮和活性磷含量,增加表层土壤酸解未知态氮比例,减少下层土壤无机氮积累,TJ1处理还显著增加中层土壤活性磷及中等活性磷含量。
    结论 有机肥施用显著提升0—40 cm土层土壤全氮含量,提高其活性较强的酸解铵态氮与酸解氨基酸态氮组分占比,进而增强氮、磷转化相关胞外酶活性,促进砂质潮土表层和中层土壤磷素活化。在此基础上,每年配施生物炭12 t/hm2进一步促进了氮素向酸解未知态氮转化,提高表层易分解有机氮固持和表层活性磷含量,稳定中层和下层土壤磷库,有效减少氮磷养分淋溶损失。因此,在砂质潮土地区,以有机肥替代常规化肥氮施用量的20%,同时配施生物炭,是优化砂质潮土氮、磷库构成、提升养分供应强度的可行措施。

     

    Abstract:
    Objectives Sandy fluvo-aquic soil is characterized by prominent constraints, including poor soil structure, intense mineralization, and low water- and nutrient-retention capacity. This study investigated the effects of biochar, manure, and their combined application on soil nitrogen and phosphorus fractions and their transformation at different soil depths, providing a theoretical and technical basis for alleviating soil constraints and improving soil fertility in sandy fluvo-aquic soil.
    Methods A wheat–maize rotation experiment was established in October 2021 in Langgongmiao Town, Xinxiang County, Henan Province, China. Seven treatments were implemented during the winter wheat season: conventional chemical fertilizer (CK); one-time biochar application at 15 t/hm2(T1); annual biochar application at 12 t/hm2(T2); replacement of 20% (J1) or 40% (J2) of chemical fertilizer N with manure; and annual application of 12 t/hm2 biochar combined with J1 or J2 (TJ1 and TJ2, respectively). Soil samples were collected during the winter wheat harvest in June 2024 from three depths: 0–20 cm (topsoil), 20–40 cm (middle soil), and 40–60 cm (deep soil). The contents of inorganic N and acid-hydrolyzable organic N fractions (acid-hydrolyzable ammonium N, amino acid N, amino sugar N, unknown N, and non-acid-hydrolyzable N), labile P (H2O-P, NaHCO3-Pi, NaHCO3-Po), moderately labile P (NaOH-Pi, NaOH-Po), and stable P (HCl-P, Residual-P), as well as the activities of extracellular enzymes involved in N and P transformation, were determined.
    Results The contents of acid-hydrolyzable organic N fractions under T1 did not differ significantly from those under CK in any soil layer. Compared with CK, T2 significantly increased β-acetylglucosaminidase activity in the topsoil, increased total N contents in the topsoil and middle soil by 33.3%–52.0%, increased acid-hydrolyzable amino acid N content in the topsoil, and promoted the accumulation of stable P in the topsoil. Compared with CK, J1 and J2 significantly increased β-acetylglucosaminidase and phosphatase activities in the topsoil, as well as total N and available N and P contents across the 0–60 cm soil profile. They also significantly increased acid-hydrolyzable amino acid N content in the topsoil and acid-hydrolyzable ammonium N content in the middle soil. Labile P content increased by 31.1%–89.9% in the topsoil and by 29.6%–117.7% in the middle soil, while moderately labile P content in the middle soil increased by 51.0%–114.2%. Compared with T2, J1, and J2, TJ1 and TJ2 further increased the activities of enzymes involved in N and P transformation across the soil profile, particularly increasing inorganic N and labile P contents in the topsoil. They also increased the proportion of acid-hydrolyzable unknown N in the topsoil and reduced the accumulation of inorganic N in the deep soil. In addition, TJ1 significantly increased labile and moderately labile P contents in the middle soil.
    Conclusions Manure application significantly increased total N content in the 0–40 cm soil layer and increased the proportions of the more labile acid-hydrolyzable ammonium N and amino acid N fractions, thereby enhancing the activities of extracellular enzymes involved in N and P transformation and promoting P activation in the topsoil and middle soil of sandy fluvo-aquic soil. On this basis, annual application of biochar at 12 t/hm2 further promoted the transformation of N into the acid-hydrolyzable unknown N fraction and enhanced the retention of readily decomposable organic N and labile P pools. This combination increased labile P content in the topsoil and stabilized P pools in the middle and deep soil layers, thereby reducing the potential leaching losses of N and P. Therefore, replacing 20% of conventional chemical fertilizer N with manure, combined with annual biochar application, is a feasible strategy for increasing the capacity and supply intensity of soil N and P pools in sandy fluvo-aquic soil.

     

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