The associations of heavy metals with crystalline iron oxides in the polluted soils around the mining areas in Guangdong Province, China

被引:83
作者
Yin, Hui [1 ]
Tan, Nianhao [1 ]
Liu, Chuanping [2 ]
Wang, Juju [1 ]
Liang, Xiaoliang [3 ]
Qu, Mingkai [4 ]
Feng, Xionghan [1 ]
Qiu, Guohong [1 ]
Tan, Wenfeng [1 ]
Liu, Fan [1 ]
机构
[1] Huazhong Agr Univ, Coll Resources & Environm, Minist Agr, Key Lab Arable Land Conservat Middle & Lower Reac, Wuhan 430070, Peoples R China
[2] Guangdong Inst Ecoenvironm & Soil Sci, Guangdong Key Lab Agr Environm Pollut Integrated, Guangzhou 510650, Guangdong, Peoples R China
[3] Chinese Acad Sci, Guangzhou Inst Geochem, CAS Key Lab Mineral & Metallogeny, Guangzhou 510640, Guangdong, Peoples R China
[4] Chinese Acad Sci, Inst Soil Sci, Key Lab Soil Environm & Pollut Remediat, Nanjing 210008, Jiangsu, Peoples R China
关键词
Soil pollution; Iron oxyhydroxides; Selective sequential extraction procedures; Metal fraction; Mobility; SEQUENTIAL EXTRACTION PROCEDURE; DABAOSHAN MINE; SOUTH CHINA; ALUMINUM SUBSTITUTION; CONTAMINATED SOILS; SEDIMENT SAMPLES; TRACE-ELEMENTS; SEWAGE-SLUDGE; SPECIATION; FRACTIONATION;
D O I
10.1016/j.chemosphere.2016.07.018
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
In current selective sequential extraction (SSE) methods, heavy metals associated well-crystallized iron oxyhydroxides are not well defined and considered, and usually fall into residual forms, which actually make their mobility and environmental risk underestimated. This study compared various fractions of heavy metals in samples of mining tailings and nearby soils under different land uses in Guangdong Province of China. Iron oxides in these soils were mainly Al-substituted goethites and/or hematites. Independent of the land uses, the percentages of various Cd fractions in the soils decrease in the order of well-crystallized iron oxyhydroxides-associated (27.2-91.2%) > residual (2.1-37.0%) > reducible Fe-Mn oxides (3.2-45.7%) > exchangeable (1.0-28.2%) > organic-associated form (0-5.1%). Pb mainly existes in the residual fraction (25.9-74.5%), followed by crystalline iron oxyhydroxides-associated (0.4-69.0%) and reducible fractions (2.4-40.4%). Zn mainly exists in the residual fraction (25.4-85.9%), followed by the well-crystallized iron oxyhydroxides-associated fraction (6.4-55.0%). However, Cu mainly existes in the residual form and the fractionation of Cu varies obviously between samples. The association of these metals with crystalline iron oxyhydroxides in the soils decreases in the sequence of Cd > Pb > Zn > Cu. These results suggest that in heavy-metal-polluted weathered soils in tropical and subtropical areas enriched with iron oxides, it is essential to assess potential bioavailability and toxicity of heavy metals bound to well-crystallized iron oxyhydroxides with appropriate procedures in the fractionation measurement. The modified Tessier method present here can be used to quantify the fractions of heavy metals in such areas. (C) 2016 Elsevier Ltd. All rights reserved.
引用
收藏
页码:181 / 189
页数:9
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