Short-Term Recommendations 1. the Final Phase of the Kissimmee River
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St. Lucie and Indian River Counties Water Resources Study
St. Lucie and Indian River Counties Water Resources Study Final Summary Report November 2009 Prepared for: South Florida Water Management District St. Johns River Water Management District St Lucie and Indian River Counties Water Resource Study St Lucie and Indian River Counties Water Resources Study Executive Summary Study Purpose The purpose of this study was to evaluate the potential for capturing excess water that is currently being discharged to the Indian River Lagoon in northern St. Lucie County and southern Indian River County and making it available for beneficial uses. The study also evaluated the reconnection of the C-25 Basin in the South Florida Water Management District (SFWMD) and C-52 in the St. Johns River Water Management District (SJRWMD) so that available water supplies could be conveyed to meet demands across jurisdictional boundaries. The study objectives were to: Identify the quantity and timing of water available for diversion and storage; Identify water quality information needed to size water quality improvement facilities; Identify and provide cost estimates for the improvements and modifications to the existing conveyance systems necessary for excess runoff diversion and storage; Identify, develop cost estimates, and evaluate conceptual alternatives for storing excess runoff, and Provide conceptual designs and cost estimates for the highest ranked alternative in support of feasibility analysis and a future Basis of Design Report. Study Process The study process consisted of the following activities: Data compilation and analysis, Identification of alternative plans, Evaluation of alternative plans, Identification of the preferred plan, and Development of an implementation strategy. St Lucie and Indian River Counties Water Resource Study Formal stakeholder meetings were conducted throughout the study. -
Stormwater Management Master Plan Updates There Are 16 Defined
Stormwater Management Master Plan Updates There are 16 defined watersheds in Volusia County. Stormwater Management Master Plans (SWMP) have been prepared for the 11 of the watersheds, with the concentration on the urbanized basins. Many of these SWMPs were prepared in the 90’s and are currently over 20 years old. These plans need to be updated to address current corporate boundaries and responsibilities and to address current priorities. The SWMP updates proposed are for the Indian River Lagoon, the Halifax River, the Tomoka River and Spruce Creek. The studies will update the stormwater system improvements in these watersheds and analyze for water quantity and water quality impacts to the receiving water bodies, each of which is an impaired water body. Current Situation The Indian River Lagoon, Halifax River, Tomoka River and Spruce Creek SWMPs were completed in the 90s prior to the cities in these areas completing SWMPs. Each of these basins is an impaired water body with Total Maximum Daily Loads (TMDL) established. A Basin Management Action Plan (BMAP) has been completed for the Indian River Lagoon and the BMAP process has begun for the Halifax River (Northern Coastal Basin). Future BMAPs are scheduled for the Tomoka River and Spruce Creek basins. The goal of the SWMP Updates is to review and update Volusia County’s previous SWMPs with a focus on water quality and projects that serve areas within unincorporated Volusia County. Project The preparation of a Stormwater Management Master Plan Update for these watersheds will include: A review of previous SWMPs to determine if capital projects recommended at that time may still be recommended for grant applications An evaluation of potential water quality benefits resulting from altering or increasing stormwater maintenance practices An evaluation of water quality conditions to propose additional improvement alternatives and quantify resultant pollutant load reductions The majority of the land uses in these basins is urban and fall within city limits. -
North Fork of the St. Lucie River Floodplain Vegetation Technical Report
