Lake Tohopekaliga Nutrient Reduction Plan
Transcription
Lake Tohopekaliga Nutrient Reduction Plan
Lake Tohopekaliga Nutrient Reduction Plan Danielle Honour, P.E., D.WRE Principal Kimberly Lawrence Stormwater Program Manager Florida Stormwater Association 2011 Winter Conference December 7, 2011 Lake Tohopekaliga (Toho) Background • Upper Kissimmee River Basin • 34 square miles in size • Watershed area approximately • 473 square miles – 17 square miles – Closed basins • Class 3 fresh water lake • Heavily used for fishing, hunting, boating, bird watching, and sightseeing Lake Tohopekaliga Background Overview of Lake Toho Impairment • Placed on Verified List by FDEP in November 2010 • Lake Toho initially impaired for nutrients [(i.e., increasing trend in Trophic State Index (TSI)] • Assessment Category 5 ‐ water quality standards are not attained and a Total Maximum Daily Load (TMDL) is required • Osceola County and the City of Kissimmee disagreed with the initial listing • Performed independent analysis that showed no impairment Lake Tohopekaliga Background Overview of Lake Toho Impairment (cont.) • FDEP re‐considered modifying the cause of impairment for the lake as an imbalance of flora and fauna, which is included under the narrative nutrient criteria in Chapter 62‐303, FAC • FDEP willing to change assessment category to 4e if a Nutrient Reduction Plan (NRP) is prepared • Final listing delayed until December 2011 “TSIs and annual mean chlorophyll a values shall be the primary means for assessing whether a water should be assessed further for nutrient impairment. Other information indicating an imbalance in flora or fauna due to nutrient enrichment, including, but not limited to, algal blooms, excessive macrophyte growth, decrease in the distribution (either in density or areal coverage) of seagrasses or other submerged aquatic vegetation, changes in algal species richness, and excessive diel oxygen swings, shall also be considered.” Lake Tohopekaliga Background Lake Management History • Lake Toho has been highly managed since the 1960s – – – – Water level stabilization (1960s) Sewage treatment plant effluent discharges (1940s to 1980s) Major drawdowns to improve habitat (1969, 1979, 1987, 2004) Introduction of Hydrilla spp. into the lake (1980s) • Impact of management activities on water quality not fully understood • FDEP agrees that more research and a better understanding of lake dynamics is needed before appropriate water quality targets can be set for the lake • Local MS4 permit holders held accountable for impairment Lake Tohopekaliga Background Competing Interests Make Water Quality Improvements a Challenge • Alteration of natural hydrology and lake level stabilization – Flood control purposes (Corps, SFWMD) – Fish habitat improvement (i.e., drawdowns) (FWCC) – Snail kite nesting • Aquatic plant management (FWCC) – Herbicide treatments can contribute to buildup of organic sediments and storage of nutrients in sediments – Snail kite nesting and foraging habitat Lake Tohopekaliga Background What is a Nutrient Reduction Plan? • Hybrid of a Basin Management Action Plan (BMAP) and a Reasonable Assurance Document (RAD) • Key differences: No water quality “targets” are set Loads are not allocated Not a restoration plan Monitoring plan and research priorities will align specifically to the goals and objectives identified by the stakeholders to determine true future targets – Not a long‐term solution: stepping stone – Plan is not formally “adopted” – – – – Nutrient Reduction Plan Who are the Participating Stakeholders? NRP Funding Plan Partners • • • • • City of Kissimmee City of Orlando City of St. Cloud Florida Department of Transportation (FDOT) Osceola County Technical Resources and Plan Support • • • • • • • Nutrient Reduction Plan FDEP Florida Farm Bureau Florida Department of Agriculture and Consumer Services (FDACS) Florida Fish & Wildlife Conservation Commission (FWCC) South Florida Water Management District (SFWMD) Orange County Reedy Creek Improvement District Purpose of the Nutrient Reduction Plan • Document local efforts that achieve nutrient reductions (TN and TP) • Provide additional time to