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COLORADO DEPARTMENT OF PUBLIC HEALTH AND ENVIRONMENT, Water Quality Control Division <br />Rationale — Page 10, Permit No. C00036251 <br />To conduct a quantitative RP analysis, a minimum of 10 effluent data points from the previous 5 <br />years, should be used. The equations set out in the guidance for normal and lognormal <br />distribution, where applicable, are used to calculate the maximum estimated pollutant <br />concentration (MEPC). For data sets with non - detect values, and where at least 30% of the data <br />set was greater than the detection level, MDLWIN software is used consistent with Division <br />guidance to generate the mean and standard deviation, which are then used to establish the <br />multipliers used to calculate the MEPC. If the MDLWIN program cannot be used the Division's <br />guidance prescribes the use of best professional judgment. <br />For some parameters, recent effluent data or an appropriate number of data points may not be <br />available, or collected data may be in the wrong form (dissolved vs. total) and therefore may not <br />be available for use in conducting a RP analysis. Thus, consistent with Division procedures, <br />monitoring will be required to collect samples to support a RP analysis and subsequent decisions <br />for a numeric limit. A compliance schedule may be added to the permit for the request of a RP <br />analysis once the appropriate data have been collected. <br />For other parameters, effluent data may be available to conduct a quantitative analysis, and <br />therefore a RP analysis will be conducted to determine if there is RP for the effluent discharge to <br />cause or contribute to exceedances of ambient water quality standards. The guidance specifies <br />that if the MEPC exceeds the maximum allowable pollutant concentration (MAPC), limits must <br />be established and where the MEPC is greater than half the MAPC (but less than the MAPC), <br />monitoring must be established. Tables VI -2A and VI -2B contains the calculated MEPC <br />compared to the corresponding MAPC, and the results of the reasonable potential evaluation, for <br />those parameters that met the data requirements for Outfall OO1A and 002A, respectively. The <br />RP determination is discussed for each parameter in the text below. <br />Table VI -2A — Reasonable Potential Analysis for Outfall 001A <br />Zn, TR (µg/1) <br />Radium 226 +228 (pCi /1) <br />MEPC <br />26 <br />30 -Day Average <br />WQBEL <br />(MAPC) <br />2000 <br />4.2 s 5 <br />Reasonable <br />Potential <br />No (Qual) <br />Yes (Qual) <br />7 -Day Ave or Daily Max <br />MEPC <br />26 <br />6.5 <br />Table VI -2B — Reasonable Potential Analysis for Outfall 002A <br />WQBEL <br />(MAPC) <br />Reasonable <br />Potential <br />NA <br />Parameter <br />Zn, TR (pg/ <br />Radium 226 +228 (pCi /1) <br />MEPC <br />30 -Day Average <br />WQBEL <br />(MAPC) <br />Reasonable <br />Potential <br />0.018 2000 <br />NA 5 <br />No <br />0.018 <br />Yes (Quaff) 26 <br />7 -Day Ave or Daily Max <br />MEPC <br />WQBEL <br />(MAPC) <br />Reasonable <br />Potential <br />NA NA <br />NA ; NA <br />3. Pollutants Limited by Water Quality Standards <br />— This parameter is limited by the water quality standards of 6.5 -9.0 s.u., as this range is <br />more stringent than the range specified under the Regulations for Effluent Limitations and the <br />federal ELGs. This limitation is the same as that contained in the previous permit . and is imposed <br />effective immediately, for Outfalls OO1A, OO1B, 002A, 002B and 002C. <br />