A Unified Approach to Recovery for a Healthy & Resilient Biscayne
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Year 2 Data Summary Report: Nekton of Sarasota Bay and a Comparison of Nekton Community Structure in Adjacent Southwest Florida Estuaries
Year 2 Data Summary Report: Nekton of Sarasota Bay and a Comparison of Nekton Community Structure in Adjacent Southwest Florida Estuaries T.C. MacDonald; E. Weather; R.F. Jones; R.H. McMichael, Jr. Florida Fish and Wildlife Conservation Commission Fish and Wildlife Research Institute 100 Eighth Avenue Southeast St. Petersburg, Florida 33701-5095 Prepared for Sarasota Bay Estuary Program 111 S. Orange Avenue, Suite 200W Sarasota, Florida 34236 June 4, 2012 TABLE OF CONTENTS LIST OF FIGURES ........................................................................................................................................ iii LIST OF TABLES .......................................................................................................................................... v ACKNOWLEDGEMENTS ............................................................................................................................ vii SUMMARY .................................................................................................................................................... ix INTRODUCTION ........................................................................................................................................... 1 METHODS .................................................................................................................................................... 2 Study Area ............................................................................................................................................... -
Current Status of Oyster Reefs in Florida Waters: Knowledge and Gaps
Current Status of Oyster Reefs in Florida Waters: Knowledge and Gaps Dr. William S. Arnold Florida FWC Fish and Wildlife Research Lab 100 Eighth Avenue SE St. Petersburg, FL 33701 727-896-8626 [email protected] Outline • History-statewide distribution • Present distribution – Mapped populations and gaps – Methodological variation • Ecological status • Application Need to Know Ecological value of oyster reefs will be clearly defined in subsequent talks Within “my backyard”, at least some idea of need to protect and preserve, as exemplified by the many reef restoration projects However, statewide understanding of status and trends is poorly developed Culturally important- archaeological evidence suggests centuries of usage Long History of Commercial Exploitation US Landings (Lbs of Meats x 1000) 80000 70000 60000 50000 40000 30000 20000 10000 0 1950 1960 1970 1980 1990 2000 Statewide: Economically important: over $2.8 million in landings value for Florida fishery in 2003 Most of that value is from Franklin County (Apalachicola Bay), where 3000 landings have been 2500 2000 relatively stable since 1985 1500 1000 In other areas of state, 500 0 oysters landings are on 3000 decline due to loss of 2500 Franklin County 2000 access, degraded water 1500 quality, and loss of oyster 1000 populations 500 0 3000 Panhandle other 2500 2000 1500 1000 Pounds500 of Meats (x 1000) 0 3000 Peninsular West Coast 2500 2000 1500 1000 500 0 Peninsular East Coast 1985 1986 1987 1988 1989 1990 1991 1992 1993 Year 1994 1995 1996 1997 1998 1999 2000 MAPPING Tampa Bay Oyster Maps More reef coverage than anticipated, but many of the reefs are moderately to severely degraded Kathleen O’Keife will discuss Tampa Bay oyster mapping methods in the next talk Caloosahatchee River and Estero Bay Aerial imagery used to map reefs, verified by ground-truthing Southeast Florida oyster maps • Used RTK-GPS equipment to map in both the horizontal and the vertical. -
State of Emergency on Red Tide for Tampa Bay
