reglab/statecodes huggingface dataset:
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.415 - Lower St. Johns River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Lower St. Johns River (freshwater segments from Buffalo Bluff to Black Creek).
				The TMDL for the freshwater segments of the Lower St. Johns River, which is
				that portion of the river from Buffalo Bluff to Black Creek, is 500, 325
				kilograms per year (kg/y) of TP and 8, 571, 563 kg/y of TN, and is allocated as
				follows:
(a) The WLA for point sources
				discharging to the freshwater portion of the river is 46, 357 kg/y of TP and
				236, 695 kg/y of TN; and
(b) The LA
				for nonpoint sources is 453, 968 kg/y of TP and 8, 334, 868 kg/y of
				TN.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.425 - Nassau River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Unnamed Branch. The bacteriological TMDL for Unnamed Branch is 400 counts/100
				mL for fecal coliform and is allocated as follows:
(2) 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 2003 to 2004
				period, will require a 46% reduction at sources contributing to exceedances of
				the criteria; and
(3) 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 2003 to 2004 period, will require a 46%
				reduction at sources contributing to exceedances of the
				criteria.
Rulemaking Authority
					 403.061,
					 403.067 FS. Law Implemented
					 403.031,
					 403.061,
					 403.062,
					 403.067
					 FS.
New 5-1-07, Amended
					 5-9-21.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.435 - Upper East Coast Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) Spruce
				Creek (Freshwater Segment). The bacteriological TMDL for the freshwater segment
				of Spruce Creek is 400 counts/100mL for fecal coliform, and is allocated as
				follows:
(a) 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 1997 to 2005
				period, will require a 53% reduction at sources contributing to exceedances of
				the criteria; and
(b) 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 1997 to 2005 period, will require a 53%
				reduction at sources contributing to exceedances of the
				criteria.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.500 - Ocklawaha River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Hatchet Creek. The Iron TMDL for Hatchet Creek is 35.91 pounds per day and is
				allocated as follows:
(a) The WLA for point
				sources discharging wastewater to Hatchet Creek is 5.6 pounds per day and for
				discharges subject to the Department's NPDES MS4 Permitting Program is a 30.8%
				reduction in current Iron loading; and
(b) The LA for nonpoint sources is a 30.8%
				reduction in current Iron loading.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.505 - Middle St. Johns River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Lake Jesup. The TMDL for Lake Jesup is 247.3 tons/year of TN and 19.0 tons/year
				of TP, and is allocated as follows:
(a) The
				WLA for wastewater point sources is not applicable;
(b) The WLA for discharges subject to the
				Department's NPDES MS4 Permitting Program is a 50% reduction of current TN
				loading and a 34% reduction of TP loading; and
(c) The LA for nonpoint sources is 247.3
				tons/year of TN and 19.0 tons/year of TP.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.506 - Wekiva Springs Study Area TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Wekiwa Spring. The TMDL for Wekiwa Spring is to achieve 0.286 mg/L
				nitrate-nitrite and 0.065 mg/L TP for the discharge from Wekiwa Spring, and is
				allocated as follows:
(a) The WLA for
				wastewater point sources is not applicable;
(b) The WLA for discharges subject to the
				Department's NPDES MS4 Permitting Program is a 79% reduction of nitrate-nitrite
				and a 64% reduction of TP based on data in the period from 1996 through 2006;
				and
(c) The LA for nonpoint sources
				is a 79% reduction of nitrate-nitrite and a 64% reduction of TP based on data
				in the period from 1996 through 2006.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.510 - Upper St. Johns River TMDLS

Current through Reg. 50, No. 138; July 16, 2024
(1) St.
