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Blue-Green Algal Bloom Weekly Update Reporting June 26 - July 1, 2020
BLUE-GREEN ALGAL BLOOM WEEKLY UPDATE REPORTING JUNE 26 - JULY 1, 2020 SUMMARY There were 14 reported site visits in the past six days (6/26-7/1), with 16 samples collected. Algal bloom conditions were observed by the samplers at 11 sites. Satellite imagery from 6/29 shows bloom potential in Lake Okeechobee on approximately 45% coverage concentrated in the center of the lake, while visible portions of the Caloosahatchee and St. Lucie rivers and estuaries show no observable bloom activity. Over the course of the week, the area of potential algal bloom has decreased in open waters and intensified along the northwestern and northeastern shorelines. Satellite imagery from 6/29 for the St. Johns River is partially obscured by cloud cover, but shows little bloom potential in visible portions of Lake George or on the mainstem of the St. Johns River downstream of Lake George. The imagery indicates there may be an uptick on some of the lakes associated with the St. Johns River System. Please keep in mind that bloom potential is subject to change due to rapidly changing environmental conditions or satellite inconsistencies (i.e., wind, rain, temperature or stage). On 6/29, South Florida Water Management District (SFWMD) staff sampled the C43 Canal – Upstream of S77, C43 – Upstream of S79 and Lake Okeechobee – S308C (Lakeside). The Lake Okeechobee – S308C sample and C43 Canal – Upstream of S79 were both dominated by Microcystis aeruginosa, while the C43 Canal – Upstream of S77 had no dominant algal taxon. No cyanotoxins were detected in these three samples. On 6/29, the St. -
C.B. Moore on the Ocklawaha River: No Place for a Gopher
C.B. MOORE ON THE OCKLAWAHA RIVER: NO PLACE FOR A GOPHER CYNTHIA L. CERRATO Osceola National Forest, P.O. Box 70, Olustee, Florida 32072 In 1992, I conducted an archaeological research project at Some of the collection, along with Moore's original field notes, Davenport Landing in the Ocala National Forest (ONF). This remains there today (Davis 1987). small, high bluff is in the northernmost part of the forest, on the Considering the era in which Moore worked, there was a southern bank of the Ocklawaha River. Since preliminary testing limited choice of transportation modes. Since most of Moore's in 1991 yielded prehistoric ceramics and lithics, the goals of the 'excavations were at coastal or riverine sites, he traveled by project's first phase were to determine the site's time period, water. To reach his destinations, Moore employed the Gopher, function, and significance in American prehistory and to a stem-wheel steamboat (Figure 2). The Gopher was 30.5 m delineate the site's boundaries. The second phase of this project (100 ft) long, about 6 m (20 ft) wide, and normally "carried a was to investigate an earthwork on the bluff. The earthwork captain, a pilot, an engineer, a crew of five men, six men to resembled a small volcano and was approximately 12 m in dig, and special guests" (Morse and Morse 1983:21). diameter. The central "pit" was at least 1 m deep with ridges 1- Moore's Southeastern excavations began in Florida. From 2 m high. The ONF Archeologist, Ray Willis, and I believed 1891 to 1895, he excavated sites along the St. -
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. -
Putnam County Conservation Element Data & Analysis
