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Page 1! <br />COLORADO DEPARTMENT OF HEALTH, Water Quality Control Division <br />Rationale -Page 19 Pennlt No. CO-0045675 <br />VI. TERMS AND CONDITIONS OF PERMIT <br />A. Determination of Elf/uent Limitations (Cont.) <br />4 Discussion of Etttuent Limitations (Cont.) <br />c) Pollutants Limited by Water Ouality Standards -For the parameters shown in Table VI-3, the mass <br />balance equation shown in VI-A.2. was used to calculate the allowable eRluent limitations that would not <br />cause the water quality standards to be violated. These IimitaUons are shown as the values for M= in <br />Table Vt-3. The values for Or, Qa and O, fa chronic and acute limitations, taken from section 111.8.2, o/ <br />this rationale, end used in the calculations (or water quality limited parameters are: <br />Flow ~ Chronic (30E3) ~; Acute (iE3) <br />Q, 1.8 cfs 1.3 c(s <br />OOIa = 0.89 cfs OOfa = 0.89 cfs <br />ps OOfb = 0.557 cfs 001b = 0.557 cis <br />001 c = 0.245 cfs 001 c = 0.245 c/s <br />001 a = 2.69 cfs 001 a = 2.19 cfs <br />Q, 0016 = 2.36 cfs 0016 = 1.86 cfs <br />001c =2.045 cfs OOIC =1.545 cfs <br />Values for M, and M, vary depending on the background stream quality data (M,) and the applicable water <br />qualtty standard (M~. The hardness-based TVS metal standards were determined with a mean total <br />hardness value of 64 mg/1 as CaCO,. The M, and M, values are shown in Table VI-3 along with the <br />calculated eHfuent limitations (M~. In addition, Table VI-3 contains the anb'degredadon-based water <br />quality standard and limitation where this is applicable. Table VI-3 shows the calculations for a facility Bow <br />limitation (or outfall 0016 of 250 gpm (or 0.36 MGD, or 0.557 cfs). For the calculations for the other tiered <br />Bow limits o(400 gpm (001a) and 110 gpm (001c), as well as for the determination of baseline loads for <br />this permit, refer to Appendix B. <br />d) Antid radation Review: Because segment 28 does not include a Use Protected classi0cation, an <br />anbdegredation reviewls required for this permit since this is a new discharge. As is discussed in Section <br />31.8 ofthe Basic Standards and Alethodoloaies for SuAace Wafer (SCCR 1002-31), antidegredation <br />reviews are required to be peAormed for new dischargers to a reviewable stream segment that is not use <br />protected. <br />As indicated in 31.8(3)(c) of the Basic Standards. the initial step in an antidegredation review is a <br />determination whether the activity in ques8on is likely to result in significant degradation of reviewable <br />waters, with respect to adopted narrative or numeric standards. The sign~cance determination is based <br />on the chronic numeric standard and Bow for the pollutant of concern except for those pollutants which <br />have only acute numeric standards in which case the acute standard and flow will be used. The activity <br />shall be considered not to result in sign cant degradation, as measured in the reviewable waters <br />segment, rf <br />(i) The Bow rate or volume of a new or increased discharge under review is small enough that it will tie <br />diluted by 100 to 1 or more at low Oow, as defined in section 31.9, by water in the stream; or <br />(ii) The new or increased loading from the source under review is less than 10 peroent of the exisa'ng <br />total load to that segment (or cri0cal constituents (e.g. those (or which there are stream standards set <br />and which are present in the discharge); provided, that the cumulative impact of increased loadings <br />Irom all sources shell not exceed f0 percent of the baseline total load established (or the segment <br />(the baseline total load shall be determined at the time of the Orst proposed new or increased water <br />quality impacts to the reviewable waters.); or <br />(iU) The new or increased loading Irom the source under review will consume, after mixing, less than 15 <br />