DOI https://doi.org/10.36487/ACG_repo/605_58
Cite As:
Sutton, MW, Weiersbye, IM, Galpin, JS & Heller, D 2006, 'A GIS-Based History of Gold Mine Residue Deposits and Risk Assessment of Post-Mining Land-Uses on the Witwatersrand Basin, South Africa', in AB Fourie & M Tibbett (eds),
Mine Closure 2006: Proceedings of the First International Seminar on Mine Closure, Australian Centre for Geomechanics, Perth, pp. 667-678,
https://doi.org/10.36487/ACG_repo/605_58
Abstract:
In 1886, an Australian prospector named George Harrison discovered gold in the Main Reef Conglomerates
on the farm Langlaagte, which now falls within the present day City of Johannesburg. Since then, hundreds
of mine residue deposits (MRDs) have been built across the Witwatersrand Basin. By the mid-1970s, gold
recovery processes had improved sufficiently to also allow residual gold from old MRDs to be recovered at a
profit. This resulted in dump reprocessing operations and the clearing of soils previously covered by MRDs
(`footprints’). Estimates put the area of MRDs and ‘footprints’ at between 400 and 500 km2, comprising
some 6 billion t of tailings (Chevrel et al., 2003), containing approximately 430000 t of low-grade uranium
(Winde et al., 2004) and 30 million t of sulphur (Witkowski and Weiersbye, 1998).
Historically, mining companies often located MRDs in sensitive areas and employed no pollution control.
Acid mine drainage (AMD) is associated with Witwatersrand gold mines and MRDs (Maree et al., 1996),
and contamination from gold mining has been identified many kilometres downstream from the original
sources (Naiker et al., 2003). An argument on the environmental merit of dump reprocessing is that this
provides opportunity to relocate residues to more appropriate and better contained sites. However, there is
also evidence that reprocessing exacerbates contamination though exposure of previously anaerobic tailings
to air and water (Tutu et al., 2005).
With the curtailing of mining activities and clearing of land previously covered by MRDs, there comes a
demand to use this land for residential, agricultural or industrial purposes. In South Africa, the right to an
environment not harmful to a person’s health and wellbeing, and the right to the protection of the
environment are basic constitutional human rights (s24 of the Constitution of the Republic of South Africa
108 of 1996). Thus there is a need to understand the extent and types of contamination, and the potential
risks associated with different land-uses not only on mining land after closure, but on other affected land.
Baseline environmental conditions were rarely established prior to commencing with mining operations and
subsequent dump reprocessing. In order for such operations to achieve mine closure it is necessary that they
obtain agreement with Government regarding the limits of their liabilities, which could originate from up to
120 years of mining by numerous companies, many of which no longer exist. Historical aerial photographs
and satellite-based earth observation systems are powerful tools that have been used to establish culpability
(such as in the case of the failure of the Merriespruit slimes dam), but also have the potential to demonstrate
absence of liability via mapping of historical contamination that pre-dates current mining operations.
The aim of this study is to determine the adequacy of historical aerial photographs and satellite thematic
imagery (TERRA satellite ASTER images), integrated with geographic information systems (GIS)-based
metadata, for visualising historical contamination emanating from MRDs in a representative semi-arid gold
and uranium-mining region (the East Rand of Johannesburg). This aim is of value in establishing
standardized tools for mapping mine impacts, in order to focus environmental cleanup, demonstrate
compliance, and assist in closure planning.
Mine Closure 2006 ― Andy Fourie and Mark Tibbett (eds)
© 2006 Australian Centre for Geomechanics, Perth, ISBN 0-9756756-6-4
Mine Closure 2006, Perth, Australia 667
References:
Agresti, A. (1996) An introduction to categorical data analysis. Wiley, New York.
Chevrel, S., Courant, C., Cottard, F., Coetzee, H., Bourguignon, A. and Ntsume, G. (2003) Very high resolution remote
sensing coupled to GIS-based environmental assessment – East Rand goldfield, South Africa. Report
BRGM/RP-52724-FR.
