Annual Meeting Preliminary Program - Full Brochure (PDF) - SME
Annual Meeting Preliminary Program - Full Brochure (PDF) - SME
Annual Meeting Preliminary Program - Full Brochure (PDF) - SME
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TECHNICAL PROGRAM<br />
chair:<br />
2:00 PM<br />
Introductions<br />
environmental:<br />
environmental topics<br />
2:00 PM • Monday, February 25<br />
A. Duex, Rio Tinto, South Jordan, UT<br />
2:05 PM<br />
Kennecott Utah Copper Quality Hectares Assessment Framework<br />
B. Boyle 1 , M. Wheeler 3 , T. Gullison 2 and A. Neville 4 ; 1 Ecology and<br />
Evolutionary Biology, University of Arizona, Tucson, AZ; 2 Hardner<br />
& Gullison Associates, LLC, Lantzville, BC, Canada; 3 WP Natural<br />
Resource Consulting, Inc, Salt Lake City, UT and 4 Sustainable<br />
Development, Kennecott Utah Copper, South Jordan, UT<br />
Rio Tintos goal is to have a net positive impact on biodiversity in the regions<br />
where its mines operate. For most species and habitats area-based metrics adjusted<br />
for habitat quality are used to determine a sites net impact. These qualityhectares<br />
measures provide a common currency for integrating the positive and<br />
negative impacts to native vegetation at a site with the biodiversity benefits provided<br />
by reclamation and restoration. Rio Tintos Kennecott Utah Copper site in<br />
Utah developed the quality-hectares framework in the following steps: (i) identification<br />
and description of the natural vegetation communities present on property;<br />
(ii) identification of benchmark conditions of structure and composition for<br />
each vegetation type in order to function as a point of comparison for the actual<br />
natural and restored areas of vegetation present the property; and (iii) development<br />
of a scoring system for natural vegetation and reclaimed and restored sites<br />
against the benchmark sites. <strong>Preliminary</strong> results of the application of the qualityhectares<br />
framework will be presented as well as a description of the vegetation<br />
monitoring program Kennecott is implementing.<br />
2:25 PM<br />
Managing Air Quality Impacts of a Global Diversified<br />
Mining Company<br />
F. Turatti; Group HSEC, Rio Tinto, Salt Lake City, UT<br />
Rio Tinto is one of the world’s largest international mining groups with operations<br />
located in more than 50 countries in multiple continents. This diversity of<br />
operations and variation in the nature, amount and impacts of air emissions<br />
poses a significant environmental management challenge in an increasingly regulated<br />
environment. A global strategy was developed to manage air quality impacts,<br />
consisting of three objectives: improving air quality performance of operations,<br />
developing industry leading practices and engaging and influencing in air<br />
issues. Each objective is supported by comprehensive work programs that are delivered<br />
globally and tailored regionally for a holistic global approach. This presentation<br />
will discuss Rio Tintos approach to global air quality management and<br />
the successes this approach has secured. Three programs of work are highlighted.<br />
Firstly, how airshed resources are managed in constrained airsheds where we<br />
have operations. Secondly, how financial modeling has allowed a true value to be<br />
placed on air constraints and thirdly, how a rigorous e-learning course was developed<br />
to improve the overall level of air management knowledge of environment<br />
managers.<br />
2:45 PM<br />
Arsenic Leaching from a Mine Tailing by Acidithiobacillus<br />
Ferrooxidans: Role of Temperature, pH, and Pulp Density<br />
J. Park 1 , E. Lee 1 , J. Hong 1 , K. Yoo 2 , J. Park 3 , U. Choi 3 and H. Kim 1 ;<br />
1<br />
Department of Mineral Resources and Energy Engineering, Chonbuk<br />
National University, Jeonju, Republic of Korea; 2 Department of<br />
Energy & Resources Engineering, Korea Maritime University, Busan,<br />
Republic of Korea and 3 R&D Team, Institute of Mine Reclamation<br />
Corporation, Seoul, Republic of Korea<br />
Arsenic leaching behavior from a mine tailing by Acidithiobacillus Ferrooxidans<br />
(A. Ferrooxidans) was i emp=30 oC), and temperature (25-35 oC, pulp density=0.5%,<br />
pH=1.8). The reaction speed and initial cell concentration were fixed<br />
to 150 rpm and 1E8 cells/ml, respectively. To complement leaching experiments,<br />
zeta potential measurements for cells and tailings, and SEM, XRD, and particle<br />
size analyses for tailings before and after leaching were conducted. Overall, the<br />
