State Key Laboratory for Managing Biotic and Chemical Threats to the Quality and Safety of Agro-products, Institute of Environment, Resource, Soil and Fertilizers, Zhejiang Academy of Agricultural Sciences, Hangzhou, 310021, China.
State Key Laboratory for Managing Biotic and Chemical Threats to the Quality and Safety of Agro-products, Institute of Environment, Resource, Soil and Fertilizers, Zhejiang Academy of Agricultural Sciences, Hangzhou, 310021, China; Key Laboratory of Traceability for Agricultural Genetically Modified Organisms, Ministry of Agriculture and Rural Affairs, PR China, Hangzhou 310021, China.
Chemosphere. 2023 Sep;335:139051. doi: 10.1016/j.chemosphere.2023.139051. Epub 2023 Jun 2.
Manure has been considered as a source of soil heavy metal (HM) pollution. However, the long-term impact of manure application on soil HM accumulation have not been well studied. This study tracked the long-term cumulative trends of soil copper (Cu), zinc (Zn), arsenic (As), and lead (Pb) in three soil-crop systems over 5-8 years' application of commercial manure fertilizer. The contribution of different fertilization treatments (CF, chemical fertilizer; T1-T3, manure with different application dosages) to soil HMs pollution risk were assessed. There are accumulating tendencies for Cu, Zn, and Pb in paddy fields, Cu and As in orchard fields, and Zn, As, and Pb in vegetable fields, while the concentrations of As in paddy fields and Zn in orchard fields decreased over time. Manure application significantly influenced the accumulation of Cu, Zn, and As in soils rather than that of Pb. The modeling prediction subsequently revealed that the time required to reach the risk screening values (Cu: 50 mg kg; Zn: 200 mg kg) for HM content in paddy soil, according to GB15618-2018, decreased from 18.20 years to 7.20 years due to the introduction of Cu and Zn via manure use. Recommend annual manure application dosage was 7.73 t hm y to ensure a 20-year period of clean production in paddy soils, while it was 26.15 t hm y in the orchard soil and 16.23 t hm y in vegetable soil to ensure a 50-year period of clean production, respectively. Overall, the impacts of HMs input by manure application on soil HMs accumulation varied depending on the type of metal and the soil-crop system. The cumulative trends of HMs in soils play a crucial role in determining whether the input of HMs through manure application can lead to the risk of HM pollution.
粪便一直被认为是土壤重金属 (HM) 污染的来源。然而,粪便施用对土壤 HM 积累的长期影响尚未得到很好的研究。本研究跟踪了商业有机肥施用 5-8 年后三种土壤-作物系统中土壤铜 (Cu)、锌 (Zn)、砷 (As) 和铅 (Pb) 的长期累积趋势。评估了不同施肥处理 (CF,化肥;T1-T3,不同施用量的粪便) 对土壤 HM 污染风险的贡献。在稻田中,Cu、Zn 和 Pb 呈累积趋势,在果园中,Cu 和 As 呈累积趋势,在蔬菜田中,Zn、As 和 Pb 呈累积趋势,而稻田中 As 的浓度和果园中 Zn 的浓度随时间呈下降趋势。粪便施用量显著影响土壤中 Cu、Zn 和 As 的积累,而对 Pb 的积累影响不大。随后的建模预测显示,根据 GB15618-2018,由于 Cu 和 Zn 通过粪便使用进入土壤,达到农田土壤 HM 含量风险筛选值 (Cu:50 mg kg;Zn:200 mg kg) 所需的时间从 18.20 年缩短到 7.20 年。建议每年施用 7.73 t hm y 的粪肥,以确保在稻田土壤中实现 20 年的清洁生产,而在果园土壤中则需要 26.15 t hm y,在蔬菜土壤中则需要 16.23 t hm y,以确保 50 年的清洁生产。总体而言,粪便施用对土壤 HM 积累的影响因金属类型和土壤-作物系统而异。土壤中 HM 的累积趋势在确定通过粪便施用输入的 HM 是否会导致 HM 污染风险方面起着至关重要的作用。