assess the complex relationships within the lake • Focuses on reducing nutrient loads that can be achieved through management activities, capital improvement projects, non‐structural best management practices, and/or research activities • Can only control what’s in your own “backyard” Nutrient Reduction Plan Benefits of Nutrient Reduction Plan • Eliminates short‐term need for TMDL • May eliminate the long‐term need for TMDL • “Control your own destiny” – Allows flexibility • FDEP provides support where needed • Work closely with FDEP so that NRP is accepted • Begins reduction activities quickly • Potential long‐term cost savings Small investment helps focus where efforts should be vs. spending millions on questionable targets Nutrient Reduction Plan Benefits of Nutrient Reduction Plan (cont.) • FDEP moves Lake Toho to Category 4e (restoration activities) • Avoids additional permit requirements under a TMDL • Allows for more time for lake dynamics to be understood so that appropriate water quality targets can be set in the future • May discover that there is no “causative pollutant” for the excessive macrophyte impairment: Category 4d • Enhancement of public relations • Prepare for downstream TMDLs Nutrient Reduction Plan Nutrient Reduction Plan Approach • Estimate existing annual stormwater‐related anthropogenic land‐based pollutant loads generated from land surface (i.e., loads that stakeholders can control) • Define existing loads by jurisdiction • Evaluate load reduction associated with planned projects/activities • NRP modeling will not be used for the following: – Setting water quality targets – Determining load allocations Approach Modeling Approach • Applied HSPF model used for Kissimmee River Basin TMDL modeling • Used HSPF output in conjunction with GIS layers to estimate land‐based loading for all jurisdictional entities (including agriculture) • Apply attenuation factors to account for natural assimilation processes • Calculated baseline load (untreated load) • Calculated existing treated load (accounting for BMPs) • Year 2008 as the starting point of analysis Approach Modeling Approach (cont.) Loading Rates Soil TP TN Type (lb/ac/yr) (lb/ac/yr) A 1.96 14.3 B 2.01 14.7 Commercial/Industrial C 2.04 15.0 D 2.08 15.3 A 0.23 1.7 Cropland/ B 0.95 6.8 Improved Pasture C 1.43 10.3 D 2.11 15.4 A 1.26 9.2 High Density B 1.40 10.4 Residential C 1.48 11.0 D 1.57 11.8 A 0.33 2.5 Low Density B 0.60 4.6 Residential C 0.77 5.9 D 0.95 7.3 A 0.68 5.0 Medium Density B 0.91 6.8 Residential C 1.04 7.9 D 1.20 9.0 A 0.02 0.5 B 0.12 1.7 Forest/ Rangeland C 0.18 2.6 D 0.29 3.6 A 0.06 0.7 B 0.32 2.9 Unimproved Pasture C 0.49 4.4 D 0.72 6.3 A ‐‐‐ ‐‐‐ B ‐‐‐ ‐‐‐ Wetland C ‐‐‐ ‐‐‐ D 0.09 1.4 Land Use Category Land Use Soils Subbasins Existing BMPs Nutrient Reduction Plan Baseline Pollutant Load Results Developed Area (Acres) TN Anthropogenic Load (lbs/yr) TN Natural Load (lbs/yr) TP TP TN Total Anthropogenic Natural Load Load Load (lbs/yr) (lbs/year) (lbs/year) TP Total Load (lbs/yr) 80,033 22,968 180,399 83,266 263,665 21,054 4,791 25,845 11,731 3,533 8,198 88,912 5,202 94,113 11,867 379 12,246 City of St. Cloud 8,582 2,146 6,436 56,658 3,451 60,109 6,740 251 6,991 Orange County 83,500 41,755 41,745 313,648 51,436 365,084 31,878 2,653 34,531 City of Orlando 34,302 11,856 22,446 130,501 13,281 143,782 12,792 601 13,393 FDOT 2,501 292 2,209 26,222 463 26,686 3,183 36 3,219 Agriculture 39,310 ‐‐‐ ‐‐‐‐ ‐‐‐ ‐‐‐ 208,412 ‐‐‐ ‐‐‐ 19,505 Other 19,956 9,028 10,928 92,603 8,692 101,295 5,966 228 6,194 148,643 154,240 888,943 165,791 1,263,146 93,480 8,939 121,924 Jurisdiction/ Area Area Natural (Acres) Area (Acres) Osceola County 103,001 City of Kissimmee Totals: 302,883 Results Existing Treated TN Load Results Jurisdictional Area (ac) TN Baseline Anthropogenic Load (lbs/yr) TN Existing Anthropogenic Load (lbs/yr) TN Anthropogenic Load Reduction (%) Osceola County 103,001 180,399 140,698 22.0% 82,198 222,896 City of Kissimmee 11,731 88,912 70,175 21.1% 4,834 75,009 City of St. Cloud 8,582 56,658 42,152 25.6% 3,292 45,444 City of Orlando 34,302 130,501 86,470 33.7% 11,393 97,863 FDOT 2,501 26,222 20,848 20.5% 389 21,237 160,117 