Putnam County COMPREHENSIVE PLAN CONSERVATION ELEMENT EAR-based Amendments Putnam County 2509 Crill Avenue, Suite 300 Palatka, FL 32178 Putnam County Conservation Element Data & Analysis Putnam County Conservation Element Table of Contents Section Page I. Introduction 4 II. Inventory of Natural Resources 5 A. Surface Water Resources 5 1. Lakes and Prairies 5 2. Rivers and Creeks 8 3. Water Quality 10 4. Surface Water Improvement and Management Act (SWIM) 15 5. Analysis of Surface Water Resources 16 B. Groundwater Resources 17 1. Aquifers 17 2. Recharge Areas 18 3. Cones of Influence 18 4. Contaminated Well Sites 18 5. Alternate Sources of Water Supply 19 6. Water Needs and Sources 21 7. Analysis of Groundwater Resources 22 C. Wetlands 23 1. General Description of Wetlands 23 2. Impacts to Wetlands 25 3. Analysis of Wetlands 26 D. Floodplains 26 1. National Flood Insurance Program 26 2. Drainage Basins 26 3. Flooding 29 4. Analysis of Floodplains 30 E. Fisheries, Wildlife, Marine Habitats, and Vegetative Communities 30 1. Fisheries 30 2. Vegetative Communities 30 3. Environmentally Sensitive Lands 35 4. Wildlife Species 55 5. Marine Habitat 57 6. Analysis of Environmentally Sensitive Lands 58 F. Air Resources 58 1. Particulate Matter (PM) 58 2. Sulfur Dioxide 59 3. Nitrogen Oxides 60 4. Total Reduced Sulfur Compounds 60 5. Other Pollutants 61 6. Analysis of Air Resources 61 EAR-based Amendments 10/26/10 E-1 Putnam County Conservation Element Data & Analysis G. Areas Known to Experience Soil Erosion 62 1. Potential for Erosion 62 2. Analysis of Soil Erosion 64 H. -
Ocklawaha River Hydrologic Basin
Why Care Implementing Future Growth Permitting Process Final Design Success Economic Growth often requires new development and/or redevelopment. Schools . Downtown Revitalization Anti-Degradation under Chapter 62-4.242 and 62-302.300, F.A.C and 40D-4.301, F.A.C., require agencies to ensure permits... “will not adversely affect the quality of receiving waters such that the water quality standards will be violated.” 403.067 F.S. Requires Consideration of Future Growth in the Development of BMAPs. Most rely on Anti-Degradation and the “Net-Improvement” Policy. Downstream Protection Protecting Waters = More Stringent Controls = More $ = Higher Project Cost WEEKI WACHEE 1948 WEEKI WACHEE 2013 http://www.slideshare.net/FloridaMemory http://www.tampabay.com/news/business/tourism/ Project/florida-winter-holidays clear-water-mermaids-and-yes-history-at-weeki-wachee- springs/2131164 Preserving Water Quality & Project Specific Requirements Williamson Blvd - road extension project of approximately 2 miles. Located: Port Orange, Volusia County Small section of existing road widening. Multi-use improvement including transportation corridor planning. Soil Conditions: High Groundwater Existing Borrow Pits remain on-site from construction of I-95. Land use change from natural conditions to roadway. Williamson Blvd Project Outfalls to Spruce Creek. Spruce Creek has an adopted Total Maximum Daily Load (TMDL) for Dissolved Oxygen (DO). Spruce Creek Impaired for . Dissolved Oxygen (DO) . Causative Pollutant . Total Phosphorus . BOD Wasteload Allocations (WLA) . NPDES MS4 % Reduction: . 27% TP . 25% BOD . TMDL (mg/L) . 0.16 mg/L TP . 2.17 mg/L BOD Net Improvement is required for Phosphorus. Net Improvement meets: . Anti-Degradation Rules . 403.067 Future Growth . -
Fish Study Cover 3
Putnam County Environmental Council ! !"#"$%&%#'("#)(*%+',-"'.,#(,/( '0%(1.+0(2,345"'.,#+(,/(6.57%-( 63-.#$+("#)('0%(!.))5%("#)(8,9%-( :;<5"9"0"(*.7%-=(15,-.)"=(>6?( ( *,@(*A(8%9.+(BBB=(!A?A=(2ACA6A( MANAGEMENT AND RESTORATION OF THE FISH POPULATIONS OF SILVER SPRINGS AND THE MIDDLE AND LOWER OCKLAWAHA RIVER, FLORIDA, USA A Special Report for The Putnam County Environmental Council Funded by a Grant from the Felburn Foundation By Roy R. “Robin” Lewis III, M.A., P.W.S. Certified Professional Wetland Scientist and Certified Senior Ecologist May 14, 2012 Cover photograph: Longnose Gar, Lepisosteus osseus, in Silver Springs, Underwater Photograph by Peter Butt, KARST Environmental ACKNOWLEDGEMENTS The author wishes to thank all those who reviewed and commented on the numerous drafts of this document, including Paul Nosca, Michael Woodward, Curtis Kruer and Sandy Kokernoot. All conclusions, however, remain the responsibility of the author. CITATION The suggested citation for this report is: LEWIS, RR. 2012. MANAGEMENT AND RESTORATION OF THE FISH POPULATIONS OF SILVER SPRINGS AND THE MIDDLE AND LOWER OCKLAWAHA RIVER, FLORIDA, USA. Putnam County Environmental Council, Interlachen, Florida. 