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2014-069 - Final Environmental Impact Report No. 2014-01
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2014-069 - Final Environmental Impact Report No. 2014-01
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11/18/2014 10:54:14 AM
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11/18/2014 10:38:50 AM
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City Clerk
Doc Type
Resolution
Doc #
2014-069
Date
10/21/2014
Destruction Year
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HARBOR BLVD. MIXED USE TRANSIT CORRIDOR PLAN FINAL FIR <br />CITY OF SANTA ANA <br />5. Environmental Analysis <br />AIR QUALITY <br />By the last update to the TAC list in December 1999, CARB has designated 244 compounds as TACs (CARB <br />1999). Additionally, CARB has implemented control measures for a number of compounds that pose high <br />risks and show potential for effective control. The majority of the estimated health risks from TACs can be <br />attributed to relatively few compounds, the most important being DPM. <br />In 1998, CARB identified diesel particulate matter as a TAC. Previously, the individual chemical compounds <br />in diesel exhaust were considered TACs. Almost all diesel exhaust particle mass is 10 microns or less in <br />diameter. Because of their extremely small size, these particles can be inhaled and eventually trapped in the <br />bronchial and alveolar regions of the lung. <br />Multiple Air Toxics Exposure Study (MATES) III <br />In 2000, SCAQMD conducted a study on ambient concentrations of TACs and estimated the potential health <br />risks from au toxics. The results showed that the overall risk for excess cancer from a lifetime exposure to <br />ambient levels of au toxics was about 1,400 in a million. The largest contributor to this risk was diesel <br />exhaust, accounting for 71 percent of the au toxics risk. In 2008, SCAQMD conducted its third update to its <br />study on ambient concentrations of TACs and estimated the potential health risks from au toxics. The results <br />showed that the overall risk for excess cancer from a lifetime exposure to ambient levels of au toxics was <br />about 1,200 in one million. The largest contributor to this risk was diesel exhaust, accounting for <br />approximately 84 percent of the au toxics risk (SCAQMD 2008a). Excess cancer risk is 742 to 1,035 in a <br />million in the vicinity of the Harbor Boulevard Mixed Use Transit Corridor Plan area (SCAQMD 2008a). <br />Regulatory Setting <br />AAQS have been promulgated at the local, state, and federal levels for criteria pollutants. The project site is in <br />the SoCAB and is subject to the rules and regulations imposed by SCAQMD as well as the California AAQS <br />adopted by CARB and federal AAQS. <br />Ambient Air Quality Standards <br />The Clean An Act (CAA) was passed in 1963 by the US Congress and has been amended several times. The <br />1970 Clean Air Act amendments strengthened previous legislation and laid the foundation for the regulatory <br />scheme of the 1970s and 1980s. In 1977, Congress again added several provisions, including nonattainment <br />requirements for areas not meeting National AAQS and the Prevention of Significant Deterioration program. <br />The 1990 amendments represent the latest in a series of federal efforts to regulate the protection of au <br />quality in the United States. The CAA allows states to adopt more stringent standards or to include other <br />pollution species. The California Clean Air Act (CCAA), signed into law in 1988, requires all areas of the state <br />to achieve and maintain the California AAQS by the earliest practical date. The California AAQS tend to be <br />more restrictive than the National AAQS, based on even greater health and welfare concerns. <br />These National AAQS and California AAQS are the levels of air quality considered to provide a margin of <br />safety in the protection of the public health and welfare. They are designed to protect "sensitive receptors" <br />most susceptible to further respiratory distress, such as asthmatics, the elderly, very young children, people <br />already weakened by other disease or illness, and persons engaged in strenuous work or exercise. Healthy <br />Page 5.26 PlaceWorkr <br />
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