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2018-04-23_REVISION - M2007031 (4)
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2018-04-23_REVISION - M2007031 (4)
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Entry Properties
Last modified
6/15/2021 2:35:25 PM
Creation date
4/23/2018 2:16:13 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M2007031
IBM Index Class Name
Revision
Doc Date
4/23/2018
Doc Name Note
Response to Deficiencies
Doc Name
Response to Deficiencies
From
The Turquoise Connection, Inc.
To
DRMS
Type & Sequence
AM1
Email Name
ERR
Media Type
D
Archive
No
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COLORADO <br /> Department of Public <br /> Health 8 Environment Water Quality Control Division Fact Sheet,Permit No. C00048939 <br /> zero low flow, and a mixing zone is not applicable to this discharge, a mixing zone study is not <br /> warranted at this time. <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, 2002. This guidance document utilizes both quantitative and qualitative <br /> approaches to establish RP depending on the amount of available data. <br /> A qualitative determination of RP may be made where ancillary and/or additional treatment <br /> technologies are employed to reduce the concentrations of certain pollutants. Because it may be <br /> anticipated that the limits for a parameter could not be met without treatment, and the treatment is <br /> not coincidental to the movement of water through the facility, limits may be included to assure that <br /> treatment is maintained. <br /> A qualitative RP determination may also be made where a federal ELG exists for a parameter, and <br /> where the results of a quantitative analysis results in no RP. As the federal ELG is typically less <br /> stringent than a Limitation based on the WQBELs, if the discharge was to contain concentrations at the <br /> ELG (above the WQBEL), the discharge may cause or contribute to an exceedance of a water quality <br /> standard. <br /> For this permit, the division also used information provided in the US EPA Development Document for <br /> Effluent Limitations Guidelines and New Source Performance Standards for the Ore Mining and Dressing <br /> Point Source Category, Gold Placer Mine Subcategory May 1988 (the development document for the <br /> federal ELG), which identifies various metals and other parameters that can be found in placer mining <br /> discharges, as part of the qualitative RP analysis. Metals for which a water quality standard was not <br /> identified for the receiving stream were typically not considered further in the qualitative RP analysis. <br /> The metals considered from the development document are: arsenic, cadmium, chromium, copper, <br /> mercury, nickel, lead, selenium, silver, and zinc. The permittee indicated that no on-site dressing or <br /> processing of gold bearing ores is conducted at the Scott Blue II placer mine, and this condition was <br /> considered the RP analysis provided below. <br /> To conduct a quantitative RP analysis, a minimum of 10 effluent data points from the previous 5 years, <br /> should be used. The equations set out in the guidance for normal and lognormal distribution, where <br /> applicable, are used to calculate the maximum estimated pollutant concentration (MEPC). For data <br /> sets with non-detect values, and where at least 30%of the data set was greater than the detection <br /> level, MDLWIN software is used consistent with Division guidance to generate the mean and standard <br /> deviation, which are then used to establish the multipliers used to calculate the MEPC. If the MDLWIN <br /> program cannot be used the Division's 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 be <br /> available for use in conducting an RP analysis. Thus, consistent with Division procedures, monitoring <br /> will be required to collect samples to support a RP analysis and subsequent decisions for a numeric <br /> limit. A compliance schedule may be added to the permit to require the request of an RP analysis once <br /> the appropriate data have been collected. <br /> For other parameters, effluent data may be available to conduct a quantitative analysis, and therefore <br /> an RP analysis will be conducted to determine if there is RP for the effluent discharge to cause or <br /> contribute to exceedances of ambient water quality standards. The guidance specifies that if the MEPC <br /> exceeds the maximum allowable pollutant concentration (MAPC), limits must be established and where <br /> the MEPC is greater than half the MAPC (but less than the MAPC), monitoring must be established. <br /> Discussions for RP determinations for each parameter are shown in the parameter Evaluation section <br /> below. <br /> Page 6 of 17 <br /> 4300 Cherry Creek Drive S.,Denver,CO 80246-1530 P 303-692-2000 www.colorado.gov/cdphe/wqcd * J H <br /> r'7 <br /> John W.Hickenlooper,Governor Larry Woik,MD,MSPH, Executive Director and Chief Medical Officer CO <br />
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