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Selecting Numerical Limits <br /> 7 - 20 August 2002 <br /> ❖ Tastes and Odors Objective <br /> ➢ Taste- and odor-based limits, normally in the following hierarchy <br /> ■ California Secondary MCL <br /> ■ Federal Secondary MCL <br /> • USEPA National Ambient Water Quality.Criterion based on taste & odor <br /> • Taste & odor thresholds published by other agencies or from the peer reviewed <br /> literature <br /> First, select one limit for each of the items above that begins with an arrow(➢). Record your selections <br /> in a chart, such as the following: <br /> Water Quality Relevant Portion of <br /> Ob'ective/Criterion Objective/Criterion Source <br /> California Toxics Rule/ Human Health Protection CTR or NTR Concentration Units <br /> National Toxics Rule Aquatic Life Protection—CCC CTR or NTR <br /> Aquatic Life Protection —CMC CTR or NTR <br /> Chemical Constituents Drinking Water MCL (lowest) DHS <br /> Numerical Water Quality Objective Basin Plan <br /> Beneficial Use Impairment Limit <br /> Toxicity Human Health—Drinking Water <br /> Human Health—Fish Consumption USEPA, RAWQC <br /> Aquatic Life Protection —CCC <br /> Aquatic Life Protection—CMC <br /> Tastes & Odors Taste & Odor Based Limits <br /> Second, select the limit with the lowest concentration.16 The result should be a limit that satisfies all <br /> applicable water quality objectives. Where aquatic life criteria vary with hardness, pH, or other factors, <br /> aquatic life criteria may be the most restrictive under some conditions while other limits in the above <br /> table may be more restrictive under other conditions. Consideration of natural background levels and <br /> antidegradation may require further modifications to this selection, as discussed below. <br /> Limitations <br /> The above algorithms should be applied carefully, considering the factors of each specific case. <br /> Automatically selecting numerical limits according to these algorithms will not always generate the most <br /> appropriate limit. If specific beneficial uses do not apply, then limits protective of those uses should be <br /> eliminated from consideration. It may be appropriate to deviate from the hierarchies listed above in <br /> specific cases. We may have information that a particular limit is outdated or is in formal dispute at the <br /> agency that originally issued the limit (as was the case with the former PHG for chromium at OEHHA). <br /> In another example, a California health-based limit may be less stringent than a comparable USEPA <br /> limit. Normally, we would prefer using the California limit over the one from USEPA. However, if the <br /> California and EPA limits are based on the same source of toxicologic information and the California <br /> limit is higher simply because it was "rounded off' from the EPA limit, it would be logical to use the <br /> more precise USEPA limit. It may also be that a risk-management decision prevented the California <br /> 16 In the case of aquatic life criteria,both CCC and CMC limits apply,1 as noted above. <br /> � <br />