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%. w 1 .i <br /> City of Stockton and County of San Joaquin Page 75 <br /> NPDES Permit CAS0083470 <br /> Response to Comments <br /> mandated and a failure to require it would leave the Permit far short of either complying with the <br /> regulations or meeting MEP. <br /> Response: As explained in Board staff's response to Comments 12 and 13,we disagree with <br /> DeltaKeeper's claim that the regulations require MS4 dischargers to report flow, and concentration <br /> and mass loads for discharged pollutants. <br /> 52. Comment: (DK Comment 6) Comments Regarding the Water Quality-Based Program. <br /> The Permit states that"[p]ermittees shall implement a water quality based control program for <br /> pollutants of concern that have a reasonable potential to cause or contribute to exceedances of water <br /> quality standards."Tentative Permit at 44. Urban waterways have already been identified as <br /> "impaired" on the 303(d) list and as toxic hot spots pursuant to the Bay Protection and Toxic <br /> Cleanup Program. These impairments and toxic hot spots are occurring in waters that are habitat <br /> and identified"critical habitat" for species protected pursuant to state and federal endangered <br /> species acts. Storm water discharges have already been identified as causing or contributing to these <br /> impairments and toxic hot spots. The water quality based control programs in the Permit fall far <br /> short of what is minimally required to address these existing impairments and toxic hot spots and <br /> cannot reasonably be considered to comply with an MEP standard. <br /> Eighteen months to three years is far too long to wait before implementation of specific BMPs to <br /> control existing pesticide, pathogen and dissolved oxygen impairment in habitat occupied by <br /> protected species. Especially, since there are a number of obvious on-the-shelf BMPs that are <br /> clearly effective and can be immediately implemented to reduce these existing impacts. For <br /> example, the Permittees can immediately begin enforcing the prohibition against disposal of green <br /> waste in the storm sewer system. This may not completely eliminate the problem,but the discharge <br /> of prodigious quantities of organic matter into local waterways is clearly a significant contributor to <br /> low dissolved oxygen levels following rainfall. Pet waste control ordinances can be immediately <br /> developed and/or enforced since it is obvious that this is a significant source of the enormous <br /> increase in pathogen concentrations following rainfall. Years of delay in instituting obvious BMPs <br /> cannot be considered MEP. <br /> While requirements to work with the Regional Board and other agencies in developing TMDLs is <br /> both welcome and necessary, development and implementation of effective control efforts cannot <br /> wait until the development of TMDLs, which may not occur for many years. The April draft of the <br /> 2002 Revision of the Clean Water act Section 303(d)List of Water Quality Limited Segments <br /> contains no proposed schedule for developing and implementing the TMDLs for local waterway. <br /> We note that the Permit states that the Permittees will participate in stakeholder forams and <br /> collaborative technical studies necessary to assist the Regional Board in completing the TMDLs. <br /> And that these studies may include,but shall not be limited to, additional monitoring/toxicity <br /> studies for pesticides,pathogens and dissolved oxygen in Mosher Slough, Five-Mile Slough, <br /> Calaveras River, Smith Canal, Stockton Deep-water Channel, Joaquin River. Mormon Slough and <br /> Walker Slough. "May"is a discretionary word. Additional monitoring, studies and implementation <br /> of BMPs must not be dependent upon a TMDL that may or may not be developed at some future <br /> unspecified date. Additional studies must be required as soon as technically feasible. <br />