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materials (sand and gravel) over a 26- to 60 year period. The operation would be open pit, sand <br /> and gravel harvesting and processing. The impacts of operational air quality emissions of <br /> criteria pollutants are potentially significant. (Final EIR,p. 4-34.) <br /> Significance Before Mitigation: Potentially Significant <br /> Facts: Project operations would result in emission of criteria pollutants. See Final EIR,pp. 4-34 <br /> to 4-39. <br /> Mitigation Measures: <br /> Mitigation Measure 4.6.2: While several emission-reducing measures are currently available, <br /> current proven technology limits the maximum reductions. These operational impacts are a <br /> significant impact of the project after mitigation. The project proposes to operate new equipment, <br /> both on-site non road equipment and haul trucks. This provides the best available operating <br /> efficiency for the equipment. Currently, additional retrofits to reduce NOx emissions below <br /> acceptable emission standards would be cost prohibitive. Catalytic particulate filters and the use <br /> of ultra low sulfur fuels do not substantially reduce NOx emissions. (Final EIR,p. 4-39.) <br /> Findings: <br /> The impacts of operational air quality emissions of criteria pollutants would be reduced by <br /> implementation of Mitigation Measure 4.6.2, but not to a less-than-significant level. The <br /> applicant would use the latest equipment upon commencing mining, which would thereby <br /> implement BACT. ROG emissions would be just above the significance level in 2008 for annual <br /> production levels of 4 million tons. NOx emission would be 4 to 14 times above the significance <br /> criterion under the various scenarios analyzed in Tables 4.6-5A, B and C. Mitigation measures <br /> to reduce NOx impacts to less than significant are not technically feasible; thus, after mitigation <br /> this would remain a significant impact. <br /> Other technologies exist to control NOx emissions from engines, such as the use of the feel <br /> additive PuriNOx, and/or the use of urea injection system in combination with a reducing <br /> catalyst. However, these technologies have not been widely tested in the types of engines for the <br /> project. Also, they have been known to affect engine operation efficiencies and may create <br /> secondary environmental impacts. Current control technologies associated with the concrete, <br /> asphalt, and sand dryer equipment generally apply to f tgitive dust emissions and not NOx. There <br /> are no current control technologies that when applied together would reduce the total NOx <br /> emissions from the project to less than significant(that is, a 90 percent reduction). <br /> As a result, this impact is considered significant and unavoidable for the project. Based on the <br /> whole record, this Commission finds that there are no additional feasible mitigation measures <br /> that would reduce potential impacts associated with operational air quality emissions of criteria <br /> pollutants to a less than significant level. (Final FIR,p. 4-39.) <br /> 35 <br />