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11MITIM" <br />COLORADO DEPARTMENT OF PUBLIC HEALTH AND ENVIRONMENT, Water Quality Control Division <br />Fact Sheet- Page 15, Permit No. C00000906 <br />Toxicity (Sept 30, 2010). Note that this policy has recently been updated and the permittee should <br />refer to this document for additional information regarding WET. <br />4. Water Quality Regulations, Policies, and Guidance Documents <br />a. Antidegradation - Since Middle Fork Purgatoire River is Reviewable, an antidegradation evaluation is <br />required for this segment pursuant to Section 31.8 of The Basic Standards and Methodologies for <br />Surface Water. As set forth in the WQA, an antidegradation evaluation was conducted for Middle Fork <br />Purgatoire River for pollutants when water quality impacts occurred and when the impacts were <br />significant. Based on the antidegradation requirements and the reasonable potential analysis discussed <br />below, antidegradation-based average concentrations (ADBACs) may be applied. <br />According to Division procedures, the facility has three options related to antidegradation-based <br />effluent limits: (1) the facility may accept ADBACs as permit limits (see Section VII of the WQA); (2) the <br />facility may select permit limits based on their non -impact limit (NIL), which would result in the <br />facility not being subject to an antidegradation review and thus the antidegradation-based average <br />concentrations would not apply (the NILs are also contained in Section VII of the WQA); or (3) the <br />facility may complete an alternatives analysis as set forth in Section 31.8(3)(d) of the regulations which <br />would result in alternative antidegradation-based effluent limitations. <br />The effluent must not cause or contribute to an exceedance of a water quality standard and therefore <br />the WQBEL must be selected if it is lower than the NIL. Where the WQBEL is not the most restrictive, <br />the discharger may choose between the NIL or the ADBAC: the NIL results in no increased water quality <br />impact; the ADBAC results in an "insignificant" increase in water quality impact. The ADBAC limits are <br />imposed as two-year average limits. Because this facility is considered a new discharger as of <br />September 20, 2000, NILS were not calculated. <br />b. Antibacksliding - As one of the receiving waters is designated Reviewable, and the Division has <br />performed an antidegradation evaluation, in accordance with the Antidegradation Guidance, the <br />antibacksliding requirements in Regulation 61.10 have been met. <br />c. Determination of Total Maximum Daily Loads (TMDLs) - The stream segments are not on the State's <br />303(d) list, and therefore TMDLs do not apply. <br />d. Colorado Mixing Zone Regulations - Pursuant to section 31.10 of The Basic Standards and Methodologies <br />for Surface Water, a mixing zone determination is required for this permitting action. The Colorado <br />Mixing Zone Implementation Guidance, dated April 2002, identifies the process for determining the <br />meaningful limit on the area impacted by a discharge to surface water where standards may be <br />exceeded (i.e., regulatory mixing zone). This guidance document provides for certain exclusions from <br />further analysis under the regulation, based on site-specific conditions. <br />The guidance document provides a mandatory, stepwise decision-making process for determining if the <br />permit limits will not be affected by this regulation. Exclusion, based on Extreme Mixing Ratios, may <br />be granted if the ratio of the facility design flow to the chronic low flow (30E3) is greater than 2:1 or if <br />the ratio of the chronic low flow to the design flow is greater than 20:1. Since the ratio of the design <br />flow to chronic low flow at outfall 001 is 1.7:1, the permittee must perform additional studies to <br />determine if further requirements apply. The remaining threshold tests require site-specific <br />information that is currently not available and thus a determination cannot be made about how the <br />regulation may affect the setting of effluent limits in this permit. Therefore, a special study is <br />necessary for acquisition of this information, which will be used to complete the testing of exclusion <br />thresholds before the next permit renewal. <br />e. Reasonable Potential Analysis - Using the assimilative capacities contained in the WQA, an analysis <br />must be performed to determine whether to include the calculated assimilative capacities as WQBELs <br />in the permit. This reasonable potential (RP) analysis is based on the Determination of the <br />Requirement to Include Water Quality Standards -Based Limits in CDPS Permits Based on Reasonable <br />Potential, dated December, 2013. This guidance document utilizes both quantitative and qualitative <br />approaches to establish RP depending on the amount of available data. <br />