July 19, 2021 Governor Ron DeSantis State of Florida The Capitol 400 S. Monroe St. Tallahassee, FL 32399-0001 [email protected] Re: State of Emergency on Red Tide for Tampa Bay The undersigned respectfully request you immediately declare a state of emergency for the ongoing red tide and fish kill occurring in Tampa Bay. Such a declaration would help coordinate and fund relief efforts to mitigate further environmental and economic damage from red tide in the region. Red tide produces toxic chemicals that harm marine wildlife and humans. The ongoing, widespread red tide and fish kills have unreasonably interfered with the health, safety, and welfare of the State of Florida, causing harm to its environment and fragile ecosystems in Hillsborough, Manatee, Pinellas, and Sarasota counties. Therefore, we ask you exercise your authority, as the Governor of Florida, vested by the Florida Constitution and the Florida Emergency Management Act to issue an executive order declaring a state of emergency due to red tide in Tampa Bay. Sincerely, Audubon Everglades Scott Zucker, President [email protected] Cape Coral Friends of Wildlife Paul Bonasia, President [email protected] Cape Coral Wildlife Trust Lori Haus-Bulcock [email protected] Calusa Waterkeeper John Cassani, Calusa Waterkeeper [email protected] Cat Chase Media Caitlin Chase, Owner [email protected] Center for Biological Diversity Elise Bennett, Staff Attorney [email protected] Chispa Florida Maria Revelles, Program Director [email protected] Collins Law Group Martha M. Collins, Esq. [email protected] Defenders of Wildlife Elizabeth Flemming, Senior Florida Representative [email protected] Environment Florida Jenna Stevens, State Director [email protected] Florida Student Power Network Mary-Elizabeth Estrada, Tampa Climate Justice Organizer [email protected] Florida Turtle Conservation Trust George L. -
Rob Patten: Creating a Legacy for Coastal Island Sanctuaries
SUMMER 2011 2011 Audubon Assembly: Take Action for Florida’s Special Places October 14-15 Connect to Florida’s Special Places Guarding the Everglades Treasure 2011 Florida Audubon Society John Elting, Chairman, Leadership Florida Audubon Society Eric Draper Executive Director, Audubon of Florida President, Florida Audubon Our April board of directors meeting was a pivotal point for Florida Audubon Society (FAS). It was at that moment in time, surrounded by a chorus of birds at the Chinsegut Nature Center near Board of Directors FAS-owned Ahhochee Hill, that I think we all realized how far we had come this fiscal year. Our John W. Elting, Chairman Executive Director Eric Draper, our committed board and tireless staff had a lot to celebrate. Joe Ambrozy, Vice Chairman Sheri Ford Lewin, Board Secretary Even during tough economic times, we were ending the year in a positive financial position, Doug Santoni, Treasurer something other environmental groups are struggling with this year. We have achieved 100 per- Sandy Batchelor, Esq. cent board giving, both financially and in terms of gifts of time and talent. Our marketing efforts, Jim Brady particularly the expanded focus on social media, have resulted in a strong online community that Henry Dean, Esq. helped protect Florida’s state parks on three different occasions this year. Improved outreach and John Flanigan, Esq. regional events are building engagement in Audubon throughout Florida. The board’s science Charles Geanangel committee is taking our applied science work to new levels including accelerated involvement John Hood of citizen scientists. Lastly, we are beginning to work at the local, state and national level as One Reid Hughes Audubon. -
Interrelationships Among Hydrological, Biodiversity and Land Use Features of the Pantanal and Everglades
Interrelationships among hydrological, biodiversity and Land Use Features of the Pantanal and Everglades Biogeochemical Segmentation and Derivation of Numeric Nutrient Criteria for Coastal Everglades waters. FIU Henry Briceño. Joseph N. Boyer NPS Joffre Castro 100 years of hydrology intervention …urban development 1953 1999 Naples Bay impacted by drainage, channelization, and urban development FDEP 2010 SEGMENTATION METHOD Six basins, 350 stations POR 1991 (1995)-1998. NH4, NO2, TOC, TP, TN, NO3, TON, SRP, DO, Turbidity, Salinity, CHLa, Temperature Factor Analysis (PC extraction) Scores Mean, SD, Median, MAD Hierarchical Clustering NUMERIC NUTRIENT CRITERIA The USEPA recommends three types of approaches for setting numeric nutrient criteria: - reference condition approach - stressor-response analysis - mechanistic modeling. A Station’s Never to Exceed (NTE) Limit. This limit is the highest possible level that a station concentration can reach at any time A Segment’s Annual Geometric Mean (AGM) Limit. This limit is the highest possible level a segment’s average concentration of annual geometric means can reach in year A Segment’s 1-in-3 Years (1in3) Limit. This limit is the level that a segment average concentration of annual geometric means should be less than or equal to, at least, twice in three consecutive years. 