Laserfiche WebLink
5.9 PUBLIC HEALTH <br /> To evaluate potential health risks,the measures of these risks are first described in terms of <br /> the types of public health effects and the significance criteria and thresholds for those effects. <br /> 5.9.4.1 Significance Criteria <br /> Significance criteria exist for both carcinogenic and non-carcinogenic risks, and are <br /> discussed separately. <br /> 5.9.4.1.1 Cancer Risk <br /> Cancer risk is the probability or chance of contracting cancer over a human life span <br /> (assumed to be 70 years). Carcinogens are assumed to have no threshold below which there <br /> would be no human health impact. In other words, any exposure to a carcinogen is assumed <br /> to have some probability of causing cancer;the lower the exposure,the lower the cancer risk <br /> (i.e.,a linear,no-threshold model). Under state and SJVAPCD regulations,an incremental <br /> cancer risk greater than 10-in-one million due to a project is considered to be a significant <br /> impact on public health if the emitting units are determined by the District to be using <br /> Toxics Best Available Control Technology (T-BACT).13 The 10-in-one-million risk level is <br /> also used by the Air Toxics"Hot Spots" (AB 2588)program and California's Proposition 65 <br /> as the public notification level for air toxic emissions from existing sources. <br /> 5.9.4.1.2 Non-Cancer Health Impact <br /> Non-cancer health effects can be either long-term(chronic) or short-term (acute). In <br /> determining potential non-cancer health risks from air toxics, it is assumed there is a dose of <br /> the TAC below which there would be no impact on human health. The air concentration <br /> corresponding to this dose is called the Reference Exposure Level (REL). A non-cancer <br /> health impact is measured in terms of a health hazard quotient for each TAC,which is the <br /> calculated maximum exposure (concentration) of each TAC divided by its REL. Health <br /> hazard quotients for TACs affecting the same target organ are typically summed with the <br /> resulting totals expressed as health hazard indices for each organ system. A health hazard <br /> index of less than 1.0 is considered to be a less-than-significant health risk. <br /> Chronic toxicity is defined as adverse health effects from prolonged chemical exposure, <br /> caused by chemicals accumulating in the body. Because chemical accumulation to toxic <br /> levels typically occurs slowly, symptoms of chronic effects usually do not appear until long <br /> after exposure commences. The lowest no-effect chronic exposure level for a non- <br /> carcinogenic air toxic is the chronic REL. Below this threshold,the body is capable of <br /> eliminating or detoxifying the chemical rapidly enough to prevent its accumulation. The <br /> chronic health hazard index was calculated as the sum of the chronic health hazard <br /> quotients,each of which is calculated as the chronic TAC annual concentration divided by <br /> the chronic REL of the TAC. <br /> Acute toxicity is defined as adverse health effects caused by a brief chemical exposure of no <br /> more than 24 hours. For most chemicals,the air concentration required to produce acute <br /> effects is higher than the level required to produce chronic effects because the duration of <br /> exposure is shorter. Because acute toxicity is predominantly manifested in the upper <br /> respiratory system at threshold exposures, all acute health hazard quotients are typically <br /> summed to calculate the acute health hazard index. The maximum one-hour average <br /> 13 The threshold would be 1 in one million if the emitting units were determined not to be applying T-BACT. <br /> 5.9-10 SAC/371322/082340007(LEC_5.9_PUBLIC_HEALTH.DOC) <br />