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1 Impact Report Pa <br /> Draft Envnronmenta a IV.D-17 p p g <br /> Forward Landfill Expansion <br /> as Proposition 65,both of which require public notification if the incremental risk equals <br /> or exceeds 10 in a million. The SJVAPCD CEQA Guidelines also recommend that the <br /> cancer risk significance threshold be 10 in a million. The incremental risk from exposure <br /> to a given TAC is calculated by multiplying the concentration(or dosage level)of the <br /> given TAC by its specific unit risk factor or potency slope. The unit risk factor or potency <br /> slope of a TAC is derived from epidemiological studies, and the published values are <br /> based on the assumption that a person would be exposed to the given TAC at that dosage <br /> constantly for 70 years or for the life of the project. <br /> Non-Cancer Health Risk <br /> Health risks for each non-carcinogenic TAC are determined using a Hazard Index (HI), <br /> which is the ratio of the predicted exposure concentration to a threshold level that could <br /> cause adverse health effects other than cancer, as established by the Office of <br /> Environmental Health and Hazard Assessment(OEHHA). The ratio (HI) of each non- <br /> carcinogenic substance is added to the calculated Hazard Indices of the other non- <br /> carcinogens to produce an overall HI. I€the overall HI exceeds 1.0,then the impact <br /> would be significant. The HI significance threshold of greater than 1.0 is defined in the <br /> SJVAPCD CEQA Guidelines and is consistent with the value requiring public notification <br /> in the AB 2588 regulation and in Proposition 65. <br /> Cumulative Impacts <br /> According to the SJVAPCD GAMAQI, a cumulative impact occurs when two or more <br /> individual effects, considered together, are considerable or would compound or increase <br /> other environmental impacts. Cumulative impacts can result from individually minor but <br /> collectively significant impacts, meaning that the project's incremental effects are <br /> considerable when viewed in connection with the effects of past, current, and probable <br /> future projects. Notably,any project that would individually have a significant air quality <br /> impact would also be considered to have a significant cumulative air quality impact. <br /> According to the SJVAPCD GAMAQI, cumulative impacts should be assessed for ozone, <br /> PM,(), CO and TAC. <br /> Greenhouse Gases <br /> As discussed previously, at this time there are no adopted Statewide guidelines for GHG <br /> emission impacts,but this is being addressed through the provisions of Senate Bill 97 <br /> ("SB 97"). The project would be considered to have a significant impact if the project <br /> would be in conflict with the AB 32 State goals for reducing GHG emissions;with the <br /> assumption AB 32 will be successful in reducing GHG emissions and reducing the <br /> cumulative GHG emissions statewide by 2020. It is important that the state has taken <br /> these measures,because no project individually could have a major impact (either <br /> positively or negatively)on the global concentration of GHG. <br /> Impacts and Mitigation Measures <br /> This impact section evaluates the activities described in the Project Description that could <br /> potentially result in impacts to air quality, climate change, and human health based on <br /> the conditions of the project area. As described in the Project Description,the proposed <br /> expansion would increase the permitted Class II refuse footprint from 354.5 acres to 551.8 <br /> acres, adding approximately 43,367,810 cubic yards (cy) to the capacity of the landfill. <br /> The additional volume is estimated to accommodate an additional 37.7 million tons of <br /> landfill decomposable waste. This additional waste is estimated to result in a maximum <br />