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III. ENVIRONMENTAL SETTING,IMPACTS AND MITIGATION MEASURES <br /> B. AIR QUALITY <br /> es widely in size. PM-10 and PM-2.5 consist of <br /> Particulate matter in the atmosphere rang y <br /> particulates 10 microns and 2.5 microns,respectively,or less in diameter, which can be inhaled <br /> deep into the lungs and cause adverse health effects. Particulate matter in the atmosphere result <br /> from many kinds of dust-and fume-producing industrial and agricultural operations,combustion, <br /> and atmospheric photochemical reactions. Some of these operations,such as demolition and <br /> construction activities,primarily contribute to increases in local PM-10 concentrations,while <br /> others, such as vehicular traffic, affect regional PM-10 concentrations. Acute and chronic health <br /> effects associated with high particulate levels include the aggravation of chronic respiratory <br /> diseases,heart and lung disease,and coughing,bronchitis and respiratory illnesses in children. <br /> Recent mortality studies have shown a direct association between mortality and daily <br /> concentrations of particulate matter in the air(SJVUPACD, 1998a). Table III.B-2 indicates that <br /> background PM-10 concentrations in Stockton have exceeded state 24-hour-average standards in <br /> each year between 1993 and 1997. Major sources of PM-10 in the SJV include motor vehicles, <br /> power generation,industrial processes, wood burning,roads and construction and farming <br /> activities(SJVUPACD, 1998a). Fugitive windblown dust also represents a significant source of <br /> airborne dust. <br /> Carbon monoxide(CO)is an odorless,colorless gas that can be highly toxic. CO is formed by <br /> the incomplete combustion of fuels and is, unlike ozone,emitted directly into the air. Ambient <br /> CO concentrations normally are considered a local effect and typically correspond closely to the <br /> spatial and temporal distributions of vehicular traffic. CO concentrations are also influenced by <br /> wind speed and atmospheric mixing. Under inversion conditions,carbon monoxide <br /> concentrations may be distributed more uniformly over an area out to some distance from <br /> vehicular sources. CO binds with hemoglobin,the oxygen-carrying protein in blood,and reduces <br /> the blood's capacity for carrying oxygen to the heart,brain,and other parts of the body. At high <br /> concentrations,CO can cause heart difficulties in people with chronic diseases, can impair mental <br /> abilities,and can cause death(SJVUAPCD, 1998x). Exceedances of CO standards are most <br /> likely to occur in winter months, when relative low inversion levels trap pollutants near the <br /> ground and concentrate the CO. Table III.13-2 shows that background CO concentrations in the <br /> vicinity of the Hazelton Street monitoring station do not approach the state standards even during <br /> stagnant wintertime conditions. However, CO concentrations in the vicinity of congested <br /> intersections and freeway segments would be expected to be higher than the monitoring data in <br /> Table III.B-2. The primary source of CO in the San Joaquin Valley is on-road motor vehicles, <br /> which account for approximately 71 percent of total CO emissions. Other sources include other <br /> mobile sources and waste burning (SJVUAPCD, 1998x). <br /> Stationary Source Controls <br /> SJVUAPCD is the regional agency responsible for regulating stationary sources of air pollutants. <br /> SJVUAPCD regulates stationary sources through its permit program. The SJVUAPCD has not <br /> issued any permits to operate for the existing transfer station operations. Stationary equipment <br /> associated with the project site that would require a permit includes the tub grinder to be used for <br /> greenwaste processing. <br /> Stockton Scavenger Transfer Station Expansion III.B.6 ESA/990190 <br />