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Public Works - 2 - 27 July 2016 <br /> 1810 Hazelton Avenue <br /> Stockton, San Joaquin County <br /> 2. An MRP is needed to establish which Site wells will be used to monitor background <br /> (naturally occurring constituents), identify treatment, transition, and compliance zone wells, <br /> and detail the frequency of sampling and constituents to be analyzed at each well. <br /> Background wells should be located outside the area of petroleum impacts, and have <br /> historically not had any detections of pollutants, such as Site well MW-7. The need for <br /> establishing background levels of metals in groundwater is due to the potential production of <br /> harmful byproducts caused by the use of strong oxidizers, such as ozone, in the subsurface. <br /> Treatment zone wells should be located within the area of proposed active ozone injection, <br /> and transition zone wells should be located just down-gradient of the active injection area. <br /> Compliance zone wells should be located down-gradient from the transition zone wells, <br /> outside of the area of active injection but not greater than 50 feet from the injection area. An <br /> example zone setup diagram is included as Attachment D of the General Order. Please <br /> identify treatment, transition, and compliance zone wells in the MRP to be submitted as part <br /> of the NOI Addendum due 30 October 2016. <br /> 3. The network of existing and proposed wells does not allow for the establishment of proper <br /> transition and compliance zone monitoring. Additional monitoring wells need to be proposed <br /> to align this project with the General Order in order to operate under this permit. By <br /> 30 September 2016, please submit a Work Plan which proposes additional downgradient <br /> monitoring wells for transition and compliance zone monitoring related to proposed ozone <br /> injection. <br /> 4. Analysis of samples from background wells must include at a minimum: arsenic, total <br /> chromium, hexavalent chromium, bromide, and total dissolved solids (TDS). Background <br /> sample concentrations are used to establish Action Levels. An Action Level is set at 20% <br /> above the naturally occurring background concentrations. If background levels already <br /> exceed the Water Quality Objective (WOO), the Action Level is set at the background <br /> concentration and is not allowed to increase in compliance zone wells above what is <br /> naturally occurring. The WQOs for arsenic, total chromium, hexavalent chromium, bromide, <br /> and TDS are 10 ug/L, 50 ug/L, 10 ug/L, 2,300 ug/L, and 450,000 ug/L, respectively. <br /> Analysis of background samples should be performed by methods that provide Practical <br /> Quantitation Limits (laboratory reporting limits) that are lower than the WQOs to comply with <br /> the requirements of the General Order, and provide usable data. Please identify <br /> background wells and provide background data (including above listed analytes) as part of <br /> the NOI Addendum 30 October 2016. <br /> 5. A Contingency Plan is needed to detail actions that will be taken in the event that chemicals <br /> of concern in compliance zone wells exceed Action Levels. A Contingency Plan must <br /> include more than just discontinuing injection, but must also state active steps that will be <br /> implemented to reduce concentrations of constituents exceeding Action Levels. Please <br /> submit a Contingency Plan which includes calculated Action Levels as part of the NOI <br /> Addendum due 30 October 2016. <br /> 6. The lateral and vertical extent of the petroleum hydrocarbon pollution in groundwater has <br /> not been defined to the Water Quality Objects at this Site. MW-4 recently contained <br /> concentrations of MTBE of 11 ug/L, which is above the WOO of 5 ug/L. Additionally, the <br /> distance of approximately 230 feet between MW-3 and MW-4 is not adequate for delineation <br />