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IRM Prove-Out Reports -2- 29 August 1991 <br /> DDRW, Tracy <br /> not only is extracting water, but is also injecting water into the aquifer, and <br /> because there is an inadequate hydraulic data base at this site, Tracy should <br /> monitor the SWL in the injection and extraction wells for a 24 hour period prior <br /> to the implementation of the full-phase operations. This information may be used <br /> as a baseline and to determine whether or not there are any fluctuations in the <br /> water levels due to pumping influences from on- or off-site supply wells. This <br /> hydraulic information may be useful for the final design of the ground water <br /> remedial system. <br /> 2. Page 4. It is unclear what is meant by the term "surface level " . The surface <br /> level was used as the reference point for ground water level measurements. It is <br /> assumed that the surface level is the top of the casing. <br /> 3. Page 5. One of the conclusions drawn from the Prove-Out Phase is that the <br /> performance (injection flow rate) of IW-2 is much lower than that of the other two <br /> injection wells. The report states that IW-2 fills up if the flow rate exceed 15 <br /> gallons per minute (gpm) . The limited performance of this injection well was not <br /> discussed in the report. Tracy needs to evaluate why the performance of this well <br /> is less than the design, particularly when the construction was similar to that of <br /> the other injection wells. The reasons for the poor performance of IW-2 should be <br /> considered for the final ground water remedial design to optimize the performance <br /> of that system. Tracy should also consider the use of pilot holes for the final <br /> remedial design to confirm the lithologies in the areas where the injection wells <br /> are to be installed. <br /> 4. Pages 5 and 10. The data collected during the Potable Water Start-Up and Prove-Out <br /> Phases are listed in different groups of tables and figures. However, the text of <br /> the report does not provide any discussion on the tables and figures. Of <br /> particular concern is that the differences in the patterns of measured ground water <br /> levels between the different wells was not discussed. Some type of data evaluation <br /> should have been presented in the text of the report. This discussion could be <br /> helpful for future design considerations of the final ground water remedial <br /> measure. <br /> 5. Page 6. It appears that the Contaminated Water Start-Up Phase was not performed. <br /> This phase was required under Discharge Specification C. 2. of the WORs. If the <br /> Contaminated Water Start-Up Phase was performed, the report did not provide any <br /> discussion on this phase. However, because the IRM proceeded to the Prove-Out <br /> Phase and ended up with positive results, this deficiency should not prevent the <br /> Full-Scale Operation of the IRM. <br /> 6. Page 8. It is unclear whether each extraction well pump was operated for one hour <br /> and observed through three pumping cycles to confirm the proper operation of the <br /> pumps. This requirement is listed under Discharge Specification C. 2. iii . of the <br /> WDRs. Because this was a requirement of the Contaminated Water Start-Up Phase, <br /> which appears not to have been performed, this may have been performed under the <br /> Prove-Out Phase. The report should have more clearly specified whether and when <br /> the proper operation of the pumps was determined. <br /> 7. Page 8. One of the extraction wells (EW-5) was not pumped for the full 96 hours <br /> as required under Discharge Specification C. 3. i . of the WDRs due to a malfunction <br /> of the discharge valve. However, the well was pumped for 78 hours with no other <br />