Journal
JOURNAL OF SOILS AND SEDIMENTS
Volume 16, Issue 5, Pages 1519-1528Publisher
SPRINGER HEIDELBERG
DOI: 10.1007/s11368-015-1345-6
Keywords
Arsenic; NaHCO3-extractable As; Sequential extraction; Soil profile; Water-soluble As
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Funding
- National Science and Technology Support Program [2012BAC12B02]
- National Natural Science Foundation of China [51074191]
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Purpose Serious arsenic (As)-contaminated soils have the potential to cause contamination of ground water and surface water, being toxic to plant, animals, and human. The aim of study was to characterize As contamination in the soils from Shimen realgar mine area, the largest realgar deposit in Asia. Materials and methods Total As concentrations, As chemical fractionation, and As potential solubility both at various land use types (smelting and processing plants (SPP), mining site (MS), and agriculture land (AL)) and soil depths (0-100 cm) were investigated. As speciation in soil was examined using X-ray absorption fine structure (XAFS) analysis, and risk assessment was also carried out to evaluate potential ecological risk of As contamination. Results and discussion As concentrations in the studied area were extremely high, and the total As concentration reached up to 5240.8 mg kg(-1). Moreover, total As and NaHCO3-extractable As concentrations in all soil layers for various land use were far beyond the range of the non-contaminated soil. The potential ecological risk level of As posed higher to serious risk to the environment based on ecological risk index values. Sequential extraction confirmed that As is mostly bonded with amorphous and poorly crystalline hydrous iron and aluminum oxides (65 similar to 70 %), and only a small proportion (about 11 %) is partitioned in residual fraction, suggesting high risk of As mobilization. According to XAFS analysis, As was predominantly present in the form of arsenate, and arsenite was also found in the samples from SPP, MS, and AL. Conclusions The results indicate that the extra high concentrations of As were caused by both natural geochemical enrichment and long-lasting ore mining, smelting, and processing, and land use can greatly influence As contents in surface soil. These findings can be important for risk assessment and for the development and implementation of suitable management and remediation strategies.
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