Fe-sulphate-rich evaporative mineral precipitates from the Río Tinto, southwest Spain

Abstract The soluble metal sulphate salts melanterite, rozenite, rhomboclase, szomolnokite, copiapite, coquimbite, hexahydrite and halotrichite, together with gypsum, have been identified, some for the first time, on the banks of the Río Tinto, SW Spain. Secondary Fe-sulphate minerals can form directly from evaporating, acid, sulphate-rich solutions as a result of pyrite oxidation. Chemical analyses of mixtures of these salt minerals indicate concentrations of Fe (up to 31 wt.%), Mg (up to 4 wt.%), Cu (up to 2 wt.%) and Zn (up to 1 wt.%). These minerals are shown to act as transient storage for metals and can store on average up to 10% (9.5-11%) and 22% (20-23%), Zn and Cu respectively, of the total discharge of the Río Tinto during the summer period. Melanterite and rozenite precipitates at Río Tinto are only found in association with very acidic drainage waters (pH <1.0) draining directly from pyritic waste piles. Copiapite precipitates abundantly on the banks of the Río Tinto by (1) direct evaporation of the river water; or (2) as part of a paragenetic sequence with the inclusion of minor halotrichite, indicating natural dehydration and decomposition. The natural occurrences are comparable with the process of paragenesis from the evaporation of Río Tinto river water under laboratory experiments resulting in the formation of aluminocopiapite, halotrichite, coquimbite, voltaite and gypsum.

[1]  R. Howie,et al.  An Introduction to the Rock-Forming Minerals , 1966 .

[2]  A. Geen,et al.  Recent mine spill adds to contamination of southern Spain , 1998 .

[3]  C. Cravotta Secondary Iron-Sulfate Minerals as Sources of Sulfate and Acidity: Geochemical Evolution of Acidic Ground Water at a Reclaimed Surface Coal Mine in Pennsylvania , 1993 .

[4]  D. D. Runnells,et al.  Geochemical models of the impact of acidic groundwater and evaporative sulfate salts on Boulder Creek at Iron Mountain, California , 2001 .

[5]  Banfield,et al.  Distribution of thiobacillus ferrooxidans and leptospirillum ferrooxidans: implications for generation of acid mine drainage , 1998, Science.

[6]  K. Hudson-Edwards,et al.  Mineralogy and geochemistry of alluvium contaminated by metal mining in the Rio Tinto area, southwest Spain , 1999 .

[7]  R. Amils,et al.  Microbial Community Composition and Ecology of an Acidic Aquatic Environment: The Tinto River, Spain , 2000, Microbial Ecology.

[8]  D. Avery Not on Queen Victoria's birthday;: The story of the Rio Tinto mines , 1974 .

[9]  D. Nordstrom,et al.  Metal-sulfate Salts from Sulfide Mineral Oxidation , 2000 .

[10]  D. Nordstrom,et al.  Seasonal variations of Zn/Cu ratios in acid mine water from Iron Mountain, California , 1993 .

[11]  P. Singer,et al.  Acidic Mine Drainage: The Rate-Determining Step , 1970, Science.

[12]  D. Nordstrom,et al.  Negative pH, efflorescent mineralogy, and consequences for environmental restoration at the Iron Mountain Superfund site, California. , 1999, Proceedings of the National Academy of Sciences of the United States of America.

[13]  M. Coleman,et al.  Solution chemistry during the lag phase and exponential phase of pyrite oxidation by Thiobacillus ferrooxidans , 2001 .

[14]  J. Banfield,et al.  Geochemical and biological aspects of sulfide mineral dissolution: lessons from Iron Mountain, California , 2000 .

[15]  J. M. Frías,et al.  Recursos minerales de España , 1992 .

[16]  C. Nelson,et al.  Heavy metal anomalies in the Tinto and Odiel River and estuary system, Spain , 1993 .

[17]  F. Frau The formation-dissolution-precipitation cycle of melanterite at the abandoned pyrite mine of Genna Luas in Sardinia, Italy: environmental implications , 2000, Mineralogical Magazine.

[18]  D. Nordstrom,et al.  Iron and Aluminum Hydroxysulfates from Acid Sulfate Waters , 2000 .