长期施肥下红壤坡耕地土壤-花生系统重金属累积特征及风险评价

Assessment of Long-term Fertilization on Heavy Metal Ecological and Health Risks in the Soil - Peanut System of Red Soil in Sloping Farmland

  • 摘要:
    目的 长期施肥可能会对红壤坡耕地土壤重金属累积和人体健康造成一定的风险,为准确评估土壤-花生系统重金属生态与健康风险,更准确地指导红壤丘陵山区耕地培肥。
    方法 基于中国科学院红壤生态实验站红壤坡耕地12年长期施肥小区试验,采集耕层土壤及花生样品,分析不施肥(CK)、单施化肥(NPK)以及猪粪与化肥配施(NPK + PM)三种处理下土壤-花生系统中铬(Cr)、铜(Cu)、锌(Zn)、镉(Cd)四种重金属的含量。通过单因子污染指数法、内梅罗综合污染指数法及潜在生态风险指数法评价土壤中重金属污染等级及生态风险,并采用人体健康风险评估模型分析土壤和花生籽粒重金属对成人及儿童的致癌与非致癌健康风险。
    结果 与CK处理相比,NPK处理下耕层土壤Cr全量增加了23.8%(P < 0.05);而NPK + PM处理下耕层土壤Cu、Zn和Cd全量增加110% ~ 130%(P < 0.05),花生籽粒Cu、Cd全量降低50.6% ~ 83.0%(P < 0.05)。NPK + PM处理下土壤Cu污染指数达到轻度污染,综合污染指数处于轻微污染;而NPK与NPK + PM处理下重金属潜在生态风险均处于轻微风险等级,花生重金属对成人及儿童造成的非致癌健康风险可忽略;NPK + PM处理下土壤Cu、Zn、Cd对成人及儿童造成的非致癌健康风险较NPK处理增幅达67.5% ~ 174.0%,均处于可接受范围内,但土壤Cr对儿童可能造成不可接受的致癌健康风险。与成人相比,土壤重金属通过口服摄入途径对儿童造成非致癌健康风险的比例升高4.72% ~ 4.83%,而通过皮肤接触的比例降低22.9% ~ 23.0%。
    结论 长期施用猪粪显著增加了红壤坡耕地耕层土壤重金属的累积及污染风险,但并不会通过花生籽粒对人体健康产生显著危害。建议施用猪粪前通过高温堆肥、添加钝化剂以及优化施肥制度来降低潜在风险,并定期开展环境监测。

     

    Abstract:
    Objective Long-term fertilization can lead to heavy metal accumulation in red soil, posing potential health hazards to humans. Accurate assessment of the ecological and health risks of heavy metals in the soil-peanut system is crucial for guiding soil fertility management in the hilly red soil regions.
    Method Based on a long-term erosion plot experiment established in 2012 at the Chinese Academy of Sciences Red Soil Ecological Experimental Station, surface soil and peanut samples were collected in 2023. This study analyzed the concentrations of Cr, Cu, Zn, and Cd content in the soil-peanut system under three treatments: control (CK), chemical fertilizer (NPK), and a combination of pig manure with chemical fertilizer (NPK + PM). Soil heavy metal pollution grades and ecological risks were assessed using the single-factor pollution index, Nemerow comprehensive pollution index, and the potential ecological risk index. Additionally, a health risk assessment model was applied to analyze carcinogenic and non-carcinogenic risks posed to adults and children from the contaminated soil and peanut grains.
    Result Compared to the control, total Cr content in the surface soil increased significantly by 23.8% (P < 0.05) after 12 years of chemical fertilization. In contrast, the combined application of pig manure with chemical fertilizer over 12 years significantly increased total Cu, Zn, and Cd in the surface soil by 110 - 130% (P < 0.05), while significantly reducing Cu and Cd in peanut grains by 50.6 - 83.0% (P < 0.05). Long-term application of pig manure with chemical fertilizer resulted in a mild pollution index for Cu, while the comprehensive pollution index indicated slight pollution. However, the potential ecological risk of soil heavy metals under long-term fertilization remained at a slight risk level. Under long-term fertilization, the non-carcinogenic risk index from ingesting peanuts remained within the safe threshold for both adults and children. The combined pig manure with fertilizer treatment increased the non-carcinogenic risk index for Cu, Zn, and Cd in soil by 67.5 - 174% compared to chemical fertilizer alone, but still remained within safe limits. However, Cr in soil exceeded the carcinogenic risk threshold for children. Compared to adults, children showed a significantly higher proportion of non-carcinogenic risks from ingesting soil heavy metals (4.72% - 4.83%) and a significantly lower proportion through skin contact (22.9% - 23.0%).
    Conclusion The study showed that long-term application of pig manure significantly increases the accumulation and pollution risks of heavy metals in the plow layer of sloping red soil. However, it does not pose significant health hazards to humans through peanut kernels. It is recommended to treat pig manure with high-temperature composting or by adding heavy metal immobilizers before application. Additionally, adjusting the application rate and frequency, coupled with regular environmental monitoring, can effectively reduce potential risks to soil environments and human health.

     

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