				Johns River Above Lake Poinsett. The TMDL for TP is 89 tons per year, and is
				allocated as follows:
(a) The WLA for
				wastewater point sources is 0.023 tons per year of TP;
(b) The WLA for discharges subject to the
				Department's NPDES MS4 Permitting Program is a 37% reduction of current TP
				loading; and
(c) The LA for
				nonpoint sources is a 37% reduction of current TP loading.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.515 - Kissimmee River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) Lake
				Holden. The nutrient TMDL for Lake Holden is 148 lb/year of TP and 10, 526
				lb/year of TN, 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 a 74.0%
				reduction of TP based on the year 2000 landuse and a modeling period from 1996
				through 2000; and
(c) The LA for
				nonpoint sources is a 74.0% reduction of TP based on the year 2000 landuse and
				a modeling period from 1996 through 2000.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.520 - Indian River Lagoon Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Crane Creek. The bacteriological TMDL is an annual median of 1.23 x
				1011 colonies/day for fecal coliform, and is
				allocated as follows:
(a) The WLA for the
				Melbourne/Grant Street Wastewater Treatment Facility is 1.21 x
				1010 colonies/day. The WLA is only allowed during
				the maximum five-day Mechanical Integrity Test period, as defined in the
				Department permit;
(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 1999 through 2007 period, will require a 56% reduction at 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
				1999 through 2007 period, will require a 56% reduction at sources contributing
				to exceedances of the criteria.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.600 - Tampa Bay Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(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.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.605 - Alafia River TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) Thirty Mile
				Creek. The TMDL for Thirty Mile Creek (TML) is a monthly average TN
				concentration of 3.0 mg/L, and is allocated as follows:
(a) The WLA for discharges subject to the
				Department's NPDES Permitting Program is a monthly average TN concentration of
				3.0 mg/L; and
(b) The LA for
				nonpoint sources is an annual average TN concentration of 1.6
				mg/L.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.610 - Hillsborough River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Sparkman Branch. The bacteriological TMDL for Sparkman Branch is a median of
				6.52 x 108 colonies/day for fecal coliform, and is
				allocated as follows:
(a) The WLA for
				discharges subject to the Department's NPDES MS4 Permitting Program is a 59.3%
				reduction of current fecal coliform loading; and,
(b) The LA for nonpoint sources is a 59.3%
				reduction of current fecal coliform loading.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.615 - Manatee River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(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.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.620 - Little Manatee River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Little Manatee River. The bacteriological TMDL for Little Manatee River 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 79% 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 79% reduction of sources contributing to
				exceedances of the criteria.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.625 - Peace River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) Lake Cannon.
				The nutrient TMDL for Lake Cannon is an in-lake AGM concentration of 1.07 mg/L
				TN and 0.03 mg/L TP which are intended to achieve the applicable AGM
				chlorophyll a criterion for low color and high alkalinity lakes, 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 a 20% reduction of TN (calculated
				from 1.33 mg/L) and 0% reduction of TP, which is based on the highest AGM
				concentrations from the 2008 - 2016 period; and
(c) The LA for nonpoint sources is 20%
				reduction of TN (calculated from 1.33 mg/L) and 0% reduction of TP, which is
				based on the highest AGM concentration from the 2008 - 2016
				period.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.640 - Withlacoochee River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Rainbow Springs Group and Rainbow Springs Group Run. The nitrate-nitrite TMDL
				is an in-stream monthly mean concentration of 0.35 mg/L 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 nitrate-nitrite
				concentrations meet the TMDL target, which, based on the mean concentrations
				from the 2000-2010 period, will require a 82% reduction of nitrate-nitrite;
				and
(c) The LAs for nonpoint
				sources are to address anthropogenic sources in the basin such that in-stream
				nitrate-nitrite concentrations meet the TMDL target, which, based on the mean
				concentrations from the 2000-2011 period, will require a 82% reduction of
				nitrate-nitrite.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.645 - Springs Coast Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Klosterman Bayou Run Tidal Segment. The bacteriological TMDL for Klosterman
				Bayou Run is 400 counts/100 ml for fecal coliform, and is allocated as follows:
(a) 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, is a 52% reduction of current fecal coliform loading; and
(b) 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, is a 52% reduction of current fecal coliform
				loading.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.700 - Lake Okeechobee Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				The TMDL for TP for Lake Okeechobee shall be 140 metric tons, including
				atmospheric deposition. Attainment of the TMDL shall be calculated using a
				5-year rolling average of the monthly loads calculated from measured flow and
				concentration values.