NORTH FORK ST. LUCIE RIVER FLOODPLAIN VEGETATION TECHNICAL REPORT WR-2015-005 Coastal Ecosystem Section Applied Sciences Bureau Water Resources Division South Florida Water Management District Final Report July 2015 i Resources Division North Fork of the St. Lucie River Floodplain Vegetation Technical Report ACKNOWLEDGEMENTS This document is the result of a cooperative effort between the Coastal Ecosystems Section of South Florida Water Management District (SFWMD) and the Florida Department of Environmental Protection (FDEP), Florida Park Service (FPS) at the Savannas Preserve State Park in Jensen Beach, Florida and the Indian River Lagoon Aquatic Preserve Office in Fort Pierce, Florida. The principle author of this document was as follows: Marion Hedgepeth SFWMD The following staff contributed to the completion of this report: Cecilia Conrad SFWMD (retired) Jason Godin SFWMD Detong Sun SFWMD Yongshan Wan SFWMD We would like to acknowledge the contributions of Christine Lockhart of Habitat Specialist Inc. with regards to the pre-vegetation plant survey, reference collection established for this project, and for her assistance with plant identifications. We are especially grateful to Christopher Vandello of the Savannas Preserve State Park and Laura Herren and Brian Sharpe of the FDEP Indian River Lagoon Aquatic Preserves Office for their assistance in establishing the vegetation transects and conducting the field studies. And, we would like to recognize other field assistance from Mayra Ashton, Barbara Welch, and Caroline Hanes of SFWMD. Also, we would like to thank Kin Chuirazzi for performing a technical review of the document. ii North Fork of the St. Lucie River Floodplain Vegetation Technical Report TABLE OF CONTENTS Acknowledgements ..........................................................................................................................ii List of Tables ............................................................................................................................... -
The Caloosahatchee River Estuary: a Monitoring Partnership Between Federal, State, and Local Governments, 2007–13
Prepared in cooperation with the Florida Department of Environmental Protection and the South Florida Water Management District The Caloosahatchee River Estuary: A Monitoring Partnership Between Federal, State, and Local Governments, 2007–13 By Eduardo Patino The tidal Caloosahatchee River and downstream estuaries also known as S–79 (fig. 2), which are operated by the USGS (fig. 1) have substantial environmental, recreational, and economic in cooperation with the U.S. Army Corps of Engineers, Lee value for southwest Florida residents and visitors. Modifications to County, and the City of Cape Coral. Additionally, a monitor- the Caloosahatchee River watershed have altered the predevelop- ing station was operated on Sanibel Island from 2010 to 2013 ment hydrology, thereby threatening the environmental health of (fig. 1) as part of the USGS Greater Everglades Priority Eco- estuaries in the area (South Florida Water Management District, system Science initiative and in partnership with U.S. Fish and 2014). Hydrologic monitoring of the freshwater contributions from Wildlife Service (J.N. Ding Darling National Wildlife Ref- tributaries to the tidal Caloosahatchee River and its estuaries is uge). Moving boat water-quality surveys throughout the tidal necessary to adequately describe the total freshwater inflow and Caloosahatchee River and downstream estuaries began in 2011 constituent loads to the delicate estuarine system. and are ongoing. Information generated by these monitoring From 2007 to 2013, the U.S. Geological Survey (USGS), in networks has proved valuable to the FDEP for developing total cooperation with the Florida Department of Environmental Protec- maximum daily load criteria, and to the SFWMD for calibrat- tion (FDEP) and the South Florida Water Management District ing and verifying a hydrodynamic model. -
Collier Miami-Dade Palm Beach Hendry Broward Glades St
Florida Fish and Wildlife Conservation Commission F L O R ID A 'S T U R N P IK E er iv R ee m Lakewood Park m !( si is O K L D INDRIO ROAD INDRIO RD D H I N COUNTY BCHS Y X I L A I E O W L H H O W G Y R I D H UCIE BLVD ST L / S FT PRCE ILT SRA N [h G Fort Pierce Inlet E 4 F N [h I 8 F AVE "Q" [h [h A K A V R PELICAN YACHT CLUB D E . FORT PIERCE CITY MARINA [h NGE AVE . OKEECHOBEE RA D O KISSIMMEE RIVER PUA NE 224 ST / CR 68 D R !( A D Fort Pierce E RD. OS O H PIC R V R T I L A N N A M T E W S H N T A E 3 O 9 K C A R-6 A 8 O / 1 N K 0 N C 6 W C W R 6 - HICKORY HAMMOCK WMA - K O R S 1 R L S 6 R N A E 0 E Lake T B P U Y H D A K D R is R /NW 160TH E si 68 ST. O m R H C A me MIDWAY RD. e D Ri Jernigans Pond Palm Lake FMA ver HUTCHINSON ISL . O VE S A t C . T I IA EASY S N E N L I u D A N.E. 120 ST G c I N R i A I e D South N U R V R S R iv I 9 I V 8 FLOR e V ESTA DR r E ST. -
