Arsenic residues from historic gold extraction, Snowy River, Westland, New Zealand

ABSTRACT The Snowy River processing site was used to extract gold for the large historic Blackwater mine, Westland, between 1906 and 1938, and then abandoned. The site is now one of the best-preserved historic gold-processing localities, and access has been enhanced for visitors. The site has some high arsenic (As) concentrations on the surface, with some spots exceeding 40 wt% As. A variety of As-bearing minerals occurs along the former processing stream, from primary sulphides (arsenopyrite, pyrite) at the upstream end to arsenolite (As2O3) and scorodite (FeAsO4.2H2O) formed by the roasting of ore materials at the downstream end. Weathering over the past century of sulphide residues and some of the arsenolite has yielded more scorodite and some Ca arsenates. Minor authigenic As sulphide precipitates have formed on rotting wood. Arsenolite is principally distributed near to the roaster site, and this is the most soluble and potentially toxic mineral on site. Despite the locally abundant arsenolite, only minor As is mobilised into nearby waters.

[1]  A. Culka,et al.  Bioprecipitation of As4S4 polymorphs in an abandoned mine adit , 2020 .

[2]  D. Craw,et al.  Contrasting Structural Styles of Orogenic Gold Deposits, Reefton Goldfield, New Zealand , 2018, Economic Geology.

[3]  D. Craw,et al.  Authigenic realgar and gold in dynamic redox gradients developed on historic mine wastes, New Zealand , 2018, Applied Geochemistry.

[4]  D. Craw,et al.  Environmental mineralogy and geochemistry of processing residues at Prohibition historic gold mine site, Waiuta, Westland, New Zealand , 2018 .

[5]  J. Druzbicka,et al.  Conservation of saline patches in Central Otago needs better recognition of physical processes to secure future habitats , 2018 .

[6]  D. Craw,et al.  Comparison of contrasting gold mine processing residues in a temperate rain forest, New Zealand , 2017 .

[7]  D. Craw,et al.  Arsenic mineralogy and distribution at the historic Alexander gold mine, Reefton goldfield, New Zealand , 2017 .

[8]  D. Craw,et al.  Hydrothermal footprint of the Birthday Reef, Reefton goldfield, New Zealand , 2017 .

[9]  D. Craw,et al.  Evaporative Mine Water Controls on Natural Revegetation of Placer Gold Mines, Southern New Zealand , 2015, Mine Water and the Environment.

[10]  J. Druzbicka,et al.  Metalloid Attenuation from Runoff Waters at an Historic Orogenic Gold Mine, New Zealand , 2015, Mine Water and the Environment.

[11]  K. Hudson-Edwards,et al.  Mine Wastes: Past, Present, Future , 2011 .

[12]  H. Jamieson,et al.  Direct Characterization of Airborne Particles Associated with Arsenic-rich Mine Tailings: Particle Size Mineralogy and Texture , 2011 .

[13]  S. Sander,et al.  Evidence for arsenic-driven redox chemistry in a wetland system: a field voltammetric study , 2010 .

[14]  E. Holley,et al.  Natural and mining-related mercury in an orogenic greywacke terrane, South Island, New Zealand , 2010 .

[15]  D. Craw,et al.  Adsorption of arsenic by iron rich precipitates from two coal mine drainage sites on the West Coast of New Zealand , 2010 .

[16]  D. Paktunc,et al.  Solubility of nanocrystalline scorodite and amorphous ferric arsenate: Implications for stabilization of arsenic in mine wastes , 2010 .

[17]  D. Craw,et al.  Field quantification and characterisation of extreme arsenic concentrations at a historic mine processing site, Waiuta, New Zealand , 2009 .

[18]  D. Pirrie,et al.  The mineralogy of efflorescence on As calciner buildings in SW England , 2009, Mineralogical Magazine.

[19]  D. Craw,et al.  Processes of attenuation of dissolved arsenic downstream from historic gold mine sites, New Zealand. , 2008, The Science of the total environment.

[20]  D. Craw,et al.  Mineralogical controls on environmental mobility of arsenic from historic mine processing residues, New Zealand , 2008 .

[21]  Bernd Nowack,et al.  Mining landscape: A cultural tourist opportunity or an environmental problem?: The study case of the Cartagena–La Unión Mining District (SE Spain) , 2008 .

[22]  John J. Mahoney,et al.  Solubility products of amorphous ferric arsenate and crystalline scorodite (FeAsO4 · 2H2O) and their application to arsenic behavior in buried mine tailings , 2006 .

[23]  D. Craw,et al.  Processes affecting the chemical composition of Blue Lake, an alluvial gold-mine pit lake in New Zealand , 2004 .

[24]  R. Brathwaite,et al.  Hydrothermal alteration in metasedimentary rock-hosted orogenic gold deposits, Reefton goldfield, South Island, New Zealand , 2003 .

[25]  P. Potts,et al.  Portable X-ray fluorescence in the characterisation of arsenic contamination associated with industrial buildings at a heritage arsenic works site near Redruth, Cornwall, UK. , 2002, Journal of environmental monitoring : JEM.

[26]  D. Hardesty Issues in Preserving Toxic Wastes as Heritage Sites , 2001 .

[27]  José M. Torres-Ruiz,et al.  Tertiary and Quaternary alluvial gold deposits of Northwest Spain and Roman mining (NW of Duero and Bierzo Basins) , 2000 .

[28]  M. Stewart,et al.  Structural setting of the Globe‐Progress and Blackwater gold mines, Reefton goldfield, New Zealand , 2000 .

[29]  B. Lottermoser,et al.  Arsenic contamination at the Mole River mine, northern New South Wales , 1999 .

[30]  G. Mew,et al.  Soil variation on steep greywacke slopes near Reefton, Western South Island , 1994 .

[31]  V. Ettel,et al.  Solubilities and stabilities of ferric arsenate compounds , 1989 .