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连续施硅与秸秆管理对土壤-水稻系统镉积累的影响

Effects of continuous silicon application and straw management on cadmium accumulation in the soil-rice system

  • 摘要: 在农田镉(Cd)污染的背景下,秸秆还田在促进资源循环利用的同时,也可能增加Cd再活化的风险。然而,长期施用硅肥与秸秆管理对土壤Cd稳定化及水稻Cd积累的协同调控机制仍不清楚。为探明连续施硅与秸秆离/还田对土壤-水稻系统Cd迁移积累的影响,本研究在湖南省浏阳市永安镇开展连续三年田间定位试验,设置施硅秸秆还田(+SiR)、施硅秸秆离田(+SiNR)、不施硅秸秆还田(−SiR)和不施硅秸秆离田(−SiNR)4个处理。结果表明,施硅和秸秆管理均显著影响水稻Cd积累,且二者交互作用随处理年限延长而增强。连续施硅可显著提高土壤有效硅含量和pH,促进土壤Cd向铁锰氧化物结合态和残渣态转化,降低Cd生物有效性。与−SiR处理相比,连续施硅显著降低土壤有效Cd和糙米Cd含量,其中+SiNR处理降幅最大,分别降低36.67%和55.56%。+SiR处理土壤有效硅水平最高,但秸秆腐解过程中Cd再输入可能削弱部分降Cd效果。相关性分析表明,土壤有效Cd与pH呈极显著负相关(r=−0.89,P<0.001),与水稻秸秆Si含量呈显著负相关(r=−0.60,P<0.05),水稻Si积累与Cd含量呈负相关关系,表明植株Si积累可能有助于降低Cd向地上部和籽粒的转运。研究结果可为Cd污染双季稻田秸秆管理优化与硅肥合理施用提供理论依据。

     

    Abstract: In Cd-contaminated agricultural soils, straw incorporation promotes resource recycling but may also increase the risk of Cd remobilization. However, the interactive effects of long-term silicon (Si) fertilization and straw management on soil Cd stabilization and Cd accumulation in rice remain unclear. To investigate the effects of continuous Si application combined with straw incorporation or removal on Cd migration and accumulation in the soil–rice system, a three-year field experiment was conducted in Yong'an Town, Liuyang City, Hunan Province, China. Four treatments were established: Si application with straw incorporation (+SiR), Si application with straw removal (+SiNR), no Si application with straw incorporation (−SiR), and no Si application with straw removal (−SiNR). The results showed that both Si application and straw management significantly affected Cd accumulation in rice, and their interaction became increasingly pronounced with prolonged treatment duration. Continuous Si application significantly increased soil available Si concentration and soil pH, promoted the transformation of Cd into Fe-Mn oxide-bound and residual fractions, and thereby reduced Cd bioavailability. Compared with the −SiR treatment, continuous Si application significantly decreased the available Cd concentration in soil and Cd concentration in brown rice, with the greatest reductions observed in the +SiNR treatment, reaching 36.67% and 55.56%, respectively. Although the +SiR treatment resulted in the highest soil available Si concentration, Cd re-input during straw decomposition may partially offset the Cd immobilization effect of Si application. Correlation analysis showed that soil available Cd was significantly negatively correlated with soil pH (r = −0.89, P < 0.001) and straw Si concentration (r = −0.60, P < 0.05). Rice Si accumulation was negatively correlated with Cd concentration, indicating that enhanced Si accumulation may help reduce Cd translocation from roots to shoots and grains. These findings provide a theoretical basis for optimizing straw management and the rational application of Si fertilization in Cd-contaminated double-cropping rice fields.

     

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