(a) Implementation shall
				be in accordance with Section
				 373.4595, F.S.
(b) Management strategies shall be
				implemented in a phased approach.
(c) This TMDL shall be re-evaluated and, if
				appropriate, either increased or decreased through subsequent rulemaking as new
				research and data become available, but no later than 5 years from the
				effective date of this rule.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.705 - St. Lucie River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) St.
				Lucie Estuary (Lower & Middle Estuary). The TMDLs for the St. Lucie
				Estuary, based on data in the period from 1996 through 2005, are to achieve
				0.081 mg/L TP and 0.72 mg/L TN at Roosevelt Bridge and are allocated as
				follows:
(a) The WLA for wastewater sources
				is not applicable;
(b) The WLAs for
				discharges subject to the Department's NPDES MS4 Permitting Program are a 21.4%
				reduction of TN and a 41.3% reduction of TP; and
(c) The LAs for nonpoint sources are a 21.4%
				reduction of TN and a 41.3% reduction of TP.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.710 - Loxahatchee River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Southwest Fork Loxahatchee. The bacteriological TMDL for the Southwest Fork
				Loxahatchee is 43 counts/100mL for fecal coliform, and is allocated as
				follows:
(2) The WLA for the
				Loxahatchee Environmental Control District (Permit #FL0034649) is its NPDES
				permit conditions;
(3) 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 91% reduction of sources
				contributing to exceedances of the criteria; and
(4) 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 91% reduction of sources contributing to
				exceedances of the criteria.
Rulemaking Authority
					 403.061,
					 403.067 FS. Law Implemented
					 403.061,
					 403.062,
					 403.067
					 FS.
New 5-14-12, Amended
					 5-9-21.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.715 - Lake Worth Lagoon Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) E-1
				Canal. The bacteriological TMDL for E-1 Canal 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 concentration meets the fecal coliform
				criteria which, based on the measured concentrations from the 2003 to 2008
				period, will require a 94% 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 concentration meets the fecal coliform criteria which, based on the
				measured concentrations from the 2003 to 2008 period, will require a 94%
				reduction of sources contributing to exceedances of the
				criteria.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.725 - Southeast Coast Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) Wagner
				Creek. The bacteriological TMDL for Wagner Creek is 400 counts/100 mL, and is
				allocated as follows:
(a) 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 1997 to 2006 period, will require an 86% reduction at sources
				contributing to exceedances of the criteria;
(b) 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
				1997 to 2006 period, will require an 86% reduction at sources contributing to
				exceedances of the criteria.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.726 - Pompano Canal TMDL

Current through Reg. 50, No. 138; July 16, 2024
(1) Pompano Canal.
				The TMDL for the Pompano Canal is 11, 590.98 pounds per year (lbs/yr) of TN and
				923.66 pounds per year (lbs/yr) of TP, and is allocated as follows:
(2) There are no permitted NPDES wastewater
				discharges to the Pompano Canal. As such, the WLA for wastewater discharges is
				not applicable;
(3) The WLA for
				discharges subject to the Department's NPDES MS4 Permitting Program is a 15.8%
				reduction of current anthropogenic TN loading and a 13.6% reduction of current
				anthropogenic TP loading, based on measured concentrations from the 1999 to
				2002 time period; and
(4) The LA
				for nonpoint sources is a 15.8% reduction of current anthropogenic TN loading
				and a 13.6% reduction of current anthropogenic TP loading based, on measured
				concentrations from the 1999 to 2002 time period.
Rulemaking Authority
					 403.061,
					 403.067 FS. Law Implemented
					 403.061,
					 403.062,
					 403.067
					 FS.
New 6-3-08, Amended
					 5-9-21.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.735 - Everglades Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) West Palm Beach
				Canal. The bacteriological TMDL for the West Palm Beach Canal is 400
				counts/100mL for fecal coliform, and is allocated as follows:
(2) The WLA for wastewater sources is not
				applicable;
(3) The WLA for
				discharges subject to the Department's NPDES MS4 Permitting Program is not
				applicable; and
(4) 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 2005, 2006, and 2008, will require a 62% reduction
				of sources contributing to exceedances of the criteria.
