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2021-06-02_HYDROLOGY - M1977342 (2)
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2021-06-02_HYDROLOGY - M1977342 (2)
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Last modified
12/27/2024 8:39:51 PM
Creation date
6/3/2021 7:03:09 AM
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DRMS Permit Index
Permit No
M1977342
IBM Index Class Name
HYDROLOGY
Doc Date
6/2/2021
Doc Name
Water Monitoring - Groundwater
From
Climax Molybdenum
To
DRMS
Email Name
PSH
Media Type
D
Archive
No
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CMC—Henderson Operations <br /> DRMS 2020 Annual Water Monitoring Report <br /> May 2021 <br /> 2.2.3 Proposed Point of Compliance Sampling Location: MLGW-17 <br /> MLGW-17 is a deep alluvial well located downgradient of 3-Dam.Although a trend of increasing <br /> dissolved iron and zinc concentrations was noted previously, most of the 2019 and all of the 2020 <br /> results indicate an overall decrease in concentrations. <br /> Tabular data for MLGW-17 along with applicable NPLs are presented in Table 2. Accompanying <br /> graphs are provided in Trend Evaluations 25-28. <br /> 2.2.4 Point of Compliance Sampling Location: MLGW-ACR <br /> MLGW-ACR is a domestic water supply POC well located in the Aspen Canyon Ranch area. <br /> Starting in the third trimester of 2019,changes to the MLGW-ACR sampling method likely caused <br /> disturbances to the solid-wall well construction indicated by the increase in iron concentrations <br /> and established the need for the well to undergo rehabilitation. The current results presented are <br /> not believed to be representative of background water quality. Well rehabilitation will be <br /> conducted. <br /> Altogether, this has been an effort to establish an accurate representation of the ambient <br /> groundwater conditions far downstream from Henderson operations. Henderson will continue to <br /> evaluate the data collected at MLGW-ACR following future sampling events to better understand <br /> these data. <br /> Tabular data for MLGW-ACR along with applicable NPLs are presented in Table 2. <br /> Accompanying graphs are provided in Trend Evaluations 29-32. <br /> 2.2.5 Surface Water Sampling Location: WFR-20 <br /> WFR-20 is located upgradient of the Henderson Mill in the Williams Fork River and serves as an <br /> indicator of background surface water quality.A small increase in specific conductivity and sulfate <br /> during the second and third trimesters, respectively, during the summer and low-flow months <br /> might correlate with influence from Williams Fork wildfire activity. Firefighting efforts and <br /> rainfall can mobilize suspended and dissolved material into surface water. Although an increase <br /> in pH and metal concentrations was not observed, WFR-20 will continue to be monitored while <br /> the newly burned area remains susceptible to increased erosion. <br /> Tabular data for WFR-20 are presented in Table 2 with accompanying Trend Evaluations 33-36. <br /> 2.2.6 Surface Water Sampling Location: WFR-40 <br /> WFR-40 is located downgradient of the Henderson Mill in the Williams Fork River.Although still <br /> within historical levels,pH and sulfate concentrations measured in 2020 increased relative to 2019 <br /> which may relate to the Williams Fork fire activity. Increased pH and major ion loading into <br /> adjacent surface water are common responses from runoff interacting with a recently burned area. <br /> WFR-40 will continue to be monitored to determine potential influences from the recent fire <br /> activity. <br /> Tabular data for WFR-40 are presented in Table 2 with accompanying Trend Evaluations 37-40. <br /> 4of5 <br />
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