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Draft Environmental Impact Statement for Roca Honda Mine

Draft Environmental Impact Statement for Roca Honda Mine

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Regulatory Review<br />

Chapter 3. Affected Environment and <strong>Environmental</strong> Consequences<br />

New stationary sources of emissions may be subject to both Federal and State permitting<br />

requirements. These requirements include, but are not limited to, New Source Review, Prevention<br />

of Significant Deterioration, and New Source Per<strong>for</strong>mance Standards <strong>for</strong> selected categories of<br />

industrial sources. The rules <strong>for</strong> NMED’s Air Quality Program Laws and Rules are found in the<br />

New Mexico Administrative Code (NMAC). NMAC Title 20 Chapter 2 Part 7 includes emission<br />

standards and control requirements on both a pollutant specific basis and process/equipment/<br />

industry specific basis. NMAC Title 17 Chapter 2 also set <strong>for</strong>th the permitting requirements <strong>for</strong><br />

stationary emission sources and construction emissions. Given the variety and complexity of the<br />

activities at the RHR site, case-by-case determinations would be necessary to determine if new<br />

stationary sources of air emissions would require permitting.<br />

National Emission Standards <strong>for</strong> Radon Emissions from Underground Uranium <strong>Mine</strong>s, apply to<br />

an underground uranium mine that (a) has mined, will mine, or is designed to mine over 100,000<br />

tons of ore during the life of the mine, or (b) has had or will have an annual ore production rate<br />

greater than 10,000 tons, unless it can be demonstrated...that the mine will not exceed total ore<br />

production of 100,000 tons during the life of the mine (40 CFR 61.20). As discussed in more<br />

detail below, RHR would comply with national standard radon-222 (40 CFR 61.22) as annual<br />

proposed production would be greater than 10,000 tons per year.<br />

To reduce fugitive emissions generated at the mine surface, areas belowground would be<br />

backfilled with waste rock. However, due to the expansion of the waste rock as it is mined, some<br />

waste rock would still be placed at the surface. Water spray would be used to reduce dust<br />

emissions from disturbed areas of the surface where waste rock is placed. In addition, BMPs<br />

would be required and implemented <strong>for</strong> activities associated with the proposed action. The mine<br />

development, operation, and reclamation would be accomplished in full compliance with current<br />

New Mexico regulatory requirements, with compliant practices and/or products. These<br />

requirements include:<br />

• Smoke and visible emissions (NMAC 20-2.61)<br />

• Open burning (NMAC 20-2.60)<br />

• Emissions from gas burning equipment (NMAC 20-2.33)<br />

• Emissions from oil burning equipment (NMAC 20-2.34)<br />

This listing is not all-inclusive; RHR and any contractors would comply with all applicable New<br />

Mexico air pollution control regulations.<br />

3.4.2.2.4 Radon-222 Emissions<br />

The environmental consequences of radon-222 emission to the air from the proposed action are<br />

predominantly related to human health concerns from the radiation dose resulting from breathing<br />

radon-222 and its short-lived decay products. As discussed previously, Federal law limits the<br />

radiation dose from radon-222 emissions from uranium mines to any member of the public at 10<br />

mrem/yr (40 CFR 61.22). The Federal limit of 10 mrem per year is 4.7 percent of the average<br />

effective dose from background sources of radon-222 and its short-lived decay products of 212<br />

mrem per year to the U.S. population (NCRP, 2009).<br />

DEIS <strong>for</strong> <strong>Roca</strong> <strong>Honda</strong> <strong>Mine</strong>, Cibola National Forest 189

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