Rulemaking Authority
					 403.061,
					 403.067 FS. Law Implemented
					 403.061,
					 403.062,
					 403.067
					 FS.
New 7-30-13, Amended
					 5-9-21.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.800 - Caloosahatchee River Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) Nine
				Mile Canal. The bacteriological TMDL for Nine Mile Canal is 400 counts/100 mL
				for fecal coliform, and is allocated as follows:
(a) The WLA for wastewater point 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 to result in a 36% reduction of
				in-stream fecal coliform concentrations, based on the measured concentrations
				from the 1997 to June 30, 2004 period; and
(c) The LA for nonpoint sources is a 36%
				reduction of in-stream fecal coliform concentrations, based on the measured
				concentrations from the 1997 to June 30, 2004 period.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.805 - Charlotte Harbor Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1) Coral
				Creek - East Branch. The TMDLs to address the low DO condition for Coral Creek
				- East Branch are 0.74 mg/L TN, 0.044 mg/L TP, and 2.0 mg/L five-day BOD, and
				are 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 to address anthropogenic sources in
				the basin such that in-stream concentrations meet the DO criteria, based on the
				measured concentrations from the January 2007 to December 2007 period, will
				require a 31% reduction of TN, a 36% reduction of TP, and a 33% reduction of
				BOD at 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
				DO criteria which, based on the measured concentrations from the January 2007
				to December 2007 period, will require a 31% reduction of TN, a 36% reduction of
				TP, and a 33% reduction of BOD at sources contributing to exceedances of the
				criteria.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.810 - Everglades West Coast Basin TMDLs

Current through Reg. 50, No. 138; July 16, 2024
(1)
				Hendry Creek Marine. Hendry Creek Marine. The bacteriological TMDL is 400
				counts/100 ml for fecal coliform, and is allocated as follows:
(a) The WLA for wastewater point 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 57.4% reduction at 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 57.4% reduction at sources contributing to
				exceedances of the criteria.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-304 - TOTAL MAXIMUM DAILY LOADS › Section 62-304.900 - Statewide TMDLs

Current through Reg. 50, No. 138; July 16, 2024
The statewide mercury (total) TMDL for all fresh and marine
				  waters in Florida is allocated as follows:
(1) The WLA for all industrial and domestic
				wastewater sources holding NPDES permits in Florida, other than those sources
				covered under subsection
				 62-304.900(2),
				F.A.C., is 23 kg/yr mercury (total). Pursuant to paragraph
				 62-620.100(3)(m),
				F.A.C., domestic wastewater facilities with a permitted capacity of greater
				than one million gallons per day and all industrial discharges, other than
				once-through cooling waters at industrial wastewater facilities and those
				sources covered under subsection
				 62-304.900(2),
				F.A.C., that demonstrate quantifiable mercury (total) levels in their effluent
				(using clean techniques, such as EPA Method 1631e) will be required to prepare
				and implement a mercury minimization plan addressing sources of mercury (total)
				within their jurisdiction;
(2) The
				WLA for discharges subject to the Department's NPDES MS4 Permitting Program or
				for other discharges primarily treating stormwater and not expected to add
				mercury (total) to their discharge, is generally not applicable; however, a
				permittee or co-permittee may be required to reduce mercury loads if sources of
				mercury (total) under the direct control of that permittee or co-permittee are
				found to exist; and
(3) The LA for
				nonpoint sources is to address anthropogenic sources in the basin is an 86%
				reduction of mercury (total) from atmospheric sources.
Rulemaking Authority
					 403.061,
					 403.067 FS. Law Implemented
					 403.061,
					 403.062,
					 403.067
					 FS.
New 6-7-13, Amended
					 5-9-21.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-305 - TOTAL MAXIMUM DAILY LOAD WATER QUALITY RESTORATION GRANTS › Section 62-305.100 - Scope of the Rule (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 201.15(8),
					 403.890(1)(b)
					 FS. Law Implemented 201.15(8),
					 403.890(1)(b)
					 FS.
