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Annual Meeting Preliminary Program - Full Brochure (PDF) - SME

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ent on the bleeder entry conditions and many other contributing factors. This<br />

study is an investigation of the locations of hot-spots in the gob using CFD<br />

(Computational Fluid Dynamics) package. It also includes permeability<br />

measurements on selected coal samples, and studies on the effectiveness of<br />

existing and proposed ventilation systems.<br />

3:45 PM<br />

Skyline Mine - A case study in two-entry coal mining<br />

G. Kenzy; Skyline Mine, Helper, UT<br />

This paper describes and illustrates the Skyline Mine primary ventilation system<br />

and the ventilation of two-entry longwall gateroads during development<br />

and retreat longwall mining. The mine-wide utilization of an atmospheric<br />

monitoring system and the specific mine atmospheric monitoring requirements<br />

in two-entry development and retreat mining is presented and analyzed.<br />

The efficiency and performance of the mine, gateroad and bleeder ventilation<br />

systems are described, analyzed and illustrated using computer-based<br />

ventilation network modeling. Spontaneous combustion prevention in both<br />

ventilated and sealed longwall gobs is detailed, including a description and<br />

examples of the instrumentation and procedures used.<br />

Chair:<br />

Environmental: Acid Rock Drainage<br />

2:00 PM • Tuesday, February 26<br />

R. Williams, Bureau of Land Management, Butte, MT<br />

2:05 PM<br />

Culturing and Characterization of Rock Pile Microbes<br />

J. Kennedy, B. Richins and D. Adams; University of Utah,<br />

Salt Lake City, UT<br />

Expansive rock piles are often generated during large-scale mining operations.<br />

Microorganisms can directly contribute weathering actions and accelerate<br />

reactions that contribute to stability or instability within rock piles.<br />

Pared rock pile samples were collected for microbial and geochemical analysis<br />

to examine microbial variation across geological zones and geochemistry.<br />

Microbial populations were examined using selected microbial media, classical<br />

culture techniques, and nucleic acid profiling. The information gathered<br />

was used to examine the microbial populations relative to the site, across geological<br />

zones found within the rock pile, and geochemical parameters.<br />

Microbial populations found included aerobic and facultative anaerobic sp.,<br />

sulfate and iron reducing and oxidizing sp., Archea sp., Thiobacillus and<br />

Leptosprillum sp, denitrifying sp., and acidophilic species. Denaturing gradient<br />

gel electrophoresis (DGGE) was used to generate microbial population<br />

nucleic acid profiles for selected cultures obtained from different rock pile<br />

samples. Selected sequences from the profiles generated were further<br />

analyzed to identify the specific microbes present.<br />

2:25 PM<br />

Arsenic Binding Proteins for Removal of Arsenic From Solution<br />

J. Kennedy 1 , B. Richins 2 and D. Adams 3 ; 1 Metallurgical Engineering,<br />

University of Utah, Salt Lake City, UT; 2 Metallurgical Engineering,<br />

University of Utah, Salt Lake City, UT and 3 Metallurgical Engineering,<br />

University of Utah, Salt Lake City, UT<br />

Removal of soluble forms of arsenic from water is an expensive process.<br />

Alginate biopolymer bead immobilization was selected as a method to evaluate<br />

the ability of arsenic binding proteins to remove arsenic from water.<br />

Protein extracts were obtained from several microbial consortiums selected<br />

for their ability to reduce soluble metalloids. Immobilized protein extracts at<br />

a concentration 0.50 mg/ml yielded near maximal arsenic removal. Arsenic<br />

removal was somewhat dependent on temperature and pH, with maximum<br />

removal occurring at about 35° C and pH of 5.8. Kinetics studies show that<br />

selected protein mixtures remove ~98% of soluble arsenic in 24 hours. When<br />

compared with the live microbes from which they were extracted, the immobilized<br />

proteins bind more than four times the arsenic. Immobilization of<br />

arsenic-binding proteins permits arsenic recovery and potential reuse of the<br />

immobilization biopolymer-protein complex. Additional data will be<br />

presented on the arsenic-binding proteins, functional lifespan of various<br />

immobilization biopolymer-protein complexes, and arsenic removal in a<br />

bench scale bioreactor.<br />

2:45 PM<br />

Optimisation of single-layer cover made of desulphurized tailings :<br />

application to the Doyon mine tailings impoundment<br />

I. Demers 1 , B. Bussiere 1 , M. Mbonimpa 1 and A. Blier 2 ; 1 UQAT, Rouyn-<br />

Noranda, QC, Canada and 2 UQAT, Rouyn-Noranda, QC, Canada<br />

Doyon mine, Quebec, Canada evaluates the possibility of desulphurizing<br />

their tailings to produce material to be used in as cover over their acid generating<br />

tailings impoundment. Laboratory tests were conducted and showed<br />

that a single-layer desulphurized tailings cover placed over reactive tailings<br />

can prevent the generation of acid mine drainage. Modelling with the software<br />

