Fla. Admin. Code Ann. R. 62-304.600 - Tampa Bay Basin TMDLs
(1)
Allen Creek (tidal). The bacteriological TMDL for Allen Creek (tidal) 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 2000 to 2007, will require a 67% 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 2000
to 2007, will require a 67% reduction of sources contributing to exceedances of
the criteria.
(2)
Alligator Creek. The bacteriological TMDL for Alligator Creek is 4.4 x
1010 counts/day 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 2000 to 2007 period, will require a 51% 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
2000 to 2007 period, will require a 51% reduction of sources contributing to
exceedances of the criteria.
(3) Bellows Lake Outlet (also known as East
Lake Outfall). The bacteriological TMDL for Bellows Lake Outlet 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 in
2008, will require a 80% 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 in 2008, will require a 80% reduction of sources
contributing to exceedances of the criteria.
(4) Bishop Creek (freshwater). The
bacteriological TMDL for Bishop Creek (freshwater) 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 2000 to 2007 period, will require a 64% 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
2000 to 2007 period, will require a 64% reduction of sources contributing to
exceedances of the criteria.
(5) Bishop Creek (tidal). The bacteriological
TMDL for Bishop Creek (tidal) 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 2008, will require a
64% 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 2008, will require a 64% reduction of sources contributing
to exceedances of the criteria.
(6) Brushy Creek. The bacteriological TMDL
for Brushy Creek is 400 counts/100mL for fecal coliform, and is allocated as
follows:
(a) The WLA for the Hillsborough
County Dale Mabry Advanced Wastewater Treatment Plant (FL0036820) is that it
must meet its NPDES permit limits;
(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 2004 to 2007
period, will require a 36% 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 2004 to 2007 period, will require a 36%
reduction of sources contributing to exceedances of the
criteria.
(7) Bullfrog
Creek (freshwater). The bacteriological TMDL for Bullfrog Creek (freshwater) is
1.66 x 1011 counts/day 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 2000 to 2007
period, will require a 72% 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 2000 to 2007 period, will require a 72%
reduction of sources contributing to exceedances of the
criteria.
(8) Bullfrog
Creek (tidal). The bacteriological TMDL for Bullfrog Creek (tidal) 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 2000 to 2007 period, will require a 46% 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
2000 to 2007 period, will require a 46% reduction of sources contributing to
exceedances of the criteria.
(9) Cross Canal (North). The bacteriological
TMDL for Cross Canal (North) 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 2005 to 2007
period, will require a 59% 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 2005 to 2007 period, will require a 59%
reduction of sources contributing to exceedances of the
criteria.
(10) Double
Branch. The bacteriological TMDL for Double Branch is 43 counts/100mL for fecal
coliform, and is allocated as follows:
(a) The
WLA for the Hillsborough County Northwest Regional Wastewater Reclamation
Facility (FL0041670) is that it must meet the its NPDES permit
conditions;
(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 2000 to 2007 period, will require a 85% 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
2000 to 2007 period, will require a 85% reduction of sources contributing to
exceedances of the criteria.
(11) Little Bullfrog Creek. The
bacteriological TMDL for Little Bullfrog 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 2004 to 2007
period, will require a 74% 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 2004 to 2007 period, will require a 74%
reduction of sources contributing to exceedances of the
criteria.
(12) Lower
Rocky Creek. The bacteriological TMDL for Lower Rocky Creek is 43 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 2000 to 2007 period, will require a 83% 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
2000 to 2007 period, will require a 83% reduction of sources contributing to
exceedances of the criteria.
(13) Moccasin Creek (tidal). The
bacteriological TMDL for Moccasin Creek (tidal) 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 2005 to 2006
period, will require a 60% 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 2005 to 2006 period, will require a 60%
reduction of sources contributing to exceedances of the
criteria.
(14) Mullet
Creek (freshwater). The bacteriological TMDL for Mullet Creek (freshwater) 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 2000 to 2005 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
2000 to 2005 period, will require a 57% reduction of sources contributing to
exceedances of the criteria.
(15) Mullet Creek (tidal). The
bacteriological TMDL for Mullet Creek (tidal) 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 2006, will require a
49% 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 2006, will require a 49% reduction of sources contributing
to exceedances of the criteria.
(16) Rocky Creek. The bacteriological TMDL
for Rocky Creek is 400 counts/100mL for fecal coliform, and is allocated as
follows:
(a) WLAs for the Hillsborough County
Rivers Oaks Advanced Wastewater Treatment Facility (FL0027821) and the
Hillsborough County Northwest Regional Wastewater Reclamation Facility
(FL0041670) are that they meet the facilities' permit limits;
(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 2000 to 2007
period, will require a 58% 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 2000 to 2007 period, will require a 58%
reduction of sources contributing to exceedances of the
criteria.
(17) Sweetwater
Creek. The bacteriological TMDL for Sweetwater 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 2000 to 2007 period, will require a 44% 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
2000 to 2007 period, will require a 44% reduction of sources contributing to
exceedances of the criteria.
(18) Bellows Lake (also known as East Lake).
The TMDLs to address the low DO (addresses downstream impairment) and nutrient
impairments are an annual average TN of 1.40 mg/L, an annual average TP of
0.055 mg/L, and an annual average BOD of 2.00 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 to address anthropogenic sources in the basin such that in-stream
concentrations meet the DO and nutrient criteria which, based on the measured
concentrations in the 2005-2006 period, will require a 30.5% reduction of TN, a
33.3% reduction in TP, and a 63.3% reduction of BOD at sources that are
contributing to exceedances of the criteria; and
(c) The LAs for nonpoint sources are to
address anthropogenic sources in the basin such that in-stream concentrations
meet the DO and nutrient criteria which, based on the measured concentrations
in the 2005 -2006 period, will require a 30.5% reduction of TN, a 33.3%
reduction in TP, and a 63.3% reduction in BOD of sources that are contributing
to exceedances of the criteria.
Notes
Rulemaking Authority 403.061, 403.067 FS. Law Implemented 403.061, 403.062, 403.067 FS.
New 11-11-10, Amended 9-9-12, 5-9-21.
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