New 10-29-08, Repealed
					 1-2-18.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-305 - TOTAL MAXIMUM DAILY LOAD WATER QUALITY RESTORATION GRANTS › Section 62-305.200 - Definitions (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 201.15(8),
					 403.890(1)(b)
					 FS. Law Implemented 201.15(8),
					 403.890(1)(b)
					 FS.
New 10-29-08, Repealed
					 1-2-18.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-305 - TOTAL MAXIMUM DAILY LOAD WATER QUALITY RESTORATION GRANTS › Section 62-305.300 - General Program Information (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 201.15(8),
					 403.890(1)(b)
					 FS. Law Implemented 201.15(8),
					 403.890(1)(b)
					 FS.
New 10-29-08, Repealed
					 1-2-18.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-305 - TOTAL MAXIMUM DAILY LOAD WATER QUALITY RESTORATION GRANTS › Section 62-305.400 - Project Selection Criteria (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 201.15(8),
					 403.890(1)(b)
					 FS. Law Implemented 201.15(8),
					 403.890(1)(b)
					 FS.
New 10-29-08, Repealed
					 1-2-18.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-305 - TOTAL MAXIMUM DAILY LOAD WATER QUALITY RESTORATION GRANTS › Section 62-305.900 - Forms (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 201.15(8),
					 403.890(1)(b)
					 FS. Law Implemented 201.15(8),
					 403.890(1)(b)
					 FS.
New 10-29-08, Repealed
					 2-23-12.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-306 - WATER QUALITY CREDIT TRADING › Section 62-306.100 - Scope and Intent

Current through Reg. 50, No. 138; July 16, 2024
(1) This chapter
				establishes the requirements for water quality credit trading between pollutant
				sources to reduce or eliminate nutrient or nutrient-related impairments
				pursuant to Section  403.067, F.S.
(2) The generation, registration, and trading
				of water quality credits provided for in this chapter are intended to provide
				flexibility among pollutant sources to meet the nutrient reduction requirements
				of an adopted Basin Management Action Plan (BMAP) or Reasonable Assurance Plan
				(RAP). Copies of BMAP and RAP documents may be obtained by writing to the
				Florida Department of Environmental Protection, 2600 Blair Stone Road, MS
				#3510, Tallahassee, FL 32399-2400.
(3) A BMAP provides for the implementation of
				Total Maximum Daily Loads (TMDL) adopted by the Department in Chapter 62-304,
				Florida Administrative Code (F.A.C.). A RAP, pursuant to Rule
				 62-303.600, F.A.C., provides for
				the restoration of impaired waters.
(4) This chapter does not address aggregation
				of wasteload allocations by an entity with multiple wastewater facilities,
				which may be implemented via an aggregate permit that limits the total
				allocated nutrient TMDL load for the entity.
(5) Nothing in this rule is intended to limit
				any actions by federal, state, or local agencies, affected persons, or citizens
				pursuant to other rules or regulations.
Rulemaking Authority
					 403.067(9) FS.
					 Law Implemented 403.067(8)-(10)
					 FS.
New 9-6-10, Amended
					 1-11-16.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-306 - WATER QUALITY CREDIT TRADING › Section 62-306.300 - General Requirements

Current through Reg. 50, No. 138; July 16, 2024
(1) Credits may
				be traded only within the boundaries of a BMAP or RAP, or within the boundaries
				of BMAPs or RAPs addressing hydrologically-connected waters, that includes
				detailed allocations to point sources and detailed or categorical allocations
				to nonpoint sources.
(2) Credits
				generated by a point source, other than an MS4, must be confirmed by effluent
				monitoring, which must be undertaken and provided to the Department throughout
				the life of the trade.
(3) Credits
				generated by a nonpoint source or an MS4 must be measured where treatment
				methods allow influent and effluent water quality to be measured or, where
				direct measurement cannot reasonably be accomplished, they may be estimated for
				the type of operation. When estimating credits for nonpoint source pollution
				control activities, the estimate shall be the long-term average expected
				reduction. If credits are estimated, the Department will use uncertainty
				factors, as applicable, to adjust the credits available for trading.