Vadose was undertaken to optimize the design parameters, namely<br />

cover thickness, water table position, and residual sulphide content of desulphurized<br />

tailings following laboratory work. The optimal scenario for the<br />

Doyon mine tailings impoundment was selected according to a maximal<br />

acceptable oxygen flux reaching the reactive tailings predicted by the model.<br />

3:05 PM<br />

Arsenic retention by soil mineral components is inhibited by natural<br />

organic matter<br />

A. Redman 1 , D. Macalady 2 , D. Ahmann 2 and K. Ritter 2 ; 1 HydroQual,<br />

Millville, UT and 2 Colorado School of Mines, Golden, CO<br />

Inorganic arsenic species (e.g. arsenate and arsenite) are commonly found in<br />

acid rock drainage. The migration and retention of these inorganic arsenic<br />

species by soils or sediment are generally controlled by the adsorption of<br />

these compounds to iron and aluminum oxides. This reaction can be strongly<br />

affected by certain water quality characteristics. Dissolved, naturally occurring<br />

organic matter (NOM) from stream water was shown to dramatically reduce<br />

the rate and extent of arsenate and arsenite retention by a pure ironoxide<br />

mineral and by natural soils or sands. The apparent decline in arsenic<br />

removal by the presence of NOM is due to three major process: 1) competitive<br />

adsorption of NOM to the mineral phases, 2) formation of stable aqueous,<br />

or colloidal complexes that reduces that availability of arsenic to bind to<br />

soil minerals and 3) NOM promotes the reduction of arsenate to a more<br />

mobile form of arsenite. Stable aqueous complexes are thought to occur<br />

through the formation of dissolved ternary NOM-metal-arsenic complexes<br />

that are most likely mediated by iron or aluminum ions.<br />

3:25 PM<br />

Update on the INAP GARD Guide<br />

T. Chatwin 1 and K. Ferguson 2 ; 1 Technical Manager, INAP, Salt Lake City,<br />

UT and 2 Principal, Sustainability Engineering, Vancouver, BC, Canada<br />

The objective of the INAP GARD Guide (Global Acid Rock Drainage Guide)<br />

is to produce the broadest and most up-to-date reference for the mining industry,<br />

regulators, NGO’s and the public on the subject of acid-rock drainage<br />

(ARD). The Guide will address the production of contaminants from sulfide<br />

mineral oxidation that can result in ARD, neutral mine drainage (NMD) and<br />

saline mine drainage (SD). The GARD Guide is bringing together best technical<br />

and management practices with the objective of creating a body of work<br />

with high industry and external stakeholder credibility. The Guide will cover<br />

all phases of a mining operation from initial discovery through to final closure<br />

(“cradle-to-cradle”). Thus, it will assist industry in providing high levels<br />

of environmental protection, assist governments in the assessment and regulation<br />

of facilities under their jurisdiction and enable the public to have a<br />

higher degree of confidence in and understanding of acid prevention<br />

proposals and practices.<br />

3:45 PM<br />

Automated Mineralogy in the prediction of Acid Rock Drainage:<br />

Accessible mineralogy using QEMSCAN®<br />

W. Goodall; Intellection Pty Ltd, Brisbane, QLD, Australia<br />

Mineralogy is a key driver in Acid Rock Drainage (ARD) and yet access to<br />

routine and scalable mineral identification techniques has been limited on the<br />

scale required for accurate ARD prediction. Quantitative X-Ray Diffraction<br />

(XRD) has been utilised but is limited in its achievable detection limits for<br />

minerals of interest. An alternative, with cost comparisons, is proposed using<br />

QEMSCAN® for quantitative bulk mineralogical analysis. The use of QEM-<br />

SCAN® makes routine mineralogical analysis a cost effective and useful addition<br />

to ARD characterisation programs opening up new possibilities for the<br />

application of mineralogical information in better ARD management.<br />

State-of- the-art Woldwide Technical Information!<br />

45

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