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In addition to PSD AQRV analyses, visibility impacts are also included under a State Implementation Plan <br /> for the reduction of Regional Haze. This regulation is used to reduce the visibility impacts from existing <br /> facilities and introduce additional emissions controls to a standard known as Best Available Retrofit <br /> Technology. <br /> Deposition is the process by which pollutants are removed from the atmosphere via mechanical and <br /> chemical processes. When air pollutants such as sulfur and nitrogen are deposited into ecosystems,they <br /> may cause acidification, or enrichment of soils and surface waters. Atmospheric nitrogen and sulfur <br /> deposition may affect water chemistry, resulting in impacts to aquatic vegetation, invertebrate <br /> communities, amphibians, and fish. Deposition can also cause chemical changes in soils that alter soil <br /> microorganisms, plants, and trees. Although nitrogen is an essential plant nutrient, excess nitrogen from <br /> atmospheric deposition can stress ecosystems by favoring some plant species and inhibiting the growth <br /> of others. <br /> Visibility impairment or haze is caused when sunlight encounters tiny pollution particles in the <br /> atmosphere and is either absorbed or scattered which reduces the clarity and color of what can be seen. <br /> The ability of a pollutant to cause various degrees of visibility impacts is primarily a function of its physical <br /> size, and chemical composition and properties. Visibility can be expressed in terms of deciview (dv) or <br /> standard visual range(km).A change of one dv is approximately a 10 percent change in the light extinction <br /> coefficient(i.e., light that is scattered or absorbed and does not reach the observer), which is a small, but <br /> usually perceptible scenic change. <br /> 2.2.1.3 Regional Air Quality <br /> The Project Area and vicinity is currently in Attainment or unclassified for all criteria pollutants. Monitoring <br /> of criteria pollutants in the region is located near population centers or areas of specific interest. In the <br /> late 1990s, the EPA allowed monitoring to cease where pollutants were less than 60 percent of the <br /> NAAQS,and as a result the data collected for this analysis is regionally representative but often monitored <br /> at some distance from the Project Area. <br /> Table 2.2-3 shows recent ambient air quality monitor data for potential pollutants of concern from <br /> monitors located in or nearby the affected area. The primary pollutant of concern from the Proposed <br /> Action is particulate matter (as determined from the emissions inventory presented below). The area <br /> monitors also show that 03 levels are relatively close to the new standard promulgated by EPA in 2015. <br /> The 03 NAAQS is the 4t" high averaged over 3 years.There are no 3-year periods that exceed the 70 ppb. <br /> A couple of individual years from 2012 to 2017 resulted in a 4t" high greater than 70 ppb, but the highest <br /> 3-year average is the La Plata site from 2015 to 2017,which is approximately 99.0 percent of the standard. <br /> Therefore,the region remains in attainment for 03.All the monitoring data is from the USEPA's AQS Data <br /> Mart (https://www.epa.gov/outdoor-air-quality-data) and excludes exceptional events. The database <br /> contains ambient air pollution data collected by USEPA, state, local, and tribal air pollution control <br /> agencies,and from various federal land managers from thousands of monitors. Monitoring data is limited, <br /> and all pollutants are not monitored at all monitoring locations, and thus data for a pollutant may not be <br /> available for all portions of the affected environment. For example, monitoring data for Pueblo County, <br /> CO is limited to PM10 and PM2.5.The location of air quality monitoring stations within the Project analysis <br /> Dunn Ranch Area LBA and Mining Plan Modification 8 <br /> Technical Resources Report <br />