(4)
(a) An
				individually permitted wastewater facility that proposes to purchase or sell
				credits must obtain a new or revised Department permit to authorize the use or
				sale of such credits. The permit shall reflect the amount by which the
				permitted nutrient load has been adjusted by the purchase or sale of credits
				or, if no load was identified in the previous permit, the new or revised permit
				must reflect the new permitted load, the baseline load, and the basis for the
				load reduction associated with the trade.
(b) For trades not involving an entity
				required to obtain an individual wastewater permit, the Department shall
				authorize the use and sale of credits in a BMAP or RAP, which will reflect the
				baseline nutrient load and the basis for the nutrient load reduction associated
				with the credits.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-306 - WATER QUALITY CREDIT TRADING › Section 62-306.400 - Credit Eligibility

Current through Reg. 50, No. 138; July 16, 2024
(1) Activities that
				are potentially eligible to generate credits include, but are not limited to:
(a) Installation or modification of water
				pollution control equipment or activities that are not required to meet TBELs,
				WQBELs, or other pollution control obligations, and reduce nutrient loads below
				the baseline.
(b) Operational
				changes or the modification of a process or process equipment that reduce the
				quantity of water discharged through reuse, recycling, water conservation, or
				other measures and thereby reduce the load of nutrients discharged. Credits may
				be generated when a permitted surface water discharge facility closes its
				operations or ceases discharging to surface waters, but the credits shall only
				be valid while the permit remains in effect.
(c) Implementation of structural nonpoint
				source management controls.
(d)
				Installation, operation and maintenance of new drainage projects designed to
				treat stormwater.
(e)
				Implementation by agricultural operations of soil or water treatment
				technologies or water-quality enhancing production practices or systems that
				are confirmed in writing by DACS to reduce nutrient loads below the
				baseline.
(f) Other pollution
				controls, technologies or management practices with a demonstrated ability to
				reduce nutrient loads below the baseline established in a BMAP or
				RAP.
(g) A documented change in
				land use that goes beyond normal crop rotations or other standard agronomic
				practices that results in a reduction of nutrient loads below the baseline land
				use in the TMDL, BMAP or RAP.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-306 - WATER QUALITY CREDIT TRADING › Section 62-306.500 - Pre-Approval of Credit Generation

Current through Reg. 50, No. 138; July 16, 2024
(1) To
				obtain Department pre-approval of the number of credits expected to be
				generated from a project before executing an agreement on a water quality
				credit trade, the credit generator must submit information to the Department
				describing in detail the activities that will generate the credits and the
				expected nutrient load reduction below the generator's baseline. The credit
				generator must submit the information to the Department on a signed Form
				62-306(1), "Pre-Approval of Water Quality Credits Generated Form" effective
				December 2015 (
https://www.flrules.org/Gateway/reference.asp?No=Ref-06313
),
				which is adopted and incorporated by reference herein. Copies of the form may
				be obtained by writing to the Florida Department of Environmental Protection,
				2600 Blair Stone Road (MS #3510), Tallahassee, Florida 32399.
(2) The Department will notify the credit
				generator within thirty days of receipt of the signed form if the credit
				generator has not provided the information needed to determine how many credits
				are expected to be generated. After the credit generator provides all of the
				required information, the Department will timely notify the credit generator of
				the maximum number of credits that could potentially be authorized for the
				project. The Department will determine the number of credits expected to be
				generated from the activities in accordance with this chapter. The number of
				credits generated and approved may be modified by the Department if the project
				specifications are altered between the date of pre-approval issuance and the
				actual generation of credits. The number of credits needed for a given trade
				will be dependent on the specific circumstances of the trade, including the
				location of the buyer of the credits.
Rulemaking Authority
					 403.067(9) FS.
					 Law Implemented 403.067(8)-(10)
					 FS.
