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Page 10 <br />In 2024, trees in City of Pleasanton emitted an estimated 12.59 tons of volatile organic compounds (VOCs) (7.016 <br />tons of isoprene and 5.57 tons of monoterpenes). Emissions vary among species based on species characteristics (e.g. <br />some genera such as oaks are high isoprene emitters) and amount of leaf biomass. Fifty- one percent of the urban <br />forest's VOC emissions were from Coastal live oak and California white oak. These VOCs are precursor chemicals to <br />ozone formation.³ <br />General recommendations for improving air quality with trees are given in Appendix VIII. <br />³ Some economic studies have estimated VOC emission costs. These costs are not included here as there is a tendency to add positive dollar estimates of ozone <br />removal effects with negative dollar values of VOC emission effects to determine whether tree effects are positive or negative in relation to ozone. This <br />combining of dollar values to determine tree effects should not be done, rather estimates of VOC effects on ozone formation (e.g., via photochemical models) <br />should be conducted and directly contrasted with ozone removal by trees (i.e., ozone effects should be directly compared, not dollar estimates). In addition, air <br />temperature reductions by trees have been shown to significantly reduce ozone concentrations (Cardelino and Chameides 1990; Nowak et al 2000), but are not <br />considered in this analysis. Photochemical modeling that integrates tree effects on air temperature, pollution removal, VOC emissions, and emissions from <br />power plants can be used to determine the overall effect of trees on ozone concentrations.