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2022-03-10_REVISION - C1981044
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2022-03-10_REVISION - C1981044
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Last modified
3/11/2022 9:27:09 AM
Creation date
3/11/2022 7:45:53 AM
Metadata
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Template:
DRMS Permit Index
Permit No
C1981044
IBM Index Class Name
Revision
Doc Date
3/10/2022
Doc Name
Adequacy Review - Preliminary
From
Miranda Kawcak
To
DRMS
Type & Sequence
MT8
Email Name
RAR
JLE
Media Type
D
Archive
No
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23. Please provide the missing data for well 9BF as outlined in the permit monitoring requirements. <br /> a) Well 9BF has been monitored as outlined in the monitoring requirements.Well 9BF is <br /> a newer well and was never added to the AHR layout. MCM will be adding the water <br /> year and the historic data for 9BF to the 2021 AHR and future AHRs. <br /> 24. Please provide an analysis of the excursions in Well 8 1-01 and the No. 9 Mine Well. <br /> a) Well81-01 <br /> • Monitoring well 8 1-01 is screened within the Middle Sandstone located <br /> approximately 60 ft above F coal seam mined at the facility. The well is <br /> located immediately above the Williams Fork Mine shadow area. Review of <br /> the 2020 monitoring data indicates that the water level in well 81-01 is <br /> consistent with historic water levels,which have been stable since <br /> monitoring was reactivated in 2006. Although the iron measured at 8 1-01 <br /> exceeded the Domestic Water Supply Drinking Water standard(0.3 mg/L)it <br /> remains within the Agricultural Standard of 5 mg/L. This is characteristic of <br /> the Middle Sandstone which exhibited an average dissolved iron <br /> concentration of 0.41 mg/L(range: <0.02— 1.51 mg/L)that was greater than <br /> the Drinking Water Standard prior to mining (Well TR-4). Furthermore the <br /> Drinking Water Standards should not be applied to deep bedrock wells <br /> where there are no known users and limited potential for future use due to <br /> the high economic cost for drilling to the depth of the Middle Sandstone <br /> (-533 ft bgs) and location within the mine boundary. Similarly manganese <br /> exceeds the Drinking Water Standard but does not exceed the Agriculture <br /> standard, as the 0.2 mg/L Agricultural Standard is only applicable to areas <br /> where irrigation water is being applied to soils with pH values less than 6 <br /> (see Regulation 41). The Middle Sandstone is not being used for irrigation <br /> purposes and acidic soils are not present at Williams Fork,therefore this <br /> standard should not apply. The pH in the 2020 remained neutral indicating <br /> the iron and manganese where not mobilized by acidic conditions. Its <br /> possible that the filter may have burst during sample collection and the iron <br /> and manganese concentrations were elevated by solids greater than 0.45 <br /> micron that would normally be removed. Magnesium does not have a <br /> Drinking Water or Agricultural Groundwater Quality Standard and has <br /> remained fairly stable over the last few years. An increased emphasis on <br /> monitoring techniques and evaluation of the wells condition will occur <br /> during the 2022 monitoring event. <br /> b) No. 9 Mine Well(9MN) <br /> • Monitoring well 9MN is located between the Williams Fork F and E Seam <br /> Workings and Empire's P Seam Workings. The well is screened within the <br /> Twentymile Sandstone,which is several hundred ft above the F coal <br /> (shallower of two seams mined at Williams Fork) and is separated by several <br /> units of low permeable siltstone and mudstone which act as an aquitard. The <br /> groundwater levels within 9MN have remained stable since the mine ceased <br /> using the well for water supply purposes and are above the water levels <br /> present within the lower sandstone units further indicating the Twentymile <br /> Sandstone remains disconnected from deeper groundwater that could <br /> potentially be influenced by the Williams Fork underground mine <br /> area. Groundwater within the Twentymile Sandstone generally flows from <br /> the southeast to the northwest.Well 9MN is located approximately 1000 ft <br /> 4 1 P a g e <br />
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