New 9-6-10, Amended
					 1-11-16.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-306 - WATER QUALITY CREDIT TRADING › Section 62-306.700 - Water Quality Credit Availability and Trade Tracking

Current through Reg. 50, No. 138; July 16, 2024
(1) The Department shall track all credit
				generation pre-approvals and all credits traded, and shall post the information
				on its website.
(2) Information
				tracked related to credits and trades will include, at a minimum:
(a) The names and street addresses of all
				parties, locations of discharges, receiving water (WBID), and the nutrient
				involved;
(b) The generator's
				baseline and the amount of credits generated;
(c) A description of the actions that
				generated credits and whether the credits are measured or estimated;
(d) The date when credits will initially be
				generated and applied under the trade, and the effective period of the
				credits;
(e) The amount of credits
				traded and any adjustments for location or uncertainty;
(f) The unit price of the credits, including
				the amount of any state funding used to generate the credits; and,
(g) The date of the most recent inspection by
				DACS or the Department to verify implementation of activities generating
				estimated credits.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-306 - WATER QUALITY CREDIT TRADING › Section 62-306.800 - Compliance with Trade Provisions

Current through Reg. 50, No. 138; July 16, 2024
(1)
				The seller shall certify and document to the Department annually during the
				life of the trade that the control devices and systems, technologies, BMPs,
				land use changes, or other actions on which the credits are based, continue to
				be fully implemented and properly operated and maintained throughout the life
				of the trade, and for measured credits, that nutrient load reductions below the
				baseline continue to be achieved at the authorized level.
(2) If the credits traded are measured
				credits, the seller shall report to the Department the quantity of the Total
				Nitrogen or Total Phosphorus discharged on a monthly basis to demonstrate
				fulfillment of the nutrient load reduction resulting in credits. If applicable,
				a permittee may use the precoded Discharge Monitoring Report form provided by
				the permitting office to the permit holder at the time of permit issuance to
				report the amount of Total Nitrogen or Total Phosphorus discharged.
(3) If the credits traded are estimated
				credits, the seller shall report to the Department quarterly providing the
				following information:
(a) The name and
				location of the activity generating the credits;
(b) The pollutants controlled;
(c) The BMPs implemented or, in the case of
				concentrated animal feeding operations, the activities conducted under a
				comprehensive nutrient management plan;
(d) The control devices installed and date
				completed, and information on their proper operation and maintenance;
(e) The linear feet or acres for which BMPs
				or other management measures or controls have been completed; and,
(f) A calculation of the quantity of each
				pollutant controlled using the same methods and procedures used to determine
				the load reductions and credits.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-307 - BEST MANAGEMENT PRACTICES WATER QUALITY MONITORING › Section 62-307.100 - Definitions

Current through Reg. 50, No. 138; July 16, 2024
As used in this chapter:
(1) "Department" means the Department of
				Environmental Protection.
(2)
				"Nonpoint source discharger" means either a) the person responsible for the
				nonpoint source discharge, or b) the owner of the property from which the
				nonpoint source discharge originates.
(3) "BMAP" means an adopted basin management
				action plan (BMAP) that implements a total maximum daily load (TMDL).
(4) "Person" has the same meaning as provided
				in section  403.031, F.S.
(5) "Sampling and analysis plan" means the
				monitoring plan required by this chapter.
Rulemaking Authority
					 403.067 FS. Law Implemented
					 403.067
					 FS.
New 7-1-18.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-307 - BEST MANAGEMENT PRACTICES WATER QUALITY MONITORING › Section 62-307.200 - Water Quality Monitoring In Lieu of Implementing BMPs

Current through Reg. 50, No. 138; July 16, 2024
(1) A nonpoint source discharger, whose
				discharge is located within a BMAP, must either submit a notice of intent to
				implement appropriate BMPs adopted in accordance with section
				 403.067(7)(c),
				F.S., or conduct water quality monitoring to demonstrate compliance with the
				water quality criteria for the parameters addressed by the BMAP.
(2) Within 180 days of the initial adoption
				of a BMAP or the effective date of this rule, whichever is later, a nonpoint
				source discharger choosing to conduct water quality monitoring in lieu of
				implementing BMPs pursuant to subsection (1), shall submit for Department
				approval a water quality sampling and analysis plan that meets all the
				requirements of this rule and chapter 62-160, F.A.C.
