Treatment and recovery of iron from acid mine drainage: a pilot-scale study

Author(s):  
Xin Hu ◽  
Hong Yang ◽  
Keyan Tan ◽  
Shitian Hou ◽  
Jingyi Cai ◽  
...  
2016 ◽  
Vol 130 ◽  
pp. 116-125 ◽  
Author(s):  
Erin J. Clyde ◽  
Pascale Champagne ◽  
Heather E. Jamieson ◽  
Caitlin Gorman ◽  
John Sourial

2012 ◽  
Vol 65 (2) ◽  
pp. 324-331 ◽  
Author(s):  
J. Mulopo ◽  
J. N. Zvimba ◽  
H. Swanepoel ◽  
L. T. Bologo ◽  
J. Maree

Batch regeneration of barium carbonate (BaCO3) from barium sulphide (BaS) slurries by passing CO2 gas into a pilot-scale bubbling column reactor under ambient conditions was used to assess the technical feasibility of BaCO3 recovery in the Alkali Barium Calcium (ABC) desalination process and its use for sulphate removal from high sulphate Acid Mine Drainage (AMD). The effect of key process parameters, such as BaS slurry concentration and CO2 flow rate on the carbonation, as well as the extent of sulphate removal from AMD using the recovered BaCO3 were investigated. It was observed that the carbonation reaction rate for BaCO3 regeneration in a bubbling column reactor significantly increased with increase in carbon dioxide (CO2) flow rate whereas the BaS slurry content within the range 5–10% slurry content did not significantly affect the carbonation rate. The CO2 flow rate also had an impact on the BaCO3 morphology. The BaCO3 recovered from the pilot-scale bubbling column reactor demonstrated effective sulphate removal ability during AMD treatment compared with commercial BaCO3.


Author(s):  
Stoyan N. Groudev ◽  
Plamen S. Georgiev ◽  
Irena I. Spasova ◽  
Anatoli T. Angelov ◽  
Kostas Komnitsas

2013 ◽  
Vol 68 (6) ◽  
pp. 1406-1411 ◽  
Author(s):  
J. N. Zvimba ◽  
M. Mathye ◽  
V. R. K. Vadapalli ◽  
H. Swanepoel ◽  
L. Bologo

This study investigated Fe(II) oxidation during acid mine drainage (AMD) neutralization using CaCO3 in a pilot-scale Sequencing Batch Reactor (SBR) of hydraulic retention time (HRT) of 90 min and sludge retention time (SRT) of 360 min in the presence of air. The removal kinetics of Fe(II), of initial concentration 1,033 ± 0 mg/L, from AMD through oxidation to Fe(III) was observed to depend on both pH and suspended solids, resulting in Fe(II) levels of 679 ± 32, 242 ± 64, 46 ± 16 and 28 ± 0 mg/L recorded after cycles 1, 2, 3 and 4 respectively, with complete Fe(II) oxidation only achieved after complete neutralization of AMD. Generally, it takes 30 min to completely oxidize Fe(II) during cycle 4, suggesting that further optimization of SBR operation based on both pH and suspended solids manipulation can result in significant reduction of the number of cycles required to achieve acceptable Fe(II) oxidation for removal as ferric hydroxide. Overall, complete removal of Fe(II) during AMD neutralization is attractive as it promotes recovery of better quality waste gypsum, key to downstream gypsum beneficiation for recovery of valuables, thereby enabling some treatment-cost recovery and prevention of environmental pollution from dumping of sludge into landfills.


2014 ◽  
Vol 73 (8) ◽  
pp. 4717-4727 ◽  
Author(s):  
Giljae Yim ◽  
Sangwoo Ji ◽  
Youngwook Cheong ◽  
Carmen Mihaela Neculita ◽  
Hocheol Song

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