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SPX CORPORATION ORDER R5-2019-0018 <br /> SPX MARLEY COOLING TECHNOLOGIES GROUNDWATER CLEANUP NPDES NO. CA0081787 <br /> Evaluations (TREs)for Selenastrum capricornutum in 2015, C. dubia in 2015, <br /> and C. dubia in 2017. The 2015 TREs concluded the toxicity was caused by <br /> polymer coagulant overdosing and as a result, the Discharger adjusted <br /> polymer dosing and the toxicity caused by polymer overdosing has since been <br /> eliminated. The 2017 TRE showed there was a groundwater gradient shift, <br /> which may have been caused by extreme wet weather. As a result, the <br /> Discharger has made operational adjustments to address reduced hardness <br /> and EC in the groundwater being treated. The Discharger also failed the June <br /> 2018 toxicity test; however, this was quickly determined to be the result of a <br /> plant upset caused by bringing the Facility back online after a 4-month <br /> shutdown where significant repairs were required due to vandalization which <br /> occurred during the shutdown. The Discharger has made repairs and toxicity <br /> has been eliminated in the last two normal toxicity tests. Therefore, the <br /> discharge does not have reasonable potential to cause or contribute to an <br /> instream exceedance of the Basin Plan's narrative toxicity objective. <br /> D. Final Effluent Limitation Considerations <br /> 1. Mass-based Effluent Limitations <br /> 40 C.F.R section 122.45(f)(1) requires effluent limitations be expressed in terms of <br /> mass, with some exceptions, and 40 C.F.R. section 122.45(f)(2) allows pollutants that <br /> are limited in terms of mass to additionally be limited in terms of other units of <br /> measurement. This Order includes effluent limitations expressed in terms of mass and <br /> concentration. In addition, pursuant to the exceptions to mass limitations provided in <br /> 40 CF.R. section 122.45(f)(1), some effluent limitations are not expressed in terms of <br /> mass, such as pH and temperature, and when the applicable standards are expressed <br /> in terms of concentration (e.g., CTR criteria and MCL's) and mass limitations are not <br /> necessary to protect the beneficial uses of the receiving water. <br /> 2. Satisfaction of Anti-Backsliding Requirements <br /> The effluent limitations in this Order are at least as stringent as the effluent limitations in <br /> the previous Order, with the exception of effluent limitations for total chromium. The <br /> effluent limitations for these pollutants are less stringent than those in Order R5-0214- <br /> 0013. This relaxation of effluent limitations is consistent with the anti-backsliding <br /> requirements of the CWA and federal regulations. <br /> a. CWA section 402(o)(1) and 303(d)(4). CWA section 402(o)(1) prohibits the <br /> establishment of less stringent water quality-based effluent limits "except in <br /> compliance with Section 303(d)(4)." CWA section 303(d)(4) has two parts: <br /> paragraph (A) which applies to nonattainment waters and paragraph (B) which <br /> applies to attainment waters. <br /> i. For waters where standards are not attained, CWA section 303(d)(4)(A) <br /> specifies that any effluent limit based on a TMDL or other WLA may be revised <br /> only if the cumulative effect of all such revised effluent limits based on such <br /> TMDL's or WLAs will assure the attainment of such water quality standards. <br /> ii. For attainment waters, CWA section 303(d)(4)(B) specifies that a limitation <br /> based on a water quality standard may be relaxed where the action is <br /> consistent with the antidegradation policy. <br /> The Stockton Diverting Canal is considered an attainment water for total chromium <br /> because the receiving water is not listed as impaired on the 303(d) list for this <br /> ATTACHMENT F- FACT SHEET F-32 <br />