27 p + append. Additional copies of this document can be downloaded from the PCEC website at www.pcecweb.org. i EXECUTIVE SUMMARY Sixty‐nine (69) species of native fish have been documented to have utilized Silver Springs, Silver River and the Upper, Middle and Lower Ocklawaha River for the period of record. Fifty‐nine of these are freshwater fish species and ten are native migratory species using marine, estuarine and freshwater habitats during their life history. These include striped bass, American eel, American shad, hickory shad, hogchoker, striped mullet, channel and white catfish, needlefish and southern flounder. -
Silver River Ecosystem Metabolism Study (2011-2012)
Final Report Silver River Ecosystem Metabolism Study (2011-2012) Prepared for Howard T. Odum Florida Springs Institute June 2012 Prepared by Wetland Solutions, Inc. Acknowledgements This report was prepared by Wetland Solutions, Inc. (WSI) for the Howard T. Odum Florida Springs Institute (FSI) and was partially funded by a grant from the Felburn Foundation. Final Report Silver River Ecosystem Metabolism Study (2011-2012) Prepared for Howard T. Odum Florida Springs Institute June 2012 Prepared by Wetland Solutions, Inc. i Silver River Ecosystem Monitoring Project Table of Contents Figures ....................................................................................................................................................iii Tables ...................................................................................................................................................... iv Section 1.0 Introduction ........................................................................................................................ 5 Section 2.0 Methods ............................................................................................................................... 6 2.1 Sampling Events ......................................................................................................................... 6 2.2 Monitoring Stations ................................................................................................................... 7 2.3 Light Measurements ............................................................................................................... -
Status of the Aquatic Plant Maintenance Program in Florida Public Waters
Status of the Aquatic Plant Maintenance Program in Florida Public Waters Annual Report for Fiscal Year 2006 - 2007 Executive Summary This report was prepared in accordance with §369.22 (7), Florida Statutes, to provide an annual assessment of the control achieved and funding necessary to manage nonindigenous aquatic plants in intercounty waters. The authority of the Department of Environmental Protection (DEP) as addressed in §369.20 (5), Florida Statutes, extends to the management of nuisance populations of all aquatic plants, both indigenous and nonindigenous, and in all waters accessible to the general public. The aquatic plant management program in Florida’s public waters involves complex operational and financial interactions between state, federal and local governments as well as private sector compa- nies. A summary of plant acres controlled in sovereignty public waters and associated expenditures contracted or monitored by the DEP during Fiscal Year 2006-2007 is presented in the tables on page 42 of this report. Florida’s aquatic plant management program mission is to reduce negative impacts from invasive nonindigenous plants like water hyacinth, water lettuce and hydrilla to conserve the multiple uses and functions of public lakes and rivers. Invasive plants infest 95 percent of the 437 public waters inventoried in 2007 that comprise 1.25 million acres of fresh water where fishing alone is valued at more than $1.5 billion annually. Once established, eradicating invasive plants is difficult or impossible and very expensive; therefore, continuous maintenance is critical to sustaining navigation, flood control and recreation while conserving native plant habitat on sovereignty state lands at the lowest feasible cost. -
