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2018-04-23_REVISION - M2007031 (4)
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2018-04-23_REVISION - M2007031 (4)
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Last modified
6/15/2021 2:35:25 PM
Creation date
4/23/2018 2:16:13 PM
Metadata
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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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t COLORADO <br /> Department of Public <br /> Health b Environment Water Quality Control Division Fact Sheet,Permit No. C00048939 <br /> Stormwater discharges were not contemplated during development of the Protection of Irrigated Crops <br /> policy; therefore, EC and SAR monitoring is not applicable to stormwater-only discharges. <br /> b. Whole Effluent Toxicity- The Water Quality Control Division has established the use of WET testing as a <br /> method for identifying and controlling toxic discharges from wastewater treatment facilities. WET <br /> testing is being utilized as a means to ensure that there are no discharges of pollutants"in amounts, <br /> concentrations or combinations which are harmful to the beneficial uses or toxic to humans, animals, <br /> plants, or aquatic life" as required by Section 31.11 (1)of the Basic Standards and Methodologies for <br /> Surface Waters. The requirements for WET testing are being implemented in accordance with Division <br /> policy, implementation of the Narrative Standard for Toxicity in Discharge Permits Using Whole Effluent <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 the receiving water is reviewable, an antidegradation review is required <br /> pursuant to Section 31.8 of The Basic Standards and Methodologies for Surface Water. As set forth in <br /> Section VII of the WQA, an antidegradation evaluation was conducted for pollutants when water quality <br /> impacts occurred and when the impacts were significant. Based on the antidegradation requirements <br /> and the reasonable potential analysis discussed below, antidegradation-based average concentrations <br /> (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. <br /> b. Antibackslidinq -As the receiving water is designated Reviewable, and the Division has performed an <br /> antidegradation evaluation, in accordance with the Antidegradation Guidance, the antibacksliding <br /> requirements in Regulation 61.10 have been met. <br /> c. Determination of Total Maximum Daily Loads (TMDLs)- The receiving stream to which the Scott Blue II <br /> mine discharges is currently listed on the State's 303(d) list for development of TMDLs for aquatic life <br /> (provisional). However, a TMDL has not yet been established. The permit may be reopened to include <br /> limitations based upon a finalized TMDL. <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 receiving water is a <br /> Page 5 of 17 <br /> 4300 Cherry Creek Drive S.,Denver,CO 80246-1530 P 303-692-2000 www.colorado.gov/cdphe/wgcd * r,7 <br /> John W.Hickenlooper,Governor Larry Wolk,MD,MSPH,Executive Director and Chief Medical Of i CO <br /> . :pp:et peutreas <br />
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