4.5 Article

Soil Contaminated with Hazardous Waste Materials at Rio Tinto Mine (Spain) Is a Persistent Secondary Source of Acid and Heavy Metals to the Environment

Journal

MINERALS
Volume 13, Issue 4, Pages -

Publisher

MDPI
DOI: 10.3390/min13040456

Keywords

Technosol; mine wastes; soil contamination; acidity; leaching test; metal release; speciation; ICP-OES; MS; acid soil drainage; Iberian Pyrite Belt

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Mineralogical analysis and leaching tests were conducted to assess acid generation and trace element release from heavily contaminated mine waste soils. Results showed high net acid generation values, mainly attributed to sulfidic acidity and acidity retained in jarosite. Significant amounts of As and toxic heavy metals were found, particularly in slag-contaminated soil. Copper, Zn, and Pb were the most abundant metals in the acid leach solutions. Although total trace element contents in soil were high, the mobile fraction was limited. Acid soil drainage is a secondary source of acid and heavy metals, emphasizing the need for effective land reclamation programs to reduce acidity and metal mobility to sustainable levels.
Mineralogical analysis and laboratory-based leaching tests coupled with speciation modeling were undertaken to quantify the potential for short-term acid generation and the release of trace elements from soils heavily contaminated with mine waste at Rio Tinto. Three different waste materials were considered as case studies: roasted pyrite, copper slags, and leached sulfide ores. The results showed elevated values of net acid generation (up to 663 mmol H+/kg), the major pools being potential sulfidic acidity and acidity retained in jarosite. Remarkable contents of As and toxic heavy metals were found especially in the slag-contaminated soil. Copper, Zn, and Pb were the most abundant metals in the acid leach solutions resulting from mine soil-water interaction, with peak values of 55.6 mg L-1, 2.77 mg L-1, and 2.62 mg L-1, respectively. Despite the high total contents of trace elements occurring in soil, the mobile fraction was limited to maximum release values of 12.60% for Cd and 10.27% for Cu, according to the test leaching. Speciation calculations indicated that free metal ions (M2+) and sulfate species (MSO40) accounted for most of the dissolved load. Acid soil drainage is a secondary source of acid and heavy metals in the mine site and, therefore, an effective land reclamation program should ensure that acidity and metal mobility are reduced to environmentally sustainable levels.

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