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REGIONAL WATER BOARD REWNSE (SWRCB/OCC FILE A-1886) -6- <br /> PETITION FOR REVIEW OF WASTE DISCHARGE REQUIREMENTS <br /> ORDER NO. R5-2007-0113 (NPDES NO. CA0079243) <br /> CITY OF LODI, WHITE SLOUGH WATER POLLUTION CONTROL FACILITY <br /> CONTENTION D: INCORRECT HARDNESS USED FOR ESTABLISHING EFFLUENT <br /> LIMITATIONS FOR METALS <br /> The Permit establishes Effluent Limitations for metals based on the hardness of the <br /> effluent as opposed to the ambient upstream receiving water hardness as required by <br /> Federal Regulations, the California Toxics Rule (CTR, 40 CFR 131.38(c)(4)). <br /> The Order has established the CTR metals hardness-dependent criteria based on the <br /> reasonable worst-case effluent and receiving water hardness. Effluent limitations for the <br /> discharge must be set to protect the beneficial uses of the receiving water for all discharge <br /> conditions. In the absence of the option of including condition-dependent, "floating" effluent <br /> limitations that are reflective of actual conditions at the time of discharge, effluent limitations <br /> must be set using a reasonable worst-case condition in order to protect beneficial uses for all <br /> discharge conditions. <br /> The petitioner contends that the CTR requires the use of the ambient "upstream" receiving <br /> water hardness for calculating CTR hardness-dependent metal criteria. The petitioner has <br /> misquoted the regulations. The federal regulations at 40 CFR 131.38(c)(4)(i) state, in part, <br /> "For purposes of calculating freshwater aquatic life criteria for metals from the equations in <br /> paragraph (b)(2) of this section, for waters with a hardness of 400 mg/1 or less as calcium <br /> carbonate, the actual ambient hardness of the surface water shall be used in those <br /> equations..." It does not state that the "upstream" ambient surface water hardness, it simply <br /> states the ambient hardness. The term "ambient" is not defined by statute, so it cannot be <br /> assumed to mean the upstream surface water hardness. Using the ambient hardness that is a <br /> mixture of effluent and receiving water (i.e. downstream of the discharge), is the critical <br /> hardness for calculating the CTR hardness dependent metals criteria, because, this is the <br /> area of the receiving stream that is affected by the discharge. A recent study developed by <br /> Dr. Robert Emerick, titled, Developing Protective Hardness-based Metal Effluent Limitations, <br /> indicates that using the lowest upstream receiving water hardness for establishing water <br /> quality criteria is not always the most protective for the receiving water. The study describes <br /> methodologies for assigning fixed effluent limitations for hardness based metals that will be <br /> protective under all dilution conditions when the final mixed receiving water/effluent hardness <br /> is less than 400 mg/L, without being overly restrictive. The Regional Water Board has <br /> evaluated the study and concurs that for some parameters, the beneficial uses of the receiving <br /> water are best protected using the lowest hardness value of the effluent, while for other <br /> parameters, using both the lowest hardness value of the receiving water and the lowest <br /> hardness value of the effluent is the most protective. The approach presented in <br /> Dr. Emerick's study was used for calculating the CTR hardness-dependent metals criteria in <br /> the Order. <br />