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HYDRO31327
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Last modified
8/24/2016 8:55:04 PM
Creation date
11/21/2007 1:32:35 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981010
IBM Index Class Name
Hydrology
Doc Date
5/7/1996
Doc Name
FLY ASH USE AS HUAL ROAD SUBBASE TRAPPER MINE PN C-81-010 TRAPPER MINING INC
From
DMG
To
TRAPPER MINING INC
Permit Index Doc Type
CORRESPONDENCE
Media Type
D
Archive
No
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data, the study concludes that contamination from the use <br />of ash in roadway subsoil can be avoided by careful <br />planning, on a site-specific basis. <br />It would appear that no direct conclusion can be drawn <br />from this study, as to how it pertains to the Trapper <br />Mine, since the results would depend upon site-specific <br />conditions. Further study would be required at the actual <br />site, as it pertains to ground water hydrologX and near <br />surface soil permeability, before the Division can <br />approve such a plan. <br />This study presented data from five sites, located in <br />Georgia, Arkansas, Pennsylvania, Kansas and Arizona. It <br />would seem logical that the data from Arizona and Kansas <br />would be more relevant to Colorado than would the other <br />sites. It would appear that the data at these two sites <br />have some problems. On page 6-15 of the study it is <br />stated that there is no downgradient well at the Arizona <br />site. Also, the statistical conclusions from the Arizona <br />site were described, on page 6-17 of the report, as <br />"tentative because of the scarcity of the data." At the <br />Kansas site, the study was somewhat hampered by local <br />variations in native chemical constituents, as reported <br />on pages 5-15 and 5-16. However, the study found, as <br />stated on page 5-16, that limited leaching of ash <br />constituents is occurring down to a depth of about three <br />feet. This was after six years of fly ash use. <br />The Division believes that it should not base its <br />decision, for this kind of a project, on data from just <br />two sites, when one of the two sites, in Arizona, has <br />inconclusive evidence. The other site, in Kansas, did <br />show some leaching of fly ash constituents, but levels <br />were below regulatory standards (see No. 3 below), except <br />for sulfate, which the study concludes is due to native <br />sulfates, not fly ash (see page 5-19). <br />The Division could not find any reference in this report <br />as to how EPA classifies fly ash. Also, there does not <br />seem to be a clear explanation of which regulatory <br />standards are being used in the analyses. Each analyses <br />section for each of the five sites in this report <br />contains a table which lists the regulatory levels for <br />eight chemical ions. There are two regulatory levels <br />listed. One is TCLP (toxicity characteristic leaching <br />procedure) and the other is MCL (maximum contaminant <br />level). For example, Table 6-5, on page 6-11, lists TCLP <br />and MCL levels for the Arizona site, both in mg/L. On <br />page 6-10 there is a discussion of the results of Table <br />6-5. The eight metals listed in the table are RCRA metals <br />so, it is assumed, all of the regulatory standards used <br />in this study are related to RCRA, and, therefore, are <br />from the EPA. <br />
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