Updated: August 04, 2021


Please note this analysis is for informational purposes only and subject to change.

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S-79 lock. *Source: Leah Reidenbach, SCCF*.

S-79 lock. Source: Leah Reidenbach, SCCF.

Basin Information

The Caloosahatchee Basin in its entirity encompassess aproximately 860 thousand acres (3,470 square kilometers) across three counties (Lee, Hendry and Glades). The Florida Department of Environmental Protection (FDEP) has divided the Caloosahatchee basin into five planning units: East Caloosahatchee, West Caloosahatchee, Orange River, Telegraph Swamp and Caloosahatchee Estuary (Figure 1; Bailey et al. 2009). East and West Caloosahatchee are located upstream of the S-79 structure (see map below) between the S-79 and S-77 (Lake Okeechobee). Meanwhile the Orange River, Telegraph Swamp, and the Caloosahatchee Estuary planning units are located downstream of the S-79 (Figure 2). Each planning unit is composed of a series of sub-basins idenified with waterbody idenfication numbers (WBIDs). All of these sub-basins except for one are classified as Class III (Designated use: fishable and swimmable) water bodies. The exception is the Class I (Designated use: drinking water) sub-basin immediately upstream of the S-79 structure (WBID: 3235A) which extends to the Lee-Hendry county line.

Figure 1: Interactive map indicating Caloosahatchee River basins planning units.

Water Quality Impairments

Water quality impairments in the Tidal Caloosahathcee River and Tributaries were verified as an impaired waterbody due to low Dissolved Oxygen (DO) and high chlorophyll-a (Chl-a) presumably caused by high total nitrogen (TN), total phosphorus (TP) or biochemical oxygen demand (i.e. causative pollutants) concentrations determined during the Cycle 1 assessment (2005) (Table 1). Since this inital assessment, these basins have been verified as impaired for un-ionized ammonia (WBID 3240A) and iron (WBIDs 3240B and 3240C) Verified List. Since the Cycle 1, Cylce 2 and Cycle 3 impairment verification assessments and the establishment of the Total Maximum Daily Load (TMDL), estuary numeric nutrient criteria have also been developed specifically for this estuary (62-302.532(1)(d) Florida Administrative Code (FAC), Table 2 below). An interactive map for all FDEP adopted numeric nutrient criteria can be found at this link.


Table 1: Verified impaired parameters identified during Cycle 1 Impaired Water Rule assessment by FDEP in 2005 for Tidal Caloosahatchee addressed in the 2009 Total Maximum Daily Load (TMDL; Bailey et al. 2009).
WBID Waterbody Segment
Waterbody
Type
Parameters
Identified
Concentration
Causing
Impairment
3240A Tidal Caloosahatchee (Lower) Estuary (III) Nutrients (Chl-a) Median TN = 0.83mg L¹
3240B Tidal Caloosahatchee (Middle) Estuary (III) Nutrients (Chl-a) Median TN = 0.85mg L¹
3240C Tidal Caloosahatchee (Upper) Stream (III) Nutrients (Chl-a) Median TN = 1.105mg L¹
Note:
1 Cycle 1 verification period includes data from January 1, 1997 through June 30, 2004.



Table 2: Estuary numeric nutrient criteria for the Caloosahatchee River Estuary as identified by 62-302.532(1)(d).
Estuary/Segment
Total Phosphorous
(mg L⁻¹) ᵃ
Total Nitrogen
Chlorphyll-A
(μg L⁻¹) ᵃ
Upper Caloosahatchee River Estuary 0.086 See 62-304.800(2) FAC 4.2
Middle Caloosahatchee River Estuary 0.055 See 62-304.800(2) FAC 6.5
Lower Caloosahatchee River Estuary 0.040 See 62-304.800(2) FAC 5.6
Note:
a As Long-Term (5-Yr) average.
b 62-304.800(2)
* This information is up-to-date as of April 2019 and is subject to change pending revisions to Florida Administrative Code.
For the most up-to-date information please follow this link.



Figure 2: Interactive map of monitored locations within Caloosahatchee River Estuary (CRE) relative to sub-basin/Water Body Identification (WBIDs).

Water Quality Data

Presented below is grab sample water quality data (collected approximately monthly) retrieved from the South Florida Water Management online environmental database (DBHYDRO). Data presented includes total phosphorus (TP), total nitrogen (TN), chlorophyll-A (Chl-A), dissolved oxygen (DO) and salinity. The top row of plots show individual samples collected across a period of record. The bottom row of plots depict annually average data based on the Florida water (May to April), TP, TN and Chl-A are expressed as geometric mean (GM) concentrations while DO and salinity are expressed as arithmetic mean concentration. In addition to annual GM concentration a five-WY mean is also shown for TP, TN and Chl-A. The dissolved oxygen water quality standard (WQS) is identified for each station and a determination of achievement or exceedance of the WQS for each year is identified. Dissolved Oxygen WQS evaluation is consistent with 62-302.533 FAC and the associated technical support document.

Each tab presented data from sites along the Caloosahatchee River Estuary including the S-79.

CES08

WBID: 3240A (Lower Caloosahatchee River Estuary)

CES07

WBID: 3240A (Lower Caloosahatchee River Estuary)

CES06

WBID: 3240A (Lower Caloosahatchee River Estuary)

CES05

WBID: 3240A (Lower Caloosahatchee River Estuary)

CES04

WBID: 3240B (Middle Caloosahatchee River Estuary)

CES03

WBID: 3240C (Upper Caloosahatchee River Estuary)

CES02

WBID: 3240C (Upper Caloosahatchee River Estuary)

S79

WBID: 3240C (Upper Caloosahatchee River Estuary)


Reference

  • Bailey, N., W. Magley, J. Mandrup-Poulsen, K O’Donnell, R. Peets (2009) Final TMDL Report. Nutrient TMDL for the Caloosahatchee Estuary (WBIDs 3240A, 3240B and 3240C). Florida Department of Environmental Protection. Tallahassee, Florida. pdf link.
 

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