DOI https://doi.org/10.36487/ACG_rep/1152_23_Tindal
Cite As:
Tindal, MJ, Brand, D, Ludwig, B & Hackbarth, D 2011, 'Risk-based soil remediation guidelines in coal mine closure', in AB Fourie, M Tibbett & A Beersing (eds),
Mine Closure 2011: Proceedings of the Sixth International Conference on Mine Closure, Australian Centre for Geomechanics, Perth, pp. 209-215,
https://doi.org/10.36487/ACG_rep/1152_23_Tindal
Abstract:
The closure of coal mines and associated processing facilities presents many challenges, including the management of contaminant chemicals that may have been released over a potentially long and varied history of industrial activity at a site. However, the high carbon content of coal waste material that may be present at some facilities can actually facilitate site closure by decreasing the mobility of organic contaminants. The Coleman Collieries facility, located in the Municipality of Crowsnest Pass in south west Alberta, Canada operated for approximately 80 years as a coal mining and processing facility. During that time, coal waste and unmarketable coal fines from settling ponds were placed over much of the facility to a depth of 3–4 m. The Province of Alberta, like many jurisdictions, uses risk-based soil guidelines as one of the criteria in assessing whether land, such as a former mine facility, is suitable for a proposed post-closure use. Assessment of the Coleman facility found a range of contaminants exceeding Alberta’s default soil guidelines including benzene, toluene, ethylbenzene, and xylenes (BTEX) and other hydrocarbon compounds and fractions. Alberta’s soil guidelines were developed to be protective of a range of exposure pathways including vapour migration into indoor air spaces and groundwater transport to potential aquifers or surface water bodies. However, these guidelines were developed based on the expected mobility of organic compounds in typical subsoils with low organic carbon contents. Site-specific soil guidelines were developed for the Coleman facility which took into account the much higher carbon content of soils at this facility, to more accurately determine the remedial actions required for site closure.
References:
AENV (2010a) Alberta Environment, Alberta Tier 1 Soil and Groundwater Remediation Guidelines, December 2010.
AENV (2010b) Alberta Environment, Alberta Tier 2 Soil and Groundwater Remediation Guidelines, December 2010.
ESG (2003) ESG International Inc., Toxicity of Petroleum Hydrocarbons to Soil Organisms and the Effects on Soil Quality: Phase 1, Fraction-Specific Toxicity of Crude Oil, Report dated January 30, 2003, prepared for Petroleum Technology Alliance Canada, viewed June 2011,
.
Hulzebos, E.M., Adema, D.M.M. and Dirven-van Breeman, E.M. (1993) Phytotoxicity studies with Lactuca sativa in soil and nutrient solution, Environmental Toxicology and Chemistry, Vol. 12, pp. 1079–1094.
Van Gestel, C.A.M., and Ma, W. (1988) Toxicity and bioaccumulation of chlorophenols in earthworms in relation to bioavailability in soil, Ecotoxicology and Environmental Safety Vol. 15, pp. 289–291.
Van Gestel, C.A.M., and Ma, W. (1990) An approach to quantitative structure-activity relationships (QSARs) in earthworm toxicity studies, Chemosphere, Vol. 21, pp. 1023–1033.
Van Gestel, C.A.M., Ma, W. and Smit, C.E. (1991) Development of QSARs in terrestrial ecotoxicology: Earthworm toxicity and soil sorption of chlorophenols, chlorobenzenes, and dichloroanaline, Science of the Total Environment, Vol. 109/110, pp. 589–604.