Hodgson, F.D.I., Usher., B.H., Scott, R., Zeelie, S., Cruywagen, L-M. and de Necker, E. (2001) Prediction techniques
and preventative measures relating to the post-operational impact of underground mines on the quality and
quantity of groundwater resources. WRC Report No. 699/1/01.
Maree, J.P., van Tonder, G.J. and Millard, P. (1996) Underground Neutralisation of Mine Water with Limestone.
Report to the Water Research Commission by the Division of Water, Environment and Forestry Technology,
CSIR WRC Report No 609/1/96, 51 p.
Marschner, H. (1995) Mineral Nutrition of Higher Plants. Second Edition. Academic Press, London, 889 p.
Mphephu, N.F., Viljoen, M.J. and Annegarn, H.J. (2003) Geochemistry of mine tailings and contribution to soil and
water pollution on the Central Rand. In Implementing sustainable development in mining: From talk to action.
Chamber of Mines of South Africa, Mining and Sustainable Development Conference, Sandton, 3-5 November,
7C-9 to 7C-15.
Naicker, K., Cukrowska, E. and McCarthy, T.S. (2003) Acid mine drainage arising from gold mining activity in
Johannesburg, South and environs. Journal of Environmental Pollution. 122, pp. 29-40.
Richter, R. (2003) ATCOR 2.3 User guide. DLR- German Aerospace Center, Remote Sensing data center, Wessling,
Germany.
Steenekamp, V., Stewart, M. and Cukrowska, E.M. (2002) A severe case of multiple metal poisoning in a child treated
with a traditional medicine. Forensic Science International 3397, pp. 1-4.
Steenekamp, V., Stewart, M., Chimuka, L. and Cukrowska, E.M. (2005) Uranium concentrations in South African
herbal remedies, Health Physics, 2005 89(6), pp. 679-683.
Contaminant Risks and Off-Site Impacts
Mine Closure 2006, Perth, Australia 677
Tucker, C.J. (1979) Red and Photographic Infrared Linear Combinations for Monitoring Vegetation. Remote Sensing of
the Environment 8, pp. 127-150.
Tutu, H., Cukrowska, E.M., McCarthy, T.S., Mphephu, N.F. and Hart, R. (2003) Determination and modelling of
geochemical speciation of uranium in gold mine polluted land in South Africa. In: Proceedings: 8th International
Congress on Mine Water and the Environment, Johannesburg, South Africa, pp. 137-155.
Tutu, H., Cukrowska, E.M., Dohnal, V. and Havel, J. (2005) Application of artificial neural networks for classification
of uranium distribution in the central Rand goldfield, South Africa. Environmental Modelling and Assessment,
10, pp. 143-152.
World Health Organisation. (2001) Environmental Health Criteria. WHO, Geneva.
Weiersbye, I.M., Straker, C.J. and Przybylowicz, W. (1999). Micro-PIXE mapping of elemental distribution in
arbuscular mycorrhizal roots of the grass, Cynodon dactylon, from gold and uranium mine tailings. Nuclear
Instruments and Methods in Physics Research B 158, pp. 335-343.
Weiersbye, I.M. and Witkowski, E.T.F. (2003). Acid rock drainage (ARD) from gold tailings dams on the
Witwatersrand Basin impacts on tree seed fate, inorganic content and morphology. In: Proceedings: 8th
International Congress on Mine Water and the Environment, Johannesburg, South Africa, pp. 311-328.
Winde, F., Wade, P. and van der Walt, I.J. (2004) Gold tailings as a source of waterborne uranium contamination of
streams – The Koekemoerspruit (Klerksdorp goldfield, South Africa) as a case study. Part I of III: Uranium
migration along the aqueous pathway. Water SA 30(2), pp. 219-225.
Witkowski, E.T.F. and Weiersbye, I.M. (1998) Variation in geochemistry and soil features of South African gold slimes
dams and adjacent soils. Plant Ecology and Conservation Series No. 6, Report to the Anglo-American
Corporation, 111 p.
A GIS-Based History of Gold Mine Residue Deposits and Risk Assessment
of Post-Mining Land-Uses on the Witwatersrand Basin, South Africa
M.W. Sutton, et al.
678 Mine Closure 2006, Perth, Australia