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2008-08-14_REVISION - M1980244 (3)
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2008-08-14_REVISION - M1980244 (3)
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Last modified
6/15/2021 5:52:17 PM
Creation date
8/18/2008 2:32:10 PM
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DRMS Permit Index
Permit No
M1980244
IBM Index Class Name
REVISION
Doc Date
8/14/2008
Doc Name
Revegetation Review
From
DRMS-jle
To
DRMS-bmk
Type & Sequence
AM9
Email Name
BMK
Media Type
D
Archive
No
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14 August 2008 <br />Pg. 3 <br />(14) In Grassy Valley, the hydraulic gradient in the diatreme at depth is expected to be essentially <br />opposite to that of the shallow alluvium (Fig. 4.9). It is difficult to comprehend that all infiltration will <br />be captured by the deeper hydraulic gradient before being transported down the Grassy Valley and off <br />site by the shallow gradient especially if the alluvium is more transmissive than the diatreme. This <br />possibility seems more likely in the event of higher precipitation or runoff events, and such events <br />could lead to metals loading to the Grassy Valley alluvium and points downgradient. The proposed <br />mitigation plan in the event of this occurrence appears satisfactory, but the monitoring plan seems a bit <br />deficient in ground water monitoring to detect the occurrence upgradient of the compliance points. <br />Please address this concern in terms of how the proposed monitoring will detect such an occurrence, or <br />provide an augmented plan perhaps consisting of additional monitoring wells upgradient of points of <br />compliance to serve as early warning monitoring sites. <br />(15) In the event of leachate release to the environment, it is always useful to have some knowledge of <br />the expected geochemical interactions between the leachate and the material underlying the pile, <br />bedrock or unconsolidated material, to assess the attenuation properties of the material. This can also <br />be done using leach tests, but might be better approximated using sequential batch tests, which is a <br />documented ASTM method. <br />(16) For post-closure, they should provide a worst-case scenario of the quantity and quality of release <br />from the overburden storage areas. They predict a long-term average release of 6.8 gpm, but ranges <br />would be useful. And again for water quality they stress the bulk acid-base property of the rock. <br />(17) The prediction that the overall seepage water quality will be similar to the Carlton Tunnel water is <br />not entirely gratifying, since the Carlton Tunnel has sulfate running over 1000+ mg/L, which is 4x the <br />drinking water standard. Although the Carlton Tunnel was discharging 1000 mg/L sulfate long before <br />Anglo arrived, a new facility predicted to discharge a constituent with 4x the drinking water standard <br />might cause concern, even though sulfate is a secondary standard. <br />(18) The statement that the water quality will be similar to Carlton Tunnel water is of concern on two <br />levels: <br />A. First, these are two significantly different environments - one being an underground flow system <br />that has been flowing for decades and has established some level of equilibrium as evidenced by <br />the relatively consistent water quality of the tunnel discharge, the other a pile of fresh, crushed <br />rock that will be exposed to a new environment of weathering and oxidizing conditions. It is <br />unlikely the two systems will weather and leach similarly. <br />B. Second, the Carlton Tunnel has been there for 60+ years, and if an assumption is made that the <br />ground water flow system feeding it has established some kind of stasis or equilibrium, then I <br />wonder about the existence of preferential flow paths causing selective dissolution and depletion <br />of available minerals along those flow paths. The OB that will be crushed and piled will be fresh <br />material that has not undergone that level of selective dissolution and depletion.
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