1in3 AGM NTE 90% 80% 95% AGM : Annual Geometric Mean Not to be exceeded 1in3 : Annual Geometric Mean Not to exceed more than once in 3 yrs Biscayne Bay, Annual Geometric Means 0.7 AGMAGM Limit : Not to be exceeded 0.6 (Annual Geometric Mean not to be exceeded) 1in31in3 Limit : Not to exceed more 0.5 (Annualthan Geometric once Mean in not 3 to beyears exceeded more than once in 3 yrs) 0.4 0.3 Total Nitrogen, mg/LNitrogen, Total 0.2 Potentially Enriched 0.1 SCO NCO SNB NCI NNB CS SCM SCI MBS THRESHOLD ANALYSIS Regime Shift Detection methods (Rodionov 2004) Cumulative deviations from mean method CTZ CHLa Zcusum Threshold 20 0 -20 Cusum . -
Market Assessment Sources
To: Elizabeth Abernethy, Director, Date: October 2020 Planning and Development Services City of St. Petersburg Project #: 66316.00 From: Neale Stralow, Senior Planner Re: StPete2050 - Market Assessment Sources This correspondence is provided at the request of City of St. Petersburg staff relating to the final Market Assessment reporting provided by Landwise Advisors, LLC dated January 24, 2020 in support of the StPete2050 project. The final submittal includes source references and responses to City staff provided comments. The following is a source listing for future use by City staff. Slide # - Description Stated Sources Slide 5 – SWOT Grow Smarter 2014 and update 2019 State of the City, 2019 StPete2050 Economic Development Roundtable, October 10, 2019 Slide 7 – Population UF Bureau of Economic Research (BEBR) Southwest Florida Water Management District (SWFWMD) Pinellas County Metropolitan Planning Organization (MPO) Slide 8 – Population ESRI Business Analyst Online (BAO), 2019 Slide’s 23 to 30 – Employment US Census Bureau, 2017 Longitudinal Employer-Household Dynamics, OnTheMap Slide 31 – Target Industries St. Petersburg Economic and Workforce Development Department Slide 32 – Travel Time To Work US Census Bureau, 2013-2017 American Community Survey 5-year Estimates Slide’s 36 to 41 – Office Market Avision, Young Tampa Bay Office Report, Q3 2019 Statistics Slide 42 – Office Downtown Tenant CoStar, St. Petersburg City Directories Mix Slide 43 to 47 – Project Employment Moody’s 30-year forecast, Total No-Agricultural Employment, 2019 -
Assessment of the Cumulative Effects of Restoration Activities on Water Quality in Tampa Bay, Florida
Estuaries and Coasts https://doi.org/10.1007/s12237-019-00619-w MANAGEMENT APPLICATIONS Assessment of the Cumulative Effects of Restoration Activities on Water Quality in Tampa Bay, Florida Marcus W. Beck1 & Edward T. Sherwood2 & Jessica Renee Henkel3 & Kirsten Dorans4 & Kathryn Ireland5 & Patricia Varela6 Received: 10 April 2019 /Revised: 13 June 2019 /Accepted: 26 July 2019 # The Author(s) 2019 Abstract Habitat and water quality restoration projects are commonly used to enhance coastal resources or mitigate the negative impacts of water quality stressors. Significant resources have been expended for restoration projects, yet much less attention has focused on evaluating broad regional outcomes beyond site-specific assessments. This study presents an empirical framework to evaluate multiple datasets in the Tampa Bay area (Florida, USA) to identify (1) the types of restoration projects that have produced the greatest improvements in water quality and (2) time frames over which different projects may produce water quality benefits. Information on the location and date of completion of 887 restoration projects from 1971 to 2017 were spatially and temporally matched with water quality records at each of the 45 long-term monitoring stations in Tampa Bay. The underlying assumption was that the developed framework could identify differences in water quality changes between types of restoration projects based on aggregate estimates of chlorophyll-a concentrations before and after the completion of one to many projects. Water infra- structure projects to control point source nutrient loading into the Bay were associated with the highest likelihood of chlorophyll- a reduction, particularly for projects occurring prior to 1995. Habitat restoration projects were also associated with reductions in chlorophyll-a, although the likelihood of reductions from the cumulative effects of these projects were less than those from infrastructure improvements alone. -
