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Environmental Life Cycle Assessment of Southern Yellow Pine ...

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EXECUTIVE SUMMARY<br />

Indicator results in Table 1 show that a significant volume <strong>of</strong> untreated hazardous waste is generated <br />

in the BAU scenario – over 590,000 tons over the 40-­‐year time horizon. The difference between the <br />

BAU and SPR scenarios is enough hazardous waste to completely fill nearly 300 Olympic-­‐size <br />

swimming pools. <br />

1.6 Discussion <strong>of</strong> the <strong>Environmental</strong> Advantages <strong>of</strong> the BAU Scenario <br />

1.6.1 Lower Land Use Ecological Impacts in the Mesabi and Marquette Iron Ranges <br />

As shown in Table 1, the BAU and SPR scenarios impact different regions with different biomes and <br />

species affected. The BAU scenario does not impact three terrestrial species and one biome in the <br />

Mesabi and Marquette Iron Ranges. These lowered impacts include disturbance to Western Great <br />

Lakes forests, and the habitat <strong>of</strong> the Kirtland’s warbler, Wood turtle, and Blanding’s turtle.. <br />

1.6.2 Lower Emissions Affecting Regional Acidification <br />

The BAU scenario category indicator results are lower for Regional Acidification. The emissions in the <br />

SPR scenario classified in this impact category are dominated by those resulting from steel <br />

production, hot-­‐dipped galvanization, and zinc smelting; most <strong>of</strong> these emissions are occurring in the <br />

Midwestern United States and Great Lakes region. These regions have sensitive soils, and a large <br />

fraction <strong>of</strong> acidifying emissions from steel production in this region deposit in sensitive areas, and can <br />

lead to acidification. In the BAU scenario, most emissions result from the electricity generation used <br />

in the production <strong>of</strong> the CCA treatment chemical. Though also occurring in relatively sensitive <br />

regions, the level <strong>of</strong> acidifying emissions in the BAU scenario is less, leading to a smaller indicator <br />

result. <br />

1.6.3. Lower Emissions Leading to Ground Level Ozone and PM 2.5 Exposure Risks <br />

The BAU scenario results in fewer risks <strong>of</strong> the exposure to humans from both ground level ozone and <br />

fine particulate matter (PM2.5). In the SPR scenario, the production <strong>of</strong> steel is the largest contributor <br />

to results for both <strong>of</strong> the impact categories <strong>of</strong> Ground Level Ozone Exposure Risks and PM 2.5 <br />

Exposure Risks. In the SPR scenario, the unit processes associated with steel production are <br />

concentrated in the United States Midwest and Great Lakes regions, both <strong>of</strong> which have relatively <br />

high population densities. This results in larger exposure risks from the emissions classified in these <br />

impact categories. In the BAU scenario, most emissions result from the production <strong>of</strong> the precursors <br />

going into CCA production, and the installation <strong>of</strong> wood utility poles. Though also occurring in <br />

relatively densely populated regions, the level <strong>of</strong> emissions in the BAU scenario is less, leading to a <br />

smaller indicator result. <br />

1.6.4. Zinc Resource Depletion <br />

The depletion <strong>of</strong> zinc resources is a clear advantage <strong>of</strong> the BAU scenario. For galvanized steel utility <br />

poles, zinc provides a sacrificial coating and very little zinc is recovered at end-­‐<strong>of</strong>-­‐life. <br />

April 2013 | ©SCS Global Services <br />

ES-­‐ 21

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