Acid mine drainage in the Bakers Creek waste rock dump, Hercules, Western Tasmania
Smith, SE (1998) Acid mine drainage in the Bakers Creek waste rock dump, Hercules, Western Tasmania. Honours thesis, University of Tasmania.
Mining has occurred at the Hercules Ag, Au, Cu, Pb, Zn VHMS deposit in western
Tasmania, almost continuously for the last I 00 years. Mining activity has degraded the
local environment, through clearing of vegetation, enhanced erosion and the formation of
acid mine drainage (AMD). Of significant concern is the Bakers Creek waste rock dump,
situated in a waterfall in the upper reaches of Bakers Creek. This steep, unstable sulfidic
rock pile cannot be readily removed or engineered, and is an on-going source of AMD. To
allow rehabilitation options for the waste rock dump to be devised, the contribution of
AMD from the Bakers Creek waste rock dump needed to be ascertained.
Long term and intensive water sampling programs have been implemented to characterise
and quantify AMD emanating from the waste rock dump, and to investigate climatic
controls on water quality of Bakers Creek. Water samples were collected from ten sites
along Bakers Creek, where field analyses of pH, Eh, conductivity and temperature were
conducted. Water samples were collected for laboratory analyses of major and trace
element concentrations, sulphate, chloride and alkalinity.
The pH of the drainage waters vary from 5.6 (upstream of mining activity) to 3.0 (foot of
the waste rock dump). Maximum metal concentrations were measured at the adit, or the
base of the waste rock dump. Major contaminants are Fe (43.8ppm), Pb (19.2ppm), AI
(8.47ppm) and Sulfate (1440ppm) and Zn (82.2ppm). During base flow, approximately
47.6 T/yr of Zn is discharging from Bakers Creek into Ring River, (98% of which is
contributed by the waste rock dump). Other contaminants contributed by the waste rock
dump, represented at least 95% of the total contamination in Bakers Creek including AI
(2.87 T/yr), Cu (0.77 T/yr), Fe (1.54 T/yr), Pb 1.9 T/yr, and Sulfate, (199T/yr). The
maximum mass loads were recorded during storm events (measured at the base of Bakers
Creek). The maximum mass load for each contaminant was 158.9 T/yr Zn, 13.9 T/yr AI,
0.33 T/yr Cd, 3.95 T/yr Cu, 65.4 T/yr Fe, 56.15 T/yr Mn, 23.75 Pb T/yr, and 756 T/yr
sulphate. These metal mass loads are high enough to consider metal recovery strategies.
To remediate Bakers Creek, a combination of treatment strategies are probably required.
Diversion of Bakers Creek upstream of the waste rock dump, combined with the
installation of a biosulphide metal recovery plant to treat Zn, have potential to reduce
metal and sulphate concentrations to acceptable levels, and to increase pH. A major advantage would be the metals can be extracted from solution and sold to create revenue to
offset costs incurred from installing and operating the plant. Diversion of Bakers Creek
combined with a wetland filter system at Williamsford, could be an alternative remediation
strategy if a biosulphide treatment is not viable.
|Item Type:||Thesis (Honours)|
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|Deposited On:||23 Jun 2012 17:38|
|Last Modified:||02 Sep 2012 14:30|
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