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Public Works 2 27 July 2016 <br />1810 HazeIton Avenue <br />Stockton, San Joaquin County <br />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 />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 />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 (WQO), 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 WQ0s 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 WQ0s 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 />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 NO1 <br />Addendum due 30 October 2016. <br />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