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2022-09-29_PERMIT FILE - C1980007 (2)
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2022-09-29_PERMIT FILE - C1980007 (2)
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Last modified
10/6/2022 2:39:13 PM
Creation date
10/6/2022 2:29:35 PM
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Template:
DRMS Permit Index
Permit No
C1980007
IBM Index Class Name
Permit File
Doc Date
9/29/2022
Doc Name
pg 2.05-200 to 2.05-300
Section_Exhibit Name
2.05.6 Mitigation of Surface Coal Mining Operation Impacts Part 2
Media Type
D
Archive
No
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West E!k Mine <br />term increase would have no effect on the crops. The 500 mg/L level at which there may be <br />limited restrictions for irrigation is applicable to the average concentration of the source <br />irrigation water. The instantaneous concentration of the source water can exceed 500 mg/L <br />without adverse impact to irrigated crops. The more relevant analysis is to consider the annual <br />salinity loading to the North Fork, which is presented in the CHIA, and remains valid. <br />To protect agricultural and municipal uses in the lower Colorado River Basin, Colorado <br />participates in the multi-state, basin-wide approach for managing salinity (TDS) in the Colorado <br />River. There are no Colorado stream standazds for TDS based on stream classifications. TDS is <br />controlled to maintain the following flow-weighted annual values for TDS: Below Hoover Dam: <br />723 mg/L; below Pazker Dam: 747 mg/L; at Imperial Dam: 879 mg/L. The Colorado regulation <br />recognized that periodic increases above the criteria aze in conformance with the standazds, <br />provided that, when conditions return to normal, concentrations are expected to be at or below <br />the criteria level. <br />The normal range for TDS in irrigation water is between 0 to 2,000 mg/L. Continued and <br />prolonged irrigation with water having a TDS concentration between 500 mg/L and 2,000 mg/L <br />may impose slight to moderate requirements for management practices (leaching and drainage) <br />or crop selection (use of less sensitive crops) in order to avoid crop yield reductions. Because <br />crops aze affected only when TDS in root-zone water builds up to excessive levels, occasional <br />excursions of TDS in irrigation water above 500 mg/L aze generally not significant, as long as <br />the average annual value is lower. <br />Dr. Robert Weiner of WWE has evaluated the concentrations of the individual constituents <br />which collectively constitute TDS in mine dischazges. Dr. Weiner has determined that the pond <br />discharge water is predominantly sodium carbonate/sodium bicarbonate in nature. Aside from <br />high concentrations of sodium, none of the other parameters, including the heavy metals, are <br />found in significant concentrations. As for sodium, there aze no applicable numeric standards or <br />criteria. <br />Elevated sodium levels can have negative implications for irrigated soils that are clayey in <br />nature. This is because high sodium can cause such soils to "seal." The sodium adsorption ratio <br />Table 55 <br />Re resentative TDS Standards/Criteria <br />TDS Standards or Criteria TDS (m /L) <br />Seconds Drinkin Water Standard 500 <br /> <450: None <br />Restrictions for Irrigation 450 - 2,000: Slight to Moderate <br /> >2,000: Severe <br />Restrictions for Livestock <1,000: None <br /> 1,000-3,000: None forACClimatedLivestock <br />Restrictions for Recreation No restrictions <br /> High TDS can cause deposits in heat exchangers and <br />Restrictions for Industrial Use boilers. (Ambient North Fork water would require <br /> treatment . <br />A vatic Life No TDS standards <br /> <br />2.05-137 Revised June 2005 PR/0; Rev. March 2006; Rev. May 1006 PR70 <br />
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