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Acid mine water reclamation using the ABC process

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dc.contributor.author De Beer, Morris
dc.contributor.author Maree, JP
dc.contributor.author Wilsenach, J
dc.contributor.author Motaung, S
dc.contributor.author Bologo, L
dc.contributor.author Radebe, V
dc.date.accessioned 2011-08-29T13:13:13Z
dc.date.available 2011-08-29T13:13:13Z
dc.date.issued 2010-09
dc.identifier.citation De Beer, M., Maree, J.P., Wilsenach, J., et al. 2010. Acid mine water reclamation using the ABC process. International Mine Water Association Symposium. Cape Brenton University, Sydney, Nova Scotia, Canada, 4-9 Sept 2010, pp. 6 en_US
dc.identifier.uri http://hdl.handle.net/10204/5137
dc.description International Mine Water Association Symposium. Cape Brenton University, Sydney, Nova Scotia, Canada, 4-9 Sept 2010 en_US
dc.description.abstract The gold mines on which much of South Africa’s wealth was founded are closed or closing. Mining concerns therefore have stopped pumping underground water from the mines which are filling with water (AMD) that is acidic, saline and vitiated with metals from iron to uranium. By 2002 the West Rand Basin’s mines were all flooded and some 15 million litres of AMD started to decant each day. The acid mine drainage (AMD) of this area (region) is characterised by a pH of around 3 and by concentrations of about 2 to 4.5 g/L of sulphate, 250 to 1200 mg/L of Ferrous iron, 60 to 175 mg/L of Mn and 120 mg/L of Mg. The CSIR ABC desalination process, developed for AMD neutralisation and the removal of total dissolved solids from 2 600 to 360 mg/L was demonstrated at a pilot plant. Metals were effectively removed through precipitation with CaS, Ca(HS)2 or Ca(OH)2. The tests showed that during pre-treatment, sulphate was lowered from 4 500 mg/L to 1 250 mg/L by gypsum crystallization; metals were precipitated to low values as either hydroxides or sulfides, depending on the precipitation agent used. The BaCO3 treatment then lowered sulphate to less than 100 mg/L. The alkalinity of the calcium bicarbonate-rich water was reduced from 1 000 to 110 mg/L (as CaCO3). Raw materials for the water treatment stage were recovered through the sludge processing stage. CaS or Ca(HS)2 was produced from the CaSO4 sludge and BaCO3 from the BaSO4/CaCO3 sludge en_US
dc.language.iso en en_US
dc.relation.ispartofseries Workflow;4531
dc.subject ABC process en_US
dc.subject AMD treatment en_US
dc.subject BaCO3 en_US
dc.subject Sludge processing en_US
dc.subject Acid mine water en_US
dc.subject Mine water en_US
dc.title Acid mine water reclamation using the ABC process en_US
dc.type Conference Presentation en_US
dc.identifier.apacitation De Beer, M., Maree, J., Wilsenach, J., Motaung, S., Bologo, L., & Radebe, V. (2010). Acid mine water reclamation using the ABC process. http://hdl.handle.net/10204/5137 en_ZA
dc.identifier.chicagocitation De Beer, Morris, JP Maree, J Wilsenach, S Motaung, L Bologo, and V Radebe. "Acid mine water reclamation using the ABC process." (2010): http://hdl.handle.net/10204/5137 en_ZA
dc.identifier.vancouvercitation De Beer M, Maree J, Wilsenach J, Motaung S, Bologo L, Radebe V, Acid mine water reclamation using the ABC process; 2010. http://hdl.handle.net/10204/5137 . en_ZA
dc.identifier.ris TY - Conference Presentation AU - De Beer, Morris AU - Maree, JP AU - Wilsenach, J AU - Motaung, S AU - Bologo, L AU - Radebe, V AB - The gold mines on which much of South Africa’s wealth was founded are closed or closing. Mining concerns therefore have stopped pumping underground water from the mines which are filling with water (AMD) that is acidic, saline and vitiated with metals from iron to uranium. By 2002 the West Rand Basin’s mines were all flooded and some 15 million litres of AMD started to decant each day. The acid mine drainage (AMD) of this area (region) is characterised by a pH of around 3 and by concentrations of about 2 to 4.5 g/L of sulphate, 250 to 1200 mg/L of Ferrous iron, 60 to 175 mg/L of Mn and 120 mg/L of Mg. The CSIR ABC desalination process, developed for AMD neutralisation and the removal of total dissolved solids from 2 600 to 360 mg/L was demonstrated at a pilot plant. Metals were effectively removed through precipitation with CaS, Ca(HS)2 or Ca(OH)2. The tests showed that during pre-treatment, sulphate was lowered from 4 500 mg/L to 1 250 mg/L by gypsum crystallization; metals were precipitated to low values as either hydroxides or sulfides, depending on the precipitation agent used. The BaCO3 treatment then lowered sulphate to less than 100 mg/L. The alkalinity of the calcium bicarbonate-rich water was reduced from 1 000 to 110 mg/L (as CaCO3). Raw materials for the water treatment stage were recovered through the sludge processing stage. CaS or Ca(HS)2 was produced from the CaSO4 sludge and BaCO3 from the BaSO4/CaCO3 sludge DA - 2010-09 DB - ResearchSpace DP - CSIR KW - ABC process KW - AMD treatment KW - BaCO3 KW - Sludge processing KW - Acid mine water KW - Mine water LK - https://researchspace.csir.co.za PY - 2010 T1 - Acid mine water reclamation using the ABC process TI - Acid mine water reclamation using the ABC process UR - http://hdl.handle.net/10204/5137 ER - en_ZA


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