arsenic leaching efficiency increased with decreasing pulp density, decreasing pH,<br />
and increasing temperature regardless of the presence of A. Ferrooxidans.<br />
Additionally, the arsenic leaching rate was faster for the samples in the presence<br />
of A. Ferrooxidans as compared to those in the absence of A. Ferrooxidans at the<br />
conditions investigated in this study.<br />
3:05 PM<br />
Aquatic Life Criteria Are Protective Against Copper-caused<br />
Impairment of Olfaction in Salmonid Fishes<br />
J. Meyer 1 , D. DeForest 2 , R. Gensemer 3 , J. Gorsuch 4 and W. Adams 5 ;<br />
1ARCADIS U.S., Lakewood, CO; 2 Windward Environmental,<br />
Seattle, WA; 3 GEI Consultants, Denver, CO; 4 Copper Development<br />
Association, Webster, NY and 5 Rio Tinto, Lake Point, UT<br />
Major concerns have recently been expressed that short-term exposures to low<br />
Cu concentrations might cause olfactory impairment in fish [especially migratory<br />
Pacific salmon and trout (Oncorhynchus spp.)], which might limit their ability<br />
to detect predators, reproduce, or migrate. This is becoming an important<br />
issue for the mining sector, and other metals are also of concern for olfactory impairment<br />
(e.g., Cd, Zn). However, water chemistry matters in determining lethal<br />
and sublethal effects (including olfaction) of metals to aquatic organisms. For example,<br />
although olfactory impairment can occur at low Cu concentrations in dilute<br />
laboratory waters, we demonstrate that the USEPAs biotic ligand model<br />
(BLM)-based aquatic life criteria for Cu are protective against olfactory impairment<br />
across a wide range of fresh waters. Additionally, we propose a unified<br />
freshwater-saltwater BLM to predict olfactory effects of Cu to salmonid fishes,<br />
which suggests that the threshold-effect concentrations of Cu will be even higher<br />
in salt water than in fresh water and that the current saltwater Cu criteria are protective<br />
across a wide range of saltwater chemistries.<br />
3:25 PM<br />
Regulatory Implications of Chemosensory and Behavioral Effects<br />
of Copper to Fish<br />
R. Gensemer 1 , D. DeForest 2 and J. Gorsuch 3 ; 1 Ecology Division, GEI<br />
Consultants, Inc., Denver, CO; 2 Windward Environmental, Seattle,<br />
WA and 3 Copper Development Association, Webster, NY<br />
Regulatory criteria for aquatic life protection are based primarily on laboratory<br />
toxicity data using test endpoints derived on the basis of survival, growth, and reproduction.<br />
These endpoints are believed to provide the best representation of<br />
overall ecological impacts of chemicals to aquatic organisms in the field.<br />
However, some have proposed that aquatic life criteria for copper are insufficiently<br />
protective of sublethal chemosensory and behavioral endpoints in<br />
salmonid fishes, and therefore regulatory criteria need to be revisited. We review<br />
the ecological basis of aquatic life criteria derivation using the more traditional<br />
endpoints of survival, growth, and reproduction, and discuss the extent to which<br />
other sublethal endpoints may influence how criteria are derived. For copper, we<br />
contend that traditionally based aquatic life criteria are adequately protective<br />
against chemosensory or behavioral effects in salmonid fishes. This is because<br />
other aquatic species are more sensitive to copper than salmon, but also owing to<br />
the influence of water chemistry on the toxicity of copper regardless of whether<br />
traditional or non-traditional sublethal endpoints are considered.<br />
chair:<br />
2:00 PM<br />
Introductions<br />
environmental:<br />
uranium<br />
2:00 PM • Monday, February 25<br />
G. Robinson, R Squared, Inc., Greenwood Village, CO<br />
2:05 PM<br />
Are We There Yet?<br />
W. Heili; Ur-Energy, Casper, WY<br />
Eight years after the initiation of permitting activities for Ur-Energy’s Lost Creek<br />
Project, the long road is coming to a successful conclusion. Facility construction<br />
is scheduled to be underway in the fall of 2012 with production commencing in<br />
2013. This presentation will take a look back at some of the pioneering efforts<br />
that went into permitting of a new ISR uranium production facility in Wyoming.<br />
Additionally, the presentation will review several technological and design innovations<br />
that are featured in the production plant and well field designs for this<br />
state-of-the-art In Situ Recovery site.<br />
This is the Technical <strong>Program</strong> as of September 1, 2012. IT IS SUBJECT TO CHANGE.<br />
50<br />
Please see the Onsite <strong>Program</strong> for final details.