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4.1 – Air Quality <br />Draft Environmental Impact Report February 2021 <br />14800 W. Schulte Road Logistics Center 4.1-3 <br />Precipitation, Humidity, and Fog <br />Precipitation and fog can result in the reduction or increase in some pollutant concentrations. For instance, O3 <br />needs sunlight for its formation, and clouds and fog can block the required solar radiation. In addition, wet fogs can <br />cleanse the air during winter as moisture collects on particles and deposits them on the ground. Fog with less <br />moisture content, however, can contribute to the formation of secondary ammonium nitrate particulate matter. <br />The winds and unstable air conditions experienced during the passage of winter storms result in periods of low <br />pollutant concentrations. Between winter storms, high pressure and light winds allow cold, moist air to pool on the <br />San Joaquin Valley floor, resulting in strong low-level temperature inversions and very stable air conditions, which <br />can lead to Tule fog. Wintertime conditions favorable to fog formation are also conditions favorable to high <br />concentrations of particulate matter. <br />Urban Heat Island Effect <br />The “urban heat island” refers to the effect of urbanized areas on surface and air temperature compared to their <br />rural surroundings. Buildings, roads, and other “hardscape” create an island of higher temperatures within the <br />regional landscape. As described by the U.S. Environmental Protection Agency (EPA), “[u]rban heat islands are <br />caused by development and the changes in radiative and thermal properties of urban infrastructure as well as the <br />impacts buildings can have on the local microclimate—for example tall buildings can slow the rate at which cities <br />cool off at night. Heat islands are influenced by a city’s geographic location and by local weather patterns, and their <br />intensity changes on a daily and seasonal basis” (EPA 2008). The term is generally used to refer to community -wide <br />effects, particularly for large metropolitan cities. The potential adverse effects of the urban heat island effect include <br />increased energy consumption, elevated emissions of air pollutants and greenhouse gases (GHGs), compromised <br />human health and comfort, and impaired water quality. Increased temperatures due to the urban heat island effect <br />may also lead to increased energy consumption, which has implications for air quality and GHG emissions. In <br />addition to energy-related increases in air emissions, elevated air temperatures increase the rate of ground -level <br />O3 formation. Communities have adopted various strategies to deal with these environmental impacts, such as <br />increasing vegetation and using more energy-efficient building materials. These strategies are often part of more <br />general energy savings or “sustainability” practices and are not identified as “urban heat island effect” mitigation, <br />but nevertheless they provide the benefits of reducing surface and atmospheric heat islands. <br />Pollutants and Effects <br />Criteria Air Pollutants <br />Criteria air pollutants are defined as pollutants for which the federal and state governments have esta blished <br />ambient air quality standards, or criteria, for outdoor concentrations to protect public health. The federal and state <br />standards have been set, with an adequate margin of safety, at levels above which concentrations could be harmful <br />to human health and welfare. These standards are designed to protect the most sensitive persons from illness or <br />discomfort. Pollutants of concern include O3, NO2, carbon monoxide (CO), sulfur dioxide (SO2), particulate matter <br />with an aerodynamic diameter less than or equal to 10 microns (PM10), particulate matter with an aerodynamic <br />diameter less than or equal to 2.5 microns (PM2.5), and lead. ROGs (also referred to as volatile organic compounds <br />[VOCs])1 and NOx are also important because they are precursors to O3. These pollutants, as well as toxic air <br /> <br />1 The SJVAPCD threshold is set for ROG. However, ROG and VOC are generally considered equivalent for CEQA analyses; as such, <br />ROG and VOC are used interchangeably in this analysis.