title: Interaction of acid mine drainage with Ordinary Portland Cement blended solid residues generated from active treatment of acid mine drainage with coal fly ash.
abstract: Fly ash (FA) has been investigated as a possible treatment agent for Acid mine drainage (AMD) and established to be an alternative, cheap and economically viable agent compared to the conventional alkaline agents. However, this treatment option also leads to generation of solid residues (SR) that require disposal and one of the proposed disposal method is a backfill in coal mine voids. In this study, the interaction of the SR with AMD that is likely to be present in such backfill scenario was simulated by draining columns packed with SR and SR + 6% Ordinary Portland Cement (OPC) unsaturated with simulated AMD over a 6 month period. The evolving geochemistry of the liquid/solid (L/S) system was evaluated in-terms of the mineral phases likely or controlling contaminants attenuation at the different pH regimes generated. Stepwise acidification of the percolates was observed as the drainage progressed. Two pH buffer zones were observed (7.5-9 and 3-4) for SR and (11.2-11.3 and 3.5-4) for SR + 6% OPC. The solid residue cores (SR) appeared to have a significant buffering capacity, maintaining a neutral to slightly alkaline pH in the leachates for an extended period of time (97 days: L/S 4.3) while SR + 6% OPC reduced this neutralization capacity to 22 days (L/S 1.9). Interaction of AMD with SR or SR + 6% OPC generated alkaline conditions that favored precipitation of Fe, Al, Mn-(oxy) hydroxides, Fe and Ca-Al hydroxysulphates that greatly contributed to the contaminants removal. However, precipitation of these phases was restricted to the pH of the leachates remaining at neutral to circum-neutral levels. Backfill of mine voids with SR promises to be a feasible technology for the disposal of the SR but its success will greatly depend on the disposal scenario, AMD generated and the alkalinity generating potential of the SR. A disadvantage would be the possible re-dissolution of the precipitated phases at pH < 4 that would release the contaminants back to the water column. However extrapolation of this concept to a field scenario can greatly enhance beneficial application of fly ash (FA) and solid residues (SR) generated from treatment of AMD.
authors.affiliation: Department of Ecology and Resources Management, School of Environmental Studies, University of Venda, South Africa.
authors.forename: Wilson M
authors.initials: WM
authors.lastname: Gitari
authors.forename: Leslie F
authors.initials: LF
authors.lastname: Petrik
authors.forename: David L
authors.initials: DL
authors.lastname: Key
authors.forename: Charles
authors.initials: C
authors.lastname: Okujeni
mesh_terms: D017610:Calcium Compounds / Q000737:chemistry*; D002244:Carbon / Q000737:chemistry*; D060729:Coal Ash; D003032:Coal Mining; D004785:Environmental Pollutants / Q000032:analysis* / Q000737:chemistry; D055593:Geological Phenomena; D006863:Hydrogen-Ion Concentration; D008855:Microscopy, Electron, Scanning; D008962:Models, Theoretical; D052638:Particulate Matter / Q000737:chemistry*; D012037:Refuse Disposal / Q000379:methods*; D017640:Silicates / Q000737:chemistry*; D013019:South Africa; D013052:Spectrometry, X-Ray Emission; D013464:Sulfuric Acids / Q000032:analysis* / Q000737:chemistry; D013499:Surface Properties; D014865:Waste Disposal, Fluid / Q000379:methods
chemical_list: D017610:Calcium Compounds; D060729:Coal Ash; D004785:Environmental Pollutants; D052638:Particulate Matter; D017640:Silicates; D013464:Sulfuric Acids; D002244:Carbon; C033158:sulfuric acid; C031293:calcium silicate