Chapter 8C: St. Lucie and Caloosahatchee River Watersheds Annual Report
2019 South Florida Environmental Report – Volume I Chapter 8C Chapter 8C: St. Lucie and Caloosahatchee River Watersheds Annual Report Cassondra Armstrong, Fawen Zheng, Anna Wachnicka, Amanda Khan, Zhiqiang Chen, and Lucia Baldwin SUMMARY A description of the estuaries and the river watersheds is followed by a summary of the conditions of the hydrology (rainfall and flow), water quality (salinity, phosphorus, nitrogen, and chlorophyll a [Chla]), and aquatic habitat (oysters and submerged aquatic vegetation [SAV]) based on results of the Research and Water Quality Monitoring Programs (RWQMPs). Following the summary for each estuary, significant findings during the Water Year 2018 (WY2018; May 1, 2017–April 30, 2018) reporting period are highlighted. In addition, the St. Lucie and Caloosahatchee river watersheds’ water quality monitoring results for total phosphorus (TP) and total nitrogen (TN) by basin are presented in Appendix 8C-1 of this volume as supplemental information. ST. LUCIE ESTUARY WY2018 total annual rainfall across the Tier 1 Contributing Areas (Lake Okeechobee, St. Lucie Basin, and Tidal Basin) to the St. Lucie Estuary (SLE) was more than the long-term average from WY1997 through WY2018. Although 74% of the annual rainfall usually occurs in the wet season, this value increased to 80% in WY2018. The relatively high amount of wet season rain was the driver for increased discharge to the SLE. The total annual freshwater inflow to the SLE in WY2018 (1.6 million acre-feet [ac-ft]) was higher than the long-term average of 1.0 million ac-ft. The inflow and percent contribution from Lake Okeechobee in WY2018 (0.6 million ac-ft and 37%, respectively) were greater than the long-term averages (0.3 million ac-ft and 26%, respectively). -
An Historical Perspective on the Kissimmee River Restoration Project
ing of 14 km of river channel, and removal of two water An Historical control structures and associated levees. Restoration of the Kissimmee River ecosystem will result in the reestablish ment of 104 km2 of river-floodplain ecosystem, including Perspective on the 70 km of river channel and 11,000 ha of wetland habitat, which is expected to benefit over 320 species of fish and Kissimmee River wildlife. Restoration Project Background he Kissimmee River basin is located in central Florida Tbetween the city of Orlando and lake Okeechobee Joseph W. Koebel, Jr.1 within the Coastal Lowlands physiographic province. It con sists of a 4229-km2 upper basin, which includes Lake Kis Abstract simmee and 18 smaller lakes ranging in size from a few hec tares to 144 km2, and a 1,963-km2 lower basin, which This paper reviews the events leading to the channeliza includes the tributary watersheds (excluding Lake Istok tion of the Kissimmee River, the physical, hydrologic, and poga) of the Kissimmee River between lake Kissimmee and biological effects of channelization, and the restoration lake Okeechobee. The physiography of the region includes movement. Between 1962 and 1971, in order to provide the Osceola and Okeechobee Plains and the Lake Wales flood control for central and southern florida, the 166 ridge of the Wicomico shore (U.S. Army Corps of Engineers km-Iong meandering Kissimmee River was transformed 1992). into a 90 km-Iong, 10 meter-deep, 100 meter-wide canal. Prior to channelization, the Kissimmee River meandered Channelization and transformation of the Kissimmee River approximately 166 km within a 1.5-3-km-wide floodplain. -
LOWRP Draft PIR/EIS Annex C
