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2014-05-29_HYDROLOGY - M1977342
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2014-05-29_HYDROLOGY - M1977342
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Last modified
9/4/2020 5:46:18 AM
Creation date
6/3/2014 8:21:03 AM
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Template:
DRMS Permit Index
Permit No
M1977342
IBM Index Class Name
Hydrology
Doc Date
5/29/2014
Doc Name
5-Quarter Water Quality Data and Baseline Parameters Report
From
Climax
To
DRMS
Permit Index Doc Type
Hydrology Report
Email Name
PSH
Media Type
D
Archive
No
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' CMC—Henderson Operations <br /> 5-Quarter Water Quality Data and Baseline Parameters Report <br /> May 2014 <br /> 1 performed at MLGW-ACR over a period of five (5) calendar quarters from the 4th quarter of 2012 <br /> through the 4th quarter of 2013 for the parameters listed in GWMP Tables 4-1 and 4-3. <br /> ' 3.1.2 Baseline Parameters Data Assessment <br /> MLGW-ACR baseline monitoring data is summarized in Table A — MLGW-ACR Monitoring Data. <br /> Results were compared against the domestic water supply standards specified in Table 1 and Table 2 <br /> (refer to Appendix B) of the Colorado Water Quality Control Commission Basic Standards for <br /> Groundwater (CBSG). All results were below the standards with the exception of iron and manganese, <br /> ' both secondary aesthetic standards.A graph summarizing iron and manganese concentrations is presented <br /> in Figure 1. Iron exceeded the CBSG Table 2 standard of 300 ug/L in two out of the five monitoring <br /> events on 12/20/2012 and 2/5/2013 with measured concentrations of 428 ug/L and 340 ug/L,respectively. <br /> Manganese exceeded the CBSG Table 2 standard of 50 ug/L in two out of the five monitoring events on <br /> 1 12/20/2012 and 2/5/2013 with measured concentrations of 225 ug/L and 72.5 ug/L respectively. These <br /> elevated iron and manganese concentrations do not appear to be in any way related to mining activities, <br /> rather, they may be due to the condition of the steel casing in the well and potential presence of iron <br /> reducing bacteria. Henderson intends to conduct further research to explore this possibility. As <br /> mentioned,no other baseline monitoring parameter results exceeded applicable CBSG standards nor were <br /> tthere any other apparent trends that were a cause for concern. <br /> The baseline water quality assessment did not result in the identification of any additional parameters that <br /> warranted consideration for inclusion in the established indicator parameter list for future monitoring at <br /> MLGW-ACR. The original set of indicator parameters summarized in Section 4.1 of the GWMP, <br /> including consideration for trace elemental cations, anionic species, oxyanions and field data, appears to <br /> continue to be an appropriate approach for this well. As stated in Section 4.2 of the GWMP, upon <br /> ' completion of baseline monitoring at MLGW-ACR, only those indicator parameters that also appear in <br /> CBSG Tables 1 and 2 (Domestic Water Supply)will be monitored on an ongoing basis: iron, manganese, <br /> selenium,zinc,pH and sulfate. <br /> 3.1.3 NPL Assessment <br /> ' Consistent with Section 5.1 of the GWMP, Henderson proposes that NPLs for MLGW-ACR be <br /> established using the most stringent domestic water supply use standards specified in CBSG Tables 1 and <br /> ' 2 (refer to Appendix B) for dissolved selenium, zinc and sulfate. The NPL range for pH was developed <br /> using ambient data as discussed in Section 3.4 below. Consistent with the Technical Consulting Report <br /> Establishing Background Threshold Values (BTVs) - Henderson Mill (Gateway Enterprises, 2014), <br /> ' included as Appendix C, Henderson proposes that NPLs for dissolved iron and dissolved manganese be <br /> developed after an investigation to determine the source of elevated Fe and Mn in the well, including the <br /> ' Page 3 of 9 <br />
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