Simultaneous Immobilization of Lead and Atrazine in Contaminated Soils Using Dairy-Manure Biochar

生物炭 阿特拉津 化学 修正案 环境化学 环境修复 肥料 土壤水分 毒性特征浸出程序 木炭 环境科学 污染 浸出(土壤学) 杀虫剂 农学 热解 重金属 土壤科学 法学 有机化学 生物 生态学 政治学
作者
Xinde Cao,Q. Lena,Liang Yuan,Bin Gao,Willie G. Harris
出处
期刊:Environmental Science & Technology [American Chemical Society]
卷期号:45 (11): 4884-4889 被引量:552
标识
DOI:10.1021/es103752u
摘要

Biochar produced from waste biomass is increasingly being recognized as a green, cost-effective amendment for environmental remediation. This work was to determine the ability of biochar to immobilize heavy metal Pb and organic pesticide atrazine in contaminated soils. Biochar prepared from dairy manure was incubated with contaminated soils at rates of 0, 2.5, and 5.0% by weight for 210 d. A commercial activated carbon (AC) was included as a comparison. The AC was effective in immobilizing atrazine, but was ineffective for Pb. However, biochar was effective in immobilizing both atrazine and Pb and the effectiveness was enhanced with increasing incubation time and biochar rates. After 210 d, soils treated with the highest rate of 5.0% biochar showed more than 57% and 66% reduction in Pb and atrazine concentrations in 0.01 M CaCl2 extraction, respectively. Lead and atrazine concentrations in the toxicity characteristic leaching procedure solutions were reduced by 70–89% and 53–77%, respectively. Uptake of Pb and atrazine by earthworms (Eisenia fetida) was reduced by up to 79% and 73%. Phosphorus originally contained in biochar reacted with soil Pb to form insoluble hydroxypyromorphite Pb5(PO4)3(OH), as determined by X-ray diffraction, which was presumably responsible for soil Pb immobilization, whereas atrazine stabilization may result from its adsorption by biochar demonstrated by the significant exponential decrease of extractable atrazine with increasing organic C in biochar (r2 > 0.97, p < 0.05). The results highlighted the potential of dairy-manure biochar as a unique amendment for immobilization of both heavy metal and organic contaminants in cocontaminated soils.
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