(1) Braden River above Ward Lake. The bacteriological TMDL for Braden River above Ward Lake is 400 counts/100mL for fecal coliform, and is allocated as follows:
    (a) The WLA for wastewater sources is not applicable;
    (b) The WLA for discharges subject to the Department’s NPDES MS4 Permitting Program is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2007 period, will require a 43% reduction of sources contributing to exceedances of the criteria; and
    (c) The LA for nonpoint sources is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2007 period, will require a 43% reduction of sources contributing to exceedances of the criteria.
    (2) Cedar Creek. The bacteriological TMDL for Cedar Creek is 400 counts/100mL for fecal coliform, and is allocated as follows:
    (a) The WLA for wastewater sources is not applicable;
    (b) The WLA for discharges subject to the Department’s NPDES MS4 Permitting Program is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 61% reduction of sources contributing to exceedances of the criteria; and
    (c) The LA for nonpoint sources is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 61% reduction of sources contributing to exceedances of the criteria.
    (3) Gilly Creek. The bacteriological TMDL for Gilly Creek is 400 counts/100mL for fecal coliform, and is allocated as follows:
    (a) The WLA for wastewater sources is not applicable;
    (b) The WLA for discharges subject to the Department’s NPDES MS4 Permitting Program is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 56% reduction of sources contributing to exceedances of the criteria; and
    (c) The LA for nonpoint sources is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 56% reduction of sources contributing to exceedances of the criteria.
    (4) Nonsense Creek. The bacteriological TMDL for Nonsense Creek is 400 counts/100mL for fecal coliform, and is allocated as follows:
    (a) The WLA for wastewater sources is not applicable;
    (b) The WLA for discharges subject to the Department’s NPDES MS4 Permitting Program is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 57% reduction of sources contributing to exceedances of the criteria; and
    (c) The LA for nonpoint sources is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 57% reduction of sources contributing to exceedances of the criteria.
    (5) Nonsense Creek. The TMDLs to address the low DO condition are an annual median TN of 0.89 mg/L and an annual median BOD of 2.0 mg/L, and are allocated as follows:
    (a) The WLA for wastewater point sources is not applicable;
    (b) The WLAs for discharges subject to the Department’s NPDES MS4 Permitting Program are a 27% reduction of current anthropogenic TN and a 36% reduction of current anthropogenic total BOD loading based on measured concentrations from the 2001 to 2008 period; and
    (c) The LAs for nonpoint sources are a 27% reduction of current anthropogenic TN, and a 36% reduction of current anthropogenic total BOD loadings based on measured concentrations from the 2001 to 2008 period.
    (6) Rattlesnake Slough. The bacteriological TMDL for Rattlesnake Slough is 400 counts/100mL for fecal coliform, and is allocated as follows:
    (a) The WLA for wastewater sources is not applicable;
    (b) The WLA for discharges subject to the Department’s NPDES MS4 Permitting Program is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 48% reduction of sources contributing to exceedances of the criteria; and
    (c) The LA for nonpoint sources is to address anthropogenic sources in the basin such that in-stream concentrations meet the fecal coliform criteria which, based on the measured concentrations from the 2001 to 2008 period, will require a 48% reduction of sources contributing to exceedances of the criteria.
    (7) Rattlesnake Slough. The TMDLs to address the low DO and nutrient impairments in Rattlesnake Slough are 0.84 mg/L of TN, 0.48 mg/L TP, and 2.4 mg/L of BOD and are allocated as follows:
    (a) The WLA for wastewater point sources is not applicable;
    (b) The WLAs for discharges subject to the Department’s NPDES MS4 Permitting Program are 30, 21, and 31% reductions of current anthropogenic TN, TP, and BOD loadings, respectively, based on measured concentrations from the 2001 to 2008 period; and
    (c) The LAs for nonpoint sources are 30, 21, and 31% reductions of current anthropogenic TN, TP, and BOD loadings, respectively, based on measured concentrations from the 2001 to 2008 period.
Rulemaking Authority 403.061, 403.067 FS. Law Implemented 403.061, 403.062, 403.067 FS. History-New 11-2-09, Amended 5-9-21.