Effect of phosphate on cadmium immobilized by microbial-induced carbonate precipitation: Mobilization or immobilization?

被引:17
|
作者
Liao, Zisheng [1 ,2 ,3 ,4 ]
Wu, Shijun [1 ,2 ,3 ]
Xie, Hong [1 ,2 ,3 ,4 ]
Chen, Fanrong [1 ,2 ,3 ]
Yang, Yongqiang [1 ,2 ,3 ]
Zhu, Runliang [1 ,2 ,3 ]
机构
[1] Chinese Acad Sci, CAS Key Lab Mineral & Metallogeny, 511 Kehua St, Guangzhou 510640, Peoples R China
[2] Chinese Acad Sci, Guangzhou Inst Geochem, Guangdong Prov Key Lab Mineral Phys & Mat, 511 Kehua St, Guangzhou 510640, Peoples R China
[3] Chinese Acad Sci, Ctr Excellence Deep Earth Sci, 511 Kehua St, Guangzhou 510640, Peoples R China
[4] Univ Chinese Acad Sci, 19 Yuquan Rd, Beijing 100049, Peoples R China
基金
中国国家自然科学基金;
关键词
Microbial-induced carbonate precipitation  (MICP); Cadmium; Phosphate; Immobilization; Soil acidification; CONTAMINATED SOIL; CHEMICAL IMMOBILIZATION; HEAVY-METALS; PADDY SOIL; REMEDIATION; SOLUBILITY; SPECIATION; BIOREMEDIATION; NITRIFICATION; FRACTIONATION;
D O I
10.1016/j.jhazmat.2022.130242
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Microbial-induced carbonate precipitation (MICP) is a promising technology to immobilize/remediate heavy metals (HMs) like cadmium (Cd). However, the long-term stability of MICP-immobilized HMs is unclear, espe-cially in farmland where chemical fertilization is necessary. Therefore, we performed MICP treatment on soils contaminated with various Cd compounds (CdCO3, CdS, and CdCl2) and added diammonium phosphate (DAP) to explore the impact of phosphate on the MICP-immobilized Cd. The results showed that MICP treatment was practical to immobilize the exchangeable Cd but to mobilize the carbonate and Fe/Mn oxide-bound Cd. After applying DAP, soil pH declined due to ammonium nitrification. At high P/Ca molar ratios (1/2 and 1), partial previously immobilized Cd was released due to the carbonate dissolution. Contrarily, exchangeable Cd trans-formed to less mobilizable Fe/Mn oxide-bound at low P/Ca molar ratios (1/4 and 1/8). Meanwhile, other treatments were also helpful in avoiding the release of immobilized Cd, such as applying non-ammonium phosphate and adding lime material after soil acidification. Our investigation suggested that the long-term stability of HMs in remediated sites should be carefully evaluated, especially in agricultural areas with phos-phate and nitrogen fertilizer input.
引用
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页数:12
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