连续三年施用改良剂对镉污染稻田的修复效果研究

Remediation of Cadmium-contaminated Rice Fields by Three Consecutive Years of Amendment Application

  • 摘要:
    目的 本研究目的为探讨连续三年施用石灰、生物炭和硅肥对中度镉污染稻田的修复效果。
    方法 以湖南省典型双季稻区土壤-水稻系统为研究对象,采用随机区组设计,共设对照(T1)、施用石灰(T2)、施用生物炭(T3)和施用硅肥(T4)4个处理,分析施用不同改良剂的稻田土壤理化性质和水稻镉含量特征,通过冗余分析与回归分析探究土壤因子对镉在土壤-水稻系统中迁移转运的影响。
    结果 相较于T1处理,T2处理土壤pH显著增加至6.92 ± 0.05,土壤有效镉降低至0.41 ± 0.09 mg kg−1;T3、T4处理与T1处理相比,土壤pH、有效镉、活性有机质均无显著差异。T3处理早稻和晚稻糙米镉含量最高,分别为0.54 ± 0.07和0.11 ± 0.04 mg kg−1;T2处理最低,分别为0.16 ± 0.00和0.03 ± 0.01 mg kg−1。冗余分析结果表明:糙米中镉含量(RiCd)与土壤pH负相关,与有效镉含量(DPTA-Cd)正相关。糙米中镉含量与土壤有效镉含量的关系式为:RiCd (mg kg−1) = −0.0822 + 0.297 DPTA-Cd (mg kg−1)(Radj2=0.503, P < 0.05)。
    结论 连续三年施用石灰对中度镉污染稻田有较好修复效果,其主要通过提升土壤pH,降低土壤有效镉含量,进而降低水稻糙米镉含量。

     

    Abstract:
    Objective The aims were to investigate the remediation effect of lime, biochar and silicon fertilizer on moderate Cd-contaminated rice fields after three consecutive years of application.
    Method The soil and rice system of typical double-cropping rice area in Hunan Province was selected as the research object. Four treatments, control (T1), application of lime (T2), biochar (T3) and silicon fertilizer (T4), were used in conducted in a randomized group design to analyze the physicochemical properties of paddy soil and the cadmium content of rice with different amendments. The effects of soil factors on cadmium transport in soil-rice system were investigated by redundancy analysis and regression analysis.
    Results The results showed that T2 increased soil pH to 6.92 ± 0.05, soil available Cd decreased to 0.41 ± 0.09 mg kg−1 compared with T1. There were no significant differences in soil pH, available Cd and dissolved organic matter in T3 and T4 treatments compared with T1 treatments. Cd content in brown rice in T3 treatment were the highest in the early and late season at 0.54 ± 0.07 and 0.11 ± 0.04 mg kg−1. The T2 treatment had the lowest at 0.16 ± 0.00 and 0.03 ± 0.01 mg kg−1. The redundancy analysis showed that Cd content in brown rice was negatively correlated with soil pH and positively correlated with soil available Cd (DPTA-Cd). The relationship between brown rice cadmium content (RiCd) and soil available Cd was as follows: RiCd mg kg−1= -0.0822 + 0.297 DPTA-Cd mg kg−1 (Radj2=0.503, P < 0.05).
    Conclusion Continuous application of lime for 3-year effectively remediated paddy fields under moderately cadmium pollution due to soil pH increase and soil available cadmium reduction, could cut down the Cd content in brown rice.

     

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