中国农业气象 ›› 2021, Vol. 42 ›› Issue (04): 272-286.doi: 10.3969/j.issn.1000-6362.2021.04.002

• 农业生态环境栏目 • 上一篇    下一篇

生物炭/石灰混施对重金属复合污染土壤的稳定化效应

戴思睿,李莲芳,秦普丰,朱昌雄,叶婧,耿兵,刘雪,李红娜,李峰   

  1. 1. 湖南农业大学资源环境学院,长沙 410128;2. 中国农业科学院农业环境与可持续发展研究所/农业农村部农业环境重点实验室,北京 100081
  • 收稿日期:2020-11-25 出版日期:2021-04-20 发布日期:2021-04-15
  • 通讯作者: 李莲芳,研究员,从事农业环境保护与生态重建修复研究,E-mail: lilianfang@caas.cn E-mail:lilianfang@caas.cn
  • 作者简介:戴思睿,E-mail:1143885795@qq.com
  • 基金资助:
    国家重点研发计划(2020YFC1806401)

Immobilization Effect of Biochar and Lime on Arsenic, Cadmium and Lead in Soils

DAI Si-rui, LI Lian-fang, QIN Pu-feng, ZHU Chang-xiong, YE Jing, GENG Bing, LIU Xue, LI Hong-na, LI Feng   

  1. 1. College of Resources and Environment, Hunan Agricultural University, Changsha 410128, China; 2. Institute of Environment and Sustainable Development in Agriculture, Chinese Academy of Agricultural Sciences/Key Laboratory of Agro-Environment, Ministry of Agriculture and Rural Affairs of the People’s Republic of China, Beijing 100081
  • Received:2020-11-25 Online:2021-04-20 Published:2021-04-15

摘要: 采用室内模拟实验,以南方砷镉铅复合污染的酸性红壤为对象,利用化学钝化原理,探讨钝化材料对重金属稳定化的技术效果及应用配方,以期为砷镉铅复合污染红壤修复与安全利用提供依据。具体做法为:选择生物炭(BC)和石灰(SH)为钝化材料,以土壤重量的1%、4%为材料添加量,单一或混合施用于砷镉铅复合污染土壤,并于恒温(25℃)条件下培养60d,在实验进行至第1天、第30天、第60天时取样,测定红壤酸碱度(pH)和水溶态(Water soluble)有效砷(As)、镉(Cd)、铅(Pb)即WSAs、WSCd、WSPb含量,以及土壤重金属As、Cd、Pb结合态含量与占比的变化,明确生物炭石灰单/混施对重金属的稳定化效应。结果表明:生物炭/石灰无论单施或混施均能不同程度地降低土壤中水溶态WSCd和WSPb含量,钝化效率分别为33.51%~78.89%和9.05%~96.24%。而材料单施(1BC、4SH)和两者混施高用量(4BC4SH)处理,均能大幅降低土壤中有效As含量,钝化效率为10.25%~55.27%,其中以两者混施高用量(4BC4SH)处理对土壤重金属As、Cd、Pb协同钝化的效果最佳,当培养实验进行至第60天时,钝化效率依次达55.27%、76.39%和96.24%。培养后土壤中As形态由易被植物吸收的非专性吸附态、专性吸附态转化为稳定的残渣态,土壤中Cd和Pb则由活性最强的酸可提取态转化为残渣态,土壤中As、Cd、Pb的稳定化效应明显,迁移系数下降;此外,生物炭/石灰的单施及混合施用,均可导致土壤酸碱度(pH)显著提升(P<0.05),有利于南方酸化土壤的改良。总体而言,本研究中生物炭/石灰两者混施高用量水平下(4BC4SH)土壤重金属的钝化效果最优,可实现对As、Cd和Pb复合污染红壤的稳定化修复。

关键词: 红壤, 重金属污染, 生物炭, 石灰, 化学钝化

Abstract: Aiming to remediate and utilize red soil contaminated by arsenic, cadmium and lead safely, simulated incubation experiments were conducted to investigate the stabilization effect of chemical amendments on the immobility of arsenic (As), cadmium (Cd) and lead (Pb) in red soil of southern China, and the technical formula of remediation materials for the best stabilization effect were also explored. Experimental procedures are as following: using biochar(BC) and lime(SH) for immobilization materials, with 1% and 4% of the weight of soil as material application rate, biochar and lime were applied singly or mixed into contaminated soil by arsenic, cadmium and lead, and incubated at the situation with a constant temperature(25℃) and 70% field capacity in soils for 60 days, then the samples were taken on the 1st, 30th and 60th days during the incubation experiment. The changes of pH, contents of water soluble As, Cd, Pb(WSAs, WSCd, WSPb) and the speciation of As, Cd, Pb in soils were determined. and the stabilization effects of single and mixed application of biochar/lime were analyzed. The results showed that the contents of water-soluble cadmium (WSCd) and lead (WSPb) in soil were reduced to different degrees by applying biochar/lime singly or in combination, and the corresponding ranges for immobilization efficiencies were 33.51%−78.89% and 9.05%−96.24%, respectively. Under the treatment of single application of biochar/lime (1BC, 4SH) or combined application of high amount of biochar and lime (4BC4SH), the content of water soluble As (WSAs) in soils decreased obviously, and the reduced percentage of WSAs ranged from 10.25% to 55.27%. Among all the treatments, the combined treatment with a high dosage had the best synergistic immobilization effect on As, Cd and Pb in red soil. When the incubation test lasted for 60 days, the immobilization efficiency reached 55.27%, 76.39% and 96.24%, respectively. In the meanwhile, the forms of As in soils changed from non-specifically sorbed and specifically sorbed phases which can be easily absorbed by plants to residual ones, and the forms of Cd and Pb in soils changed from the most active acid-extractable to residual phases. The stabilization effect of As, Cd and Pb in soil was observed obviously, and the migration coefficient decreased simutanously. In addition, the application of biochar/lime alone and in combination resulted in a significant increase of soil pH(P<0.05), which was beneficial for the improvement of acidified soil in southern China. In general, through this investigation, the combined application of biochar/lime at a high dosage(4BC4SH) as amendments can stabilize the available As, Cd and Pb in red soils effectively and has the best immobilization effect on heavy metals.

Key words: Red soil, Heavy metal contamination, Biochar, Lime, Chemical immobilization