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DAUB & ASSOCIATES, INC. 1985'Y2 SOUTH BROADWAY <br /> hi GRAND JUNCTION, CO 81507-9649 <br /> (970)254-1224 <br /> FAX(970)242-8438 <br /> email: gjdaub@daubandassociates.com <br /> www.daubandassociates.com <br /> November 19, 2020 <br /> -..� <br /> Mr. Nathan Wiser ;=a <br /> US EPA Region VIII <br /> Mail Code: 8WD-SDU NOV 2 5 2020 <br /> 1595 Wynkoop Street <br /> Denver, CO 80202-1129 <br /> Re: Natural Soda LLC, EPA UIC Permit C030358-00000: BG-9 Elevated Groundwater <br /> Chemistry <br /> Dear Mr. Wiser: <br /> The BG-9 groundwater monitoring well is exhibiting elevated chemistry values for conductivity, total <br /> dissolved solids, and alkalinity. The BG-9 is a B-Groove Aquifer (BG) and subsurface subsidence <br /> monitoring well, recompleted from the DS-5, which was initially drilled as a core hole and completed <br /> as a Dissolution Surface (DS)Aquifer and subsurface subsidence monitoring well. The DS-5 began <br /> showing elevated chemistry and temperatures, indicating possible communication with the proximal <br /> solution mining operations. The casing was intact, so the decision was made to recomplete the well <br /> to utilize it both as a BG Aquifer monitor and a subsurface subsidence monitoring well. This was <br /> accomplished by setting a bridge plug near the end of the casing, placing cement on top of the <br /> bridge plug, and then perforated the casing across the BG Aquifer interval. <br /> The chemistry departure in the BG-9 began in late 2019, but has accelerated since April of 2020. <br /> Conductivity values have subsequently elevated to the 15-16K micromhos range. An investigation <br /> was initiated to determine the cause. A video log was performed in the BG-9 on October 12, 2020. <br /> Initially, the video log showed very little fluid movement in the well until the cement plug was <br /> reached, where there was evidence of minor upflow. Subsequent scrutiny, however, revealed four <br /> slight casing partings just above casing couplings at depths of 1676.9, 1760.9, 1782.2, and 1804.2. <br /> While haloclines due to saline stratification were observed at various depths, no apparent inflow or <br /> outflow was observed from these partings. <br /> Due to the casing partings but lack of apparent flow, it was decided to remediate the well by <br /> plugging it with a second bridge plug and cementing it back to just below the BG Aquifer <br /> perforations in order to continue utilizing it as a BG monitoring well. Subsequent to the plug back, <br /> the well was airlifted to clean out the well and ensure good flow through the perforations. Field <br /> samples indicated conductivity in the range of 45-50K micro-Siemens (field measurements), <br /> appreciably above the 16K micromhos (lab analysis) seen prior to plugging back the well. The well <br /> was airlifted at intervals for three days to remove any high conductivity fluids. Conductivity fell to <br /> 30k micro-Siemens before the effort was halted. <br /> It is believed that DS Aquifer water was migrating up inside the casing and mixing with the BG up <br /> through the first cement plug, and possibly through the casing partings. During subsequent <br /> operations, the DS water was forced out of the perfs, creating a localized concentration of higher <br /> conductivity water. <br /> NS proposes that the localized high conductivity water will dissipate. The 13G-9 will be sampled at a <br /> weekly interval to monitor the water chemistry (field parameters via sampling pump or dump bailer <br /> for temperature, conductivity, and pH). If the elevated conductivity continues to lower, then the <br /> SPECIALIZING IN PROFESSIONAL GEOLOGICAL, ENVIRONMENTAL, HYDROLOGICAL, GEOTECHNICAL AND PERMITTING SERVICES <br />