482,692 360,343 25.3% 102,106 462,449 Jurisdiction/ Area Totals: Results TN Natural Treated Load TN Total Existing Load (lbs/yr) (lbs/yr) Existing Treated TP Load Results Jurisdictional Area (ac) TP Baseline Anthropogenic Load (lbs/yr) TP Existing Anthropogenic Load (lbs/yr) TP Anthropogenic Load Reduction (%) Osceola County 103,001 21,054 13,253 37.1% 4,674 17,927 City of Kissimmee 11,731 11,867 7,357 38.0% 327 7,684 City of St. Cloud 8,582 6,740 3,681 45.4% 230 3,911 City of Orlando 34,302 12,792 6,484 47.1% 435 6,919 FDOT 2,501 3,183 2,227 30.0% 27 2,254 160,117 55,636 33,002 40.6% 5,693 38,695 Jurisdiction/ Area Totals: Results TP Natural Treated Load TP Total Existing Load (lbs/yr) (lbs/yr) Management Actions to Reduce Nutrient Loading • Stakeholders provided information on projects and programs in place since 2009 or will be implemented to reduce external nutrient loads to Lake Toho over the next five years – All projects and programs required to address nutrient loads (specifically TN and TP) to receive credit – Future management actions were given credit for the portion of the load reduction that was over and above any permit requirements Stakeholders are committing to reducing external nutrient loads to Lake Toho Management Actions Management Actions to Reduce Nutrient Loading (cont.) Project Number Project Name Project Type Treatment Acres 2,300 Project Cost End Date Status Unknown 2009 Completed TN Reduction (lbs/yr) TP Reduction (lbs/yr) Osceola County OSC‐11 Stewart Street Regional Pond Retrofit Wet detention pond OSC‐12 East Lake Reserve Reuse Stormwater reuse 3.7 Unknown 12/2028 OSC‐13 Bass Road Landfill Reuse Stormwater reuse 0.9 Unknown OSC‐14 Neptune Road Reuse Stormwater reuse 3.0 OSC‐15 Waterside Vista Reuse Stormwater reuse OSC‐16 Bellalago & Isles of Bellalago Reuse 2,667.0 381.3 Ongoing 255.9 5.8 04/2031 Planned and Funded 537.1 40.2 $640,690 09/2027 Ongoing 849.0 62.0 0.3 Unknown 02/2030 Ongoing 29.0 0.7 Stormwater reuse 327 Unknown 05/2031 Ongoing 3,807.5 277.6 OSC‐17 Poinciana Commerce Stormwater reuse Center Reuse 1.3 Unknown 06/2028 Ongoing 33.6 2.8 OSC‐18 Kissimmee Bay Reuse Stormwater reuse 130.0 Unknown 10/2030 Ongoing 588.9 13.1 OSC‐19 Remington Reuse Stormwater reuse 139.0 Unknown 11/2015 Ongoing 382.6 15.1 OSC‐20 Eagle Lake Reuse Stormwater reuse 17.3 Unknown 07/2023 Ongoing 1,204.6 84.6 OSC‐21 La Quinta Inn Reuse Stormwater reuse 2.8 Unknown 10/2022 Ongoing 90.8 7.0 OSC‐22 Street Sweeping Street Sweeping N/A Unknown Ongoing Ongoing 226.8 151.2 OSC‐23 Education Education N/A Unknown Ongoing Ongoing 8,441.9 795.2 Management Actions Project Load Reduction Summary Jurisdiction Project TN Load Reduction (lbs/yr) Project TP Load Reduction (lbs/yr) City of Kissimmee 3,070 1,204 City of St. Cloud 2,529 221 Osceola County 19,154 1,844 City of Orlando 7,986 2,505 FDOT 1,380 416 225 97 34,344 6,287 Orange County Totals: Management Actions Water Quality Monitoring Plan • Objective: Identify major inputs to Lake Toho and East Lake Toho to calculate the loading to the impaired waterbodies and to identify areas of high nutrients in the watershed • Stakeholders worked to identify stations within watershed Tributaries Sampling In‐Lake Sampling (SFWMD) Core Parameters Total phosphorus as P Core Parameters Supplemental Parameters Total phosphorus as P Total suspended solids (TSS)/turbidity Orthophosphate as P Nitrate/nitrite as N Chloride Total Kjeldahl nitrogen (TKN) Total Kjeldahl nitrogen (TKN) as N True color/total organic carbon (TOC) Dissolved oxygen (DO) Orthophosphate as P pH Alkalinity Temperature Conductivity Nitrate/nitrite as N Ammonium Nitrogen dioxide Chlorophyll Alkalinity Turbidity Chloride Color TSS Water Quality Monitoring Plan Next Steps: Acceptance and Implementation • FDEP Review of NRP (December 2011) • Change assessment category to 4e by December 2011 • Establish research priorities – Literature search on linkage between submerged aquatic vegetation (hydrilla) and nutrients is underway (University of Florida) • Implement water quality monitoring program • Track implementation – Periodic stakeholder meetings and coordination Next Steps Questions and Discussion Questions