COMPREHENSIVE EVERGLADES RESTORATION PLAN LAKE OKEECHOBEE WATERSHED RESTORATION PROJECT DRAFT INTEGRATED PROJECT IMPLEMENTATION REPORT AND ENVIRONMENTAL IMPACT STATEMENT July 2018 Annex C Annex C Draft Project Operating Manual ANNEX C DRAFT PROJECT OPERATING MANUAL LOWRP Draft PIR and EIS July 2018 Annex C-i Annex C Draft Project Operating Manual This page intentionally left blank. LOWRP Draft PIR and EIS July 2018 Annex C-ii Annex C Draft Project Operating Manual Table of Contents C DRAFT PROJECT OPERATING MANUAL .................................................................... C-1 C.1 General Project Purposes, Goals, Objectives, and Benefits ................................... C-1 C.2 Project Features .................................................................................................. C-1 C.2.1 Existing Features ..................................................................................... C-2 C.2.2 Proposed Features .................................................................................. C-3 C.3 Project Relationships ........................................................................................... C-6 C.4 Major Constraints ................................................................................................ C-7 C.4.1 Paradise run ............................................................................................ C-8 C.4.2 Existing Legal Users, Levels of Flood Damage Reduction, and Water Quality ................................................................................................... -
Environmental Plan for Kissimmee Okeechobee Everglades Tributaries (EPKOET)
Environmental Plan for Kissimmee Okeechobee Everglades Tributaries (EPKOET) Stephanie Bazan, Larissa Gaul, Vanessa Huber, Nicole Paladino, Emily Tulsky April 29, 2020 TABLE OF CONTENTS 1. BACKGROUND AND HISTORY…………………...………………………………………..4 2. MISSION STATEMENT…………………………………....…………………………………7 3. GOVERNANCE……………………………………………………………………...………...8 4. FEDERAL, STATE, AND LOCAL POLICIES…………………………………………..…..10 5. PROBLEMS AND GOALS…..……………………………………………………………....12 6. SCHEDULE…………………………………....……………………………………………...17 7. CONCLUSIONS AND RECOMMENDATIONS…………………………………………....17 REFERENCES…………………………………………………………..……………………....18 2 LIST OF FIGURES Figure A. Map of the Kissimmee Okeechobee Everglades Watershed…………………………...4 Figure B. Phosphorus levels surrounding the Kissimmee Okeechobee Everglades Watershed…..5 Figure C. Before and after backfilling of the Kissimmee river C-38 canal……………………….6 Figure D. Algae bloom along the St. Lucie River………………………………………………...7 Figure E. Florida’s Five Water Management Districts………………………………………........8 Figure F. Three main aquifer systems in southern Florida……………………………………....14 Figure G. Effect of levees on the watershed………………………………………...…………...15 Figure H. Algal bloom in the KOE watershed…………………………………………...………15 Figure I: Canal systems south of Lake Okeechobee……………………………………………..16 LIST OF TABLES Table 1. Primary Problems in the Kissimmee Okeechobee Everglades watershed……………...13 Table 2: Schedule for EPKOET……………………………………………………………….…18 3 1. BACKGROUND AND HISTORY The Kissimmee Okeechobee Everglades watershed is an area of about -
Joint Public Workshop for Minimum Flows and Levels Priority Lists and Schedules for the CFWI Area
Joint Public Workshop for Minimum Flows and Levels Priority Lists and Schedules for the CFWI Area St. Johns River Water Management District (SJRWMD) Southwest Florida Water Management District (SWFWMD) South Florida Water Management District (SFWMD) September 5, 2019 St. Cloud, Florida 1 Agenda 1. Introductions and Background……... Don Medellin, SFWMD 2. SJRWMD MFLs Priority List……Andrew Sutherland, SJRWMD 3. SWFWMD MFLs Priority List..Doug Leeper, SWFWMD 4. SFWMD MFLs Priority List……Don Medellin, SFWMD 5. Stakeholder comments 6. Adjourn 2 Statutory Directive for MFLs Water management districts or DEP must establish MFLs that set the limit or level… “…at which further withdrawals would be significantly harmful to the water resources or ecology of the area.” Section 373.042(1), Florida Statutes 3 Statutory Directive for Reservations Water management districts may… “…reserve from use by permit applicants, water in such locations and quantities, and for such seasons of the year, as in its judgment may be required for the protection of fish and wildlife or the public health and safety.” Section 373.223(4), Florida Statutes 4 District Priority Lists and Schedules Meet Statutory and Rule Requirements ▪ Prioritization is based on the importance of waters to the State or region, and the existence of or potential for significant harm ▪ Includes waters experiencing or reasonably expected to experience adverse impacts ▪ MFLs the districts will voluntarily subject to independent scientific peer review are identified ▪ Proposed reservations are identified ▪ Listed water bodies that have the potential to be affected by withdrawals in an adjacent water management district are identified 5 2019 Draft Priority List and Schedule ▪ Annual priority list and schedule required by statute for each district ▪ Presented to respective District Governing Boards for approval ▪ Submitted to DEP for review by Nov. -
