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North County Recycling Center and Sanitary Landfill <br />Storm Water Pollution Prevention Plan <br /> <br /> <br /> <br />Page 58 <br />12.3.1 Level 2 ERA Action Plan <br />If Level 2 status is reached, a facility must certify and submit, via SMARTS, a Level 2 ERA <br />Action Plan prepared by a facility designated QISP that addresses each new Level 2 NAL <br />exceedance. This must be completed by January 1 following the reporting year during which <br />the NAL exceedance(s) occurred. <br />For each new Level 2 NAL exceedance, the Level 2 Action Plan will identify which Level 2 <br />ERA Technical Report demonstration the facility has selected to perform as an evaluation. See <br />SWPPP Section 12.3.2 for the list of technical reports demonstrations <br />All elements of the Level 2 ERA Action Plan shall be implemented as soon as practicable and <br />completed no later than one year after submitting the Level 2 ERA Action Plan. The Level 2 <br />ERA Action Plan shall include a schedule and a detailed description of the tasks required to <br />complete a facility’s selected demonstration. <br />On December 28, 2017, a Level 2 ERA Action Plan was prepared to address the iron NAL <br />exceedances. The Action Plan selected the industrial activity BMP demonstration. However, <br />soil analytical tests performed in December 2017 are showing that there is a considerable <br />amount of aluminum and iron in the native soils. (Refer to Section 2.3 of this SWPPP.) Upon <br />further testing and evaluation, the demonstration may be changed to a natural background <br />pollutant source. A copy of the Level 2 ERA Action Plan (and any revisions to it) is included <br />in Appendix K. <br />12.3.2 Level 2 ERA Technical Report <br />On December 11, 2018, San Joaquin County submitted on SMARTS a Technical Report <br />proposing a “Natural Background Pollutant Source Demonstration” as described in <br />Section XII.D.2.c of the General Permit. The County believes the cause of the aluminum and <br />iron NAL exceedances to be solely attributable to the natural soils for the following reasons: <br />1. Samples of storm water discharges collected from drainage areas SW-3 and SW-4 have <br />had elevated aluminum and iron concentrations. The concentrations have been very <br />consistent and similar for the two drainage areas even though the industrial activities <br />in these areas are very different. There are essentially no aluminum or iron producing <br />activities within drainage area SW-4, while most of the landfill activities that could <br />produce those metals are found in drainage area SW-3. Drainage area SW-4 is <br />generally upwind and higher in elevation than the SW-3 drainage area; meaning that it <br />would not typically experience wind deposition or run-on from drainage area SW-3. <br />2. Soil samples that were collected from the storm water conveyance swales in both <br />drainage areas tested significantly high in aluminum and iron. The same was true for <br />soil samples collected from exclusively non-industrial areas. When some of the soil <br />was placed in deionized water and the water was tested, it was found to be very high in <br />aluminum and iron. These soil samples had never come into contact with industrial <br />activities or with runoff from industrial activities. <br />3. NRCS soil survey data and other studies show that the site has alluvial soil types <br />derived of granite. Academic literature references show minerals contained in granitic