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EXECUTIVE SUMMARY<br />

1.5.2.1.3 Key Species Loss <br />

Key species included in the study were those on the US Forest Service (USFS) Threatened and <br />

Endangered Species list, or the International Union for the Conservation <strong>of</strong> Nature Red List <strong>of</strong> <br />

Threatened Species. 34,35 The assessment for terrestrial habitat disturbance was based on the same <br />

methods used to assess terrestrial biome disturbance; however, no data were available to quantify <br />

the spatial extent or severity <strong>of</strong> disturbance to wetland or freshwater habitats. The list <strong>of</strong> species <br />

impacted was compiled without assessment <strong>of</strong> these distinct category indicators. <br />

When considering the number <strong>of</strong> species impacted, the BAU scenario has higher impacts, affecting <br />

almost 90 species. Seven <strong>of</strong> these species experienced disturbance to terrestrial habitats, for which <br />

indicator results were assessed. An additional eighty-­‐one <strong>of</strong> these species experienced disturbance to <br />

freshwater and/or wetland habitats; however, indicator results could not be quantified for these <br />

species, due to a lack <strong>of</strong> data. <br />

1.5.3 Lower Hazardous Emissions Associated with Impacts to Humans, Flora and Fauna <br />

Emissions from arsenic and chromite ore extraction, required for CCA production, have impacts that <br />

are significant in nature and large in spatial extent. Another impact to human health is the degree to <br />

which workers are exposed to toxic herbicides during forestry operations. These are primary <br />

consequences <strong>of</strong> the BAU scenario; the secondary consequences from implementation <strong>of</strong> the SPR <br />

scenario are projected to lead to a decline in arsenic ore mining and smelting activities in China, <br />

resulting in impact reductions for human health and the environment. <br />

1.5.3.1 Emissions from Arsenic Ore Extraction <br />

Due to environmental concerns from mining and smelting, arsenic trioxide has not been produced in <br />

the United States since 1985. In response to environmental concerns and human health issues, the <br />

wood-­‐preserving industry made a voluntary decision to stop using CCA to treat wood for decks and <br />

outdoor residential use in 2003; however, because <strong>of</strong> known performance and lower costs, CCA is still <br />

used in nonresidential applications, such as the treatment <strong>of</strong> utility poles. 36<br />

Due to this voluntary ban on CCA use for most wood products, imports <strong>of</strong> arsenic trioxide (the <br />

primary chemical constituent <strong>of</strong> CCA) into the United States have declined since 2003 by roughly <br />

70%, when roughly 20,000 tons <strong>of</strong> this material was imported. The arsenic trioxide used in the BAU <br />

scenario is mined in China, by far the largest producer <strong>of</strong> arsenic trioxide worldwide. 37 China <br />

produces significant amounts <strong>of</strong> arsenic ores (primarily realgar and orpiment), and also manufactures <br />

34 United States Fish and Wildlife Service: Endangered Species Program. Species Searchmap. Accessed on 2/24/2012 from <br />

http://www.fws.gov/endangered/species/index.html. <br />

35 International Union for the Conservation <strong>of</strong> Nature: Red List <strong>of</strong> Threatened Species. Accessed on 2/24/2012 from <br />

http://www.iucnredlist.org/ <br />

36 USGS Minerals Commodity Summary 2012. Arsenic. http://minerals.usgs.gov/minerals/pubs/commodity/arsenic/mcs-­‐<br />

2012-­‐arsen.pdf <br />

37 The Encyclopedia <strong>of</strong> Earth: Arsenic. Retrieved on 4/6/2012 from <br />

http://www.eoearth.org/article/Arsenictopic=49557#gen1 <br />

April 2013 | ©SCS Global Services <br />

ES-­‐ 17

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