Caloosahatchee
FLORIDA DEPARTMENT OF ENVIRONMENTAL PROTECTION Division of Water Resource Management SOUTH DISTRICT • GROUP 3 BASIN • 2005 Water Quality Assessment Report Caloosahatchee FLORIDA DEPARTMENT OF ENVIRONMENTAL PROTECTION Division of Water Resource Management 2005 Water Quality Assessment Report Caloosahatchee Water Quality Assessment Report: Caloosahatchee 5 Acknowledgments The Caloosahatchee Water Quality Assessment Report was prepared by the Caloosahatchee Basin Team, Florida Department of Environmental Protection, as part of a five-year cycle to restore and protect Florida’s water quality. Team members include the following: Pat Fricano, Basin Coordinator T. S. Wu, Ph.D., P.E., Assessment Coordinator Gordon Romeis, South District Karen Bickford, South District Robert Perlowski, Watershed Assessment Section Dave Tyler, Watershed Assessment Section Ron Hughes, GIS James Dobson, Groundwater Section Janet Klemm, Water Quality Standards and OFWs Editorial and writing assistance provided by Linda Lord, Watershed Planning and Coordination Production assistance provided by Center for Information, Training, and Evaluation Services Florida State University 210 Sliger Building 2035 E. Dirac Dr. Tallahassee, FL 32306-2800 Map production assistance provided by Florida Resources and Environmental Analysis Center Florida State University University Center, C2200 Tallahassee, FL 32306-2641 For additional information on the watershed management approach and impaired waters in the Caloosahatchee Basin, contact Pat Fricano Florida Department of Environmental Protection Bureau of Watershed Management, Watershed Planning and Coordination Section 2600 Blair Stone Road, Mail Station 3565 Tallahassee, FL 32399-2400 [email protected].fl.us Phone: (850) 245-8559; SunCom: 205-8559 Fax: (850) 245-8434 6 Water Quality Assessment Report: Caloosahatchee Access to all data used in the development of this report can be obtained by contacting T.S. -
Distribution and Habitat Partitioning of Immature Bull Sharks (Carcharhinus Leucas) in a Southwest Florida Estuary
Estuaries Vol. 28, No. 1, p. 78±85 February 2005 Distribution and Habitat Partitioning of Immature Bull Sharks (Carcharhinus leucas) in a Southwest Florida Estuary COLIN A. SIMPFENDORFER*, GARIN G. FREITAS,TONYA R. WILEY, and MICHELLE R. HEUPEL Mote Marine Laboratory, 1600 Ken Thompson Parkway, Sarasota, Florida 34236 ABSTRACT: The distribution and salinity preference of immature bull sharks (Carcharhinus leucas) were examined based on the results of longline surveys in three adjacent estuarine habitats in southwest Florida: the Caloosahatchee River, San Carlos Bay, and Pine Island Sound. Mean sizes were signi®cantly different between each of these areas indicating the occurrence of size-based habitat partitioning. Neonate and young-of-the-year animals occurred in the Caloosahatchee River and juveniles older than 1 year occurred in the adjacent embayments. Habitat partitioning may reduce intraspeci®c predation risk and increase survival of young animals. Classi®cation tree analysis showed that both temperature and salinity were important factors in determining the occurrence and catch per unit effort (CPUE) of immature C. leucas. The CPUE of ,1 year old C. leucas was highest at temperatures over 298C and in areas with salinities between 7½ and 17.5½. Although they are able to osmoregulate in salinities from fresh to fully marine, young C. leucas may have a salinity preference. Reasons for this preference are unknown, but need to be further investigated. Introduction Williams (1981) and Snelson et al. (1984) reported Bull sharks (Carcharhinus leucas) are common that juveniles were common inhabitants of the In- worldwide in tropical and subtropical coastal, es- dian River Lagoon system on the east coast.