Turkey Point Units 6 & 7 COLA
Turkey Point Units 6 & 7 COL Application Part 2 — FSAR SUBSECTION 2.4.1: HYDROLOGIC DESCRIPTION TABLE OF CONTENTS 2.4 HYDROLOGIC ENGINEERING ..................................................................2.4.1-1 2.4.1 HYDROLOGIC DESCRIPTION ............................................................2.4.1-1 2.4.1.1 Site and Facilities .....................................................................2.4.1-1 2.4.1.2 Hydrosphere .............................................................................2.4.1-3 2.4.1.3 References .............................................................................2.4.1-12 2.4.1-i Revision 6 Turkey Point Units 6 & 7 COL Application Part 2 — FSAR SUBSECTION 2.4.1 LIST OF TABLES Number Title 2.4.1-201 East Miami-Dade County Drainage Subbasin Areas and Outfall Structures 2.4.1-202 Summary of Data Records for Gage Stations at S-197, S-20, S-21A, and S-21 Flow Control Structures 2.4.1-203 Monthly Mean Flows at the Canal C-111 Structure S-197 2.4.1-204 Monthly Mean Water Level at the Canal C-111 Structure S-197 (Headwater) 2.4.1-205 Monthly Mean Flows in the Canal L-31E at Structure S-20 2.4.1-206 Monthly Mean Water Levels in the Canal L-31E at Structure S-20 (Headwaters) 2.4.1-207 Monthly Mean Flows in the Princeton Canal at Structure S-21A 2.4.1-208 Monthly Mean Water Levels in the Princeton Canal at Structure S-21A (Headwaters) 2.4.1-209 Monthly Mean Flows in the Black Creek Canal at Structure S-21 2.4.1-210 Monthly Mean Water Levels in the Black Creek Canal at Structure S-21 2.4.1-211 NOAA -
2006-SBEP-Stateofthebay.Pdf
he Sarasota Bay Estuary Program would like to thank the Tmany citizens, technical advisors, elected officials and government agency staff who have participated in the process of protecting and revitalizing Sarasota Bay. The work of our small team of five can realize comprehensive achievements when our efforts are supported by partner funds, agency staff and an active and committed Board of Directors. We offer special thanks to the partners to the 2004 Interlocal Agreement, which established the Program as a special district in Florida: Sarasota County, Manatee County, City of Sarasota, City of Bradenton, Town of Longboat Key, Florida Department of Environmental Protection and Southwest Florida Water Management District. Sarasota Bay Estuary Program • State of the Bay 006 4 Preface Sarasota Bay: Our Greatest Natural Asset 6 Setting the Stage Sarasota Bay: Our Economic and Ecological Treasure 8 Executive Summary Sarasota Bay Shows Significant Improvements 10 Water Quality Nitrogen Wastewater Pollution Air Pollution Stormwater Pollution Bacteria Contamination Tributary Action Plans Red Tide 14 Hydrology Preserving Balance in the Ecosystem and Maintaining Natural Flow 16 Bay Habitat Wetlands Wetland Restoration Monitoring Wetland Restoration Projects Seagrasses Hard Bottom Habitat Oysters Artificial Reefs Monitoring Reefs 24 Public Involvement in Restoring the Bay Community Recreation, Stewardship and Citizen Action Outreach—How the Community is Involved Sarasota County Water Efficient Landscape Ordinance Manatee County Rebate Program Southwest -
Prepared for County of Sarasota Coastal
FINAL REPORT LITTLE SARASOTA BAY CIRCULATION STUDY Prepared for County of Sarasota Coastal Zone Management Division Environmental Services Department 9250-110-RT Contract No. C82-66 Prepared by Stergios A. Dendrou Charles I. Moore Raymond Walton CAMP DRESSER & MCKEE 7630 Little River Turnpike Annandale, Virginia 22003 August 1983 Suggested reference Camp Dresser & McKee and Mote Marine Laboratory. 1983. Little Sarasota Bay circulation study. Sarasota County. Contract no C82-66. Mote Marine Laboratory Technical Report no 57. 