(3) A sampling and analysis plan shall
				include the following components:
(a) A
				description of the physical and hydrogeological characteristics of the property
				and the surrounding area, including, as applicable:
1. The direction and rate of surface water
				and groundwater flow;
2. Vertical
				permeability, thickness, competence, and extent of any confining
				beds;
3. Topography, soil
				information, and surface water drainage systems surrounding the site;
4. Identification and location of wells,
				surface water discharge points, and surface water intakes within 500 feet of
				the property and within the property boundary; and
5. The locations of all surface waters and
				their classifications including springs within one quarter mile of the
				property, and onsite sinkholes with depths exceeding the seasonal high water
				table or that are perched;
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-307 - BEST MANAGEMENT PRACTICES WATER QUALITY MONITORING › Section 62-307.300 - Implementation Procedures

Current through Reg. 50, No. 138; July 16, 2024
(1) As provided in
				an approved sampling and analysis plan, a nonpoint source discharger must
				ensure that water samples are taken at the frequency at all locations set forth
				in the approved sampling and analysis plan.
(2) The collected water samples must be
				tested in accordance with the approved sampling and analysis plan.
(3) Sample collection and analytical test
				methods on the collected samples shall be conducted in accordance with chapter
				62-160, F.A.C.
(4) Monitoring
				records must be retained onsite for at least 5 years and be made available for
				inspection upon request.
(5) The
				nonpoint source discharger shall submit an annual report to the Department
				consistent with an approved sampling and analysis plan. The annual report must
				include all the laboratory analytical test results on the water samples
				taken.
(6) The Department shall
				verify implementation of nonagricultural nonpoint source BMPs required by
				section  403.067(7),
				F.S., by inspection or other appropriate compliance mechanisms.
(7) The Department shall have all remedies
				available to it under Florida law, including those in Sections
				 403.121,
				 403.141, and
				 403.161, F.S., to enforce
				compliance with this rule chapter or section
				 403.067(7)(c),
				F.S.
Rulemaking Authority
					 403.067 FS. Law Implemented
					 403.067
					 FS.
New 7-1-18.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-312 - DREDGE AND FILL ACTIVITIES › Section 62-312.010 - Scope of Part I (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 373.414(11)-(16),
					 373.4145,
					 403.805(1) FS.
					 Law Implemented 373.409,
					 373.413,
					 373.414(9), (11), (12)(a), (13), (14), (15),
					 (16),
					 373.4145,
					 373.416,
					 373.418,
					 403.061,
					 403.813,
					 403.814
					 FS.
New 12-10-84, Amended 8-7-85, Formerly 17-12.010,
					 17-312.010, Amended 10-3-95, Repealed
					 2-16-12.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-312 - DREDGE AND FILL ACTIVITIES › Section 62-312.020 - Definitions (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 373.414(11)-(16),
					 373.4145,
					 403.805(1) FS.
					 Law Implemented 373.414(11)-(16),
					 373.4145,
					 403.031,
					 403.061,
					 403.803,
					 403.911,
					 403.912
					 FS.
New 12-10-84, Amended 8-30-88, 3-26-89, Formerly 17-12.020,
					 Amended 11-16-92, Formerly 17-312.020, Repealed
					 2-16-12.
Florida Administrative Code › 62 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 62 - Departmental › Chapter 62-312 - DREDGE AND FILL ACTIVITIES › Section 62-312.030 - Jurisdiction (Repealed)

Current through Reg. 50, No. 138; July 16, 2024
Rulemaking Authority
					 373.414(11)-(16),
					 373.4145,
					 403.805(1) FS.
					 Law Implemented 373.414(11)-(16),
					 373.4145,
					 403.031,
					 403.061,
					 403.813,
					 403.817,
					 373.414
					 FS.
New 12-10-84, Amended 3-26-89, Formerly 17-12.030, Amended
					 12-7-93, Formerly 17-312.030, Amended 8-7-95, Repealed
					 2-16-12.