U N S U U S E U R a C S
Ocklawaha River 301 y 316 441 CoRd E 316 E Hw Reddick CoHwy 316 PUTNAM 1 NE Jacksonville Rd Graveyard Lake Lake Kerr 95 Grass Lake Oklawaha R 108th CongressLake Healy of theCowpond Lake United States Big Lake Louise StHwy 19 VOLUSIA Eaton Cr 5 1 3 y w FLAGLER H o Mud Lake C ) Indian Lake Prarie wy s H ing pr lt S Sa 4 ( 31 wy Salt Springs Hwy StH Lake Disston Eaton Cr N Hwy 314A 0 y 4 Ormond Beach Hw Lake St Eaton Wire Rd 0 Pierson StHwy 11 4 ) 75 N F 96 Rd y d StH w R Nfs 79 C rd e (Dan F o n t Lake e r Charles S t Lake George Lake Shaw Lake Pierson Lake Jumper St Hwy 40 ( F t Brooks Rd) Cain Lake NW 22nd St ) e NW 4th Ave v A NE 17th Rd h d 40) t R 27 S (St 8 t 40 NW 20th St NE 14th R 5 wy ( wy Redwater Lake d tH StH 4 S Daytona Beach 10th St 1 NE 14th St St 0 9 P NE 25th Ave ( Little Lake Jumper S i NE 11th St StHwy 40 (Silver n Springs Blvd) t DISTRICT e 4 H Payne Creek 1 A w StHwy 40 StHwy 40 (Silver StHwy 35 3 Ch Lake Prarie v y y e SE 25th SE Springs Blvd) w Rd Ter 196 NE tH 1 7 S 9 Mill Dam ) Ocala Ave Lake Lake Winona SE 14th St StHwy 40 (Ft Brooks Rd) SE 17th St StHwy 464 Caraway Lake 40 (17th St) StHwy SE 30th SE 17th St Bear Hole Ave Wildcat Lake Astor Lake Clifton Lake Dias StHwy St Johns River 40 Halfmoon Lake Schimmerhorne Lake Little Lake Bryant Lake Bryant North Grasshopper Lake VOLUSIA MARION NF Road 599-1 DISTRICT 24 StHwy 464 (Maricamp Rd) StHwy 35 Rd)(Baseline StHwy 200 South Grasshopper Lake Wells Pond 17 441 Halford Lake De Leon Springs Marshall Chain O Swamp Lake Lake Bessiola StHwy 35 (58th Ave) Silver Farles -
DEP RELEASES ORANGE CREEK BASIN MANAGEMENT ACTION PLAN --Program Moves Aggressively Forward with Cooperation of Local, Regional Stakeholders
DEP RELEASES ORANGE CREEK BASIN MANAGEMENT ACTION PLAN --Program moves aggressively forward with cooperation of local, regional stakeholders-- TALLAHASSEE - The Florida Department of Environmental Protection (DEP) today announced adoption of the Orange Creek Basin Management Action Plan (BMAP), a roadmap to restoring and protecting water quality in the Orange Creek Basin. The action plan was developed in partnership with the City of Gainesville, Marion and Alachua Counties, the St. Johns River Water Management District, Alachua County Health Department, University of Florida, Gainesville Regional Utilities, private silviculture interests and other local and state stakeholders. Orange Creek is a tributary of the Ocklawaha River. Implementation of the plan will benefit surface waters in Alachua and Marion Counties, including Orange Lake, Lochloosa Lake, Newnans Lake, Tumblin Creek, Sweetwater Branch, Hogtown Creek, Lake Wauberg, Paynes Prairie/Alachua Sink, and the Ocklawaha River. “The Orange Creek Basin Management Action Plan represents an exceptionally strong collaboration among local, regional, and state agencies, elected officials, citizens, and private interests,” said DEP Deputy Secretary Mimi Drew. “Together we have committed to a concrete set of actions to reduce pollution in the streams, rivers, and lakes throughout the basin.” In 2003, DEP adopted water quality restoration targets, called Total Maximum Daily Loads (TMDLs). The TMDLs establish the amount of reduction of nutrients that is needed to protect or restore the lakes and Alachua Sink, and the amount of reduction of fecal coliform bacteria that is needed to protect or restore streams in the basin. The TMDLs help stakeholders evaluate and identify local actions to control these pollutant discharges. The action plan lists the steps that must be taken, a schedule for their implementation, and potential resources to accomplish them. -