175 p. Available from: Mote Marine Laboratory Library. TABLE OF CONTENTS Section Page No. LIST OF FIGURES . iii LIST OF TABLES . ix I INTRODUCTION ........................................... I-1 DESCRIPTION OF THE STUDY AREA .......................... I-1 SCOPE OF WORK .......................................... I-3 REPORT OUTLINE ......................................... I-4 II RESULTS AND CONCLUSIONS . II-1 III LITTLE SARASOTA BAY MODEL .............................. III-1 DYNAMIC ESTUARY MODEL .................................. III-1 MODEL THEORY ........................................... III-1 Basic Hydrodynamic Equations ...................... III-4 Numerical Solution-Stability ...................... III-5 Boundary Conditions ............................... III-6 LITTLE SARASOTA BAY GRID NETWORK ....................... III-7 Geometric Input Data .............................. III-7 IV PRELIMINARY ANALYSIS ................................... IV-1 TIDES AND TIDAL PHASING ................................ IV-1 WIND -
Of 6 62-302.532 Estuary-Specific Numeric Interpretations of The
FAC 62-302.532 Estuary-Specific Numeric Interpretations of the Narrative Nutrient Criterion Effective Date: 12/20/2012 62-302.532 Estuary-Specific Numeric Interpretations of the Narrative Nutrient Criterion. (1) Estuary-specific numeric interpretations of the narrative nutrient criterion in paragraph 62-302.530(47)(b), F.A.C., are in the table below. The concentration-based estuary interpretations are open water, area-wide averages. The interpretations expressed as load per million cubic meters of freshwater inflow are the total load of that nutrient to the estuary divided by the total volume of freshwater inflow to that estuary. Page 1 of 6 FAC 62-302.532 Estuary-Specific Numeric Interpretations of the Narrative Nutrient Criterion Effective Date: 12/20/2012 Estuary Total Phosphorus Total Nitrogen Chlorophyll a (a) Clearwater Harbor/St. Joseph Sound Annual geometric mean values not to be exceeded more than once in a three year period. Nutrient and nutrient response values do not apply to tidally influenced areas that fluctuate between predominantly marine and predominantly fresh waters during typical climatic and hydrologic conditions. 1. St.Joseph Sound 0.05 mg/L 0.66 mg/L 3.1 µg/L 2. Clearwater North 0.05 mg/L 0.61 mg/L 5.4 µg/L 3. Clearwater South 0.06 mg/L 0.58 mg/L 7.6 µg/L (b) Tampa Bay Annual totals for nutrients and annual arithmetic means for chlorophyll a, not to be exceeded more than once in a three year period. Nutrient and nutrient response values do not apply to tidally influenced areas that fluctuate between predominantly marine and predominantly fresh waters during typical climatic and hydrologic conditions. -
Draft Sea Level Rise Methodology Recommendation.Docx
RECOMMENDED PROJECTIONS OF SEA LEVEL RISE IN THE TAMPA BAY REGION Tampa Bay Climate Science Advisory Panel Updated April 2019 RECOMMENDED PROJECTIONS OF SEA LEVEL RISE IN THE TAMPA BAY REGION Executive Summary In this document, the Tampa Bay Climate Science Advisory Panel (CSAP) recommends a common set of sea level rise (SLR) projections for use throughout the Tampa Bay region. The recommendation establishes the foundation for a coordinated approach to address the effects of a changing climate, which advances the objectives of the newly-established Tampa Bay Regional Resiliency Coalition. Local governments and other agencies planning for SLR in the Tampa Bay region should incorporate the following key findings of this CSAP recommendation. • Data measured at the St. Petersburg tide gauge shows that water levels in Tampa Bay have already increased approximately 7.8 inches since 1946. • Based upon a thorough assessment of scientific data and literature, the Tampa Bay region can expect to see an additional 2 to 8.5 feet of SLR by 2100. • Projections of SLR should be consistent with present and future National Climate Assessment estimates and methods. The NOAA Low scenario should not be used for planning purposes. • Projections of SLR should be regionally corrected using St. Petersburg tide gauge data. • Adaptation planning should employ a scenario-based approach that, at minimum, considers location, time horizon, and risk tolerance. Introduction Formed in spring 2014, the CSAP is an ad hoc network of scientists and resource managers working in the Tampa Bay region (Figure 1). The group’s goal is to collaboratively develop science-based recommendations for local governments and regional agencies as they respond to climate change, including associated sea level change.