Assessment of Cyanotoxins in Florida's Lakes, Reservoirs And
Assessment of Cyanotoxins in Florida’s Lakes, Reservoirs and Rivers by Christopher D. Williams BCI Engineers and Scientists, Inc. Lakeland, FL. John W. Burns Andrew D. Chapman Leeanne Flewelling St. Johns River Water Management District Palatka, FL. Marek Pawlowicz Florida Department of Health/Bureau of Laboratories Jacksonville, FL. Wayne Carmichael Wright State University Dayton, OH. 2001 Executive Summary EXECUTIVE SUMMARY Harmful algal blooms (HABs) are population increases of algae above normal background levels and are defined by their negative impacts on the environment, the economy, and human health. Historically, many of Florida's largest and most utilized freshwater and estuarine systems have been plagued by occasional blooms of harmful algae. During the last decade, however, the frequency, duration, and concentration levels of these blooms in freshwater and brackish water have increased significantly, primarily due to changes in land utilization, changes in hydrology, increases in nutrient runoff, loss of aquatic vegetation, and a climate that is very conducive to algal growth and proliferation. In 1998, the Florida Harmful Algal Bloom Task Force was established to determine the extent to which HABs pose a problem for the state of Florida. Blue-green algae (cyanobacteria) were identified as top research priorities due to their potential to produce toxic chemicals and contaminate natural water systems. In June 1999, the St. Johns River Water Management District (SJRWMD) initiated a collaborative study in conjunction with the Florida Marine Research Institute, the Florida Department of Health, and Wright State University to determine the geographical distribution of various types of toxin-producing blue-green algae in Florida's surface waters and to positively identify any algal toxins present in these waters. -
Florida Fish and Wildlife Conservation Commission Statewide Alligator Harvest Data Summary
FWC Home : Wildlife & Habitats : Managed Species : Alligator Management Program FLORIDA FISH AND WILDLIFE CONSERVATION COMMISSION STATEWIDE ALLIGATOR HARVEST DATA SUMMARY YEAR AVERAGE LENGTH TOTAL HARVEST FEET INCHES 2000 8 8 2,552 2001 8 8.2 2,268 2002 8 3.7 2,164 2003 8 4.6 2,830 2004 8 5.8 3,237 2005 8 4.9 3,436 2006 8 4.8 6,430 2007 8 6.7 5,942 2008 8 5.1 6,204 2009 8 0 7,844 2010 7 10.9 7,654 2011 8 1.2 8,103 Provisional data 2000 STATEWIDE ALLIGATOR HARVEST DATA SUMMARY AVERAGE LENGTH TOTAL AREA NO AREA NAME FEET INCHES HARVEST 101 LAKE PIERCE 7 9.8 12 102 LAKE MARIAN 9 9.3 30 104 LAKE HATCHINEHA 8 7.9 36 105 KISSIMMEE RIVER (POOL A) 7 6.7 17 106 KISSIMMEE RIVER (POOL C) 8 8.3 17 109 LAKE ISTOKPOGA 8 0.5 116 110 LAKE KISSIMMEE 7 11.5 172 112 TENEROC FMA 8 6.0 1 402 EVERGLADES WMA (WCAs 2A & 2B) 8 8.2 12 404 EVERGLADES WMA (WCAs 3A & 3B) 8 10.4 63 405 HOLEY LAND WMA 9 11.0 2 500 BLUE CYPRESS LAKE 8 5.6 31 501 ST. JOHNS RIVER 1 8 2.2 69 502 ST. JOHNS RIVER 2 8 0.7 152 504 ST. JOHNS RIVER 4 8 3.6 83 505 LAKE HARNEY 7 8.7 65 506 ST. JOHNS RIVER 5 9 2.2 38 508 CRESCENT LAKE 8 9.9 23 510 LAKE JESUP 9 9.5 28 518 LAKE ROUSSEAU 7 9.3 32 520 LAKE TOHOPEKALIGA 9 7.1 47 547 GUANA RIVER WMA 9 4.6 5 548 OCALA WMA 9 8.7 4 549 THREE LAKES WMA 9 9.3 4 601 LAKE OKEECHOBEE (WEST) 8 11.7 448 602 LAKE OKEECHOBEE (NORTH) 9 1.8 163 603 LAKE OKEECHOBEE (EAST) 8 6.8 38 604 LAKE OKEECHOBEE (SOUTH) 8 5.2 323 711 LAKE HANCOCK 9 3.9 101 721 RODMAN RESERVOIR 8 7.0 118 722 ORANGE LAKE 8 9.3 125 723 LOCHLOOSA LAKE 9 3.4 56 734 LAKE SEMINOLE 9 1.5 16 741 LAKE TRAFFORD