February 16, 2012 Adventures in Ecological Restoration Nitrate Nitrogen Control Efforts in Floridan Aquifer Springs Robert L. Knight, Ph.D.
Nitrate in Florida Spring Ecosystems Presentation Outline Healthy Spring Ecosystems Rising Spring Nitrate Concentrations Sources of Excess N Control Efforts/Needs Challenges
Healthy Springs Structure Drawn by E.A. McMahan in Odum et al. 1998
Springs Support a Unique Ecology Florida s springs are essential habitat for a diverse and unique assemblage of plants and wildlife
Springs Provide Economic Benefits The direct economic value of Florida s largest springs is estimated to be over $300,000,000 per year
Average NOx-N (mg/l) >60% of Florida s Springs are Impaired 6.00 5.00 4.00 3.00 2.00 1.00 0.00 1 Spring ID Spring ID Spring ID Beecher Spring 1 Fenney Spring 45 Cedar Head Spring 89 Copper Spring 2 Hornsby Spring 46 Wakulla Tubing D-Tunnel 90 Green Cove Spring 3 Horn Spring 47 Gum Spring Main 91 Holton Creek Rise 4 Cypress Spring 48 Little River Spring 92 Orange Spring 5 Starbuck Spring 49 Wakulla Tubing C-Tunnel 93 Suwannee Springs 6 Turtle Spring 50 Double Spring 94 Newport Spring 7 Salt Spring (Hernando) 51 Jackson Mill Pond Spring 95 Waldo Spring 8 Hunter Spring 52 Wakulla Tubing B-Tunnel 96 Warm Mineral Spring 9 Ellaville Spring 53 Rainbow Spring #6 97 Santa Fe Spring (Columbia) 10 Falmouth Spring 54 Silver Spring Main 98 Nutall Rise 11 Alapaha River Rise 55 Hart Springs 99 Alexander Springs 12 Wacissa Springs #2 56 Otter Spring 100 Silver Glen Springs 13 Wakulla Tubing A/K-Tunnel 57 Bubbling Spring 101 Washington Blue Spring (Choctawhatchee) 14 Black Spring (Jackson) 58 Wekiwa Springs 102 Steinhatchee River Rise 15 Wakulla Tubing K-Tunnel 59 Rainbow Spring #1 103 Santa Fe River Rise (Alachua) 16 Wakulla Tubing A/D-Tunnel 60 Deleon Spring (Volusia) 104 Welaka Spring 17 Holmes Blue Spring 61 Ginnie Spring 105 Williford Spring 18 Jackson Blue Hole Spring 62 Reception Hall Spring 106 Juniper Springs 19 Homosassa #1 63 Devils Ear Spring (Gilchrist) 107 Columbia Spring 20 Sanlando Springs 64 Blue Grotto Spring 108 Fern Hammock Springs 21 Suwanacoochee Spring 65 Madison Blue Spring 109 Treehouse Spring 22 Gator Spring (Hernando) 66 Rainbow Spring #4 110 Salt Springs (Marion) 23 Homosassa #2 67 Rock Springs 111 Crays Rise 24 Chassahowitzka Spring Main 68 Mearson Spring 112 Washington Blue Spring (Econfina) 25 Citrus Blue Spring 69 Gilchrist Blue Spring 113 Big Spring (Big Blue Spring) (Jefferson) 26 Levy Blue Spring 70 Manatee Spring 114 Morrison Spring 27 Mission Spring 71 Sun Springs 115 Spring Creek Rise #1 28 Allen Mill Pond Spring 72 Telford Spring 116 St. Marks River Rise (Leon) 29 Chassahowitzka Spring #1 73 Owens Spring 117 Gainer Spring #1C 30 Magnolia Spring 74 Troy Spring 118 Spring Creek Rise #2 31 Homosassa #3 75 Buckhorn Spring 119 Tarpon Hole Spring 32 Rock Bluff Springs 76 Crystal Springs 120 Gainer Spring #3 33 Bugg Spring 77 Lafayette Blue Spring 121 Poe Spring 34 Blue Hole Spring (Columbia) 78 Running Springs 122 Shepherd Spring 35 Springboard Spring 79 Unknown 11365 123 Brunson Landing Spring 36 Volusia Blue Spring 80 Lithia Springs Major 124 Gainer Spring #2 37 Branford Spring 81 Hays Spring (Jackson) 125 Ponce De Leon Springs 38 Siphon Creek Rise 82 Jackson Blue Spring 126 Sulphur Spring (Hillsborough) 39 Little Springs (Hernando) 83 Shangri-La Springs 127 Rhodes Spring #1 40 Weeki Wachee Main Spring 84 Lafayette Ruth Spring 128 Rhodes Spring #2 41 Ichetucknee Head Spring (Suwannee) 85 Fanning Springs 129 Rhodes Spring #4 42 Guaranto Spring 86 Apopka Spring 130 Natural Bridge Spring 43 Wakulla Spring 87 Beckton Springs 44 Gadsen Spring 88 4 7 10 13 16 19 22 25 28 31 34 37 40 43 46 49 52 55 58 61 64 67 70 73 76 79 82 85 88 Spring ID Stats NOx-N Average 0.803 Min 0.004 Max 5.10 FDEP s Numeric Nutrient Standard for Nitrate Nitrogen is Expected to be 0.35 mg/l 91 94 97 100 103 106 109 112 115 118 121 124 127 130
Impaired Springs (FDEP 2009) Volusia Blue DeLeon Jackson Blue Silver Springs Rainbow Weeki Wachee Fanning Manatee Wakulla Etc. Silver Jackson Blue Weeki Wachee Rainbow
A Big Problem for Springs GW nitrate nitrogen levels are increasing: Nitrate contamination is widespread in the Floridan Aquifer Springs are sensitive to elevated nitrate
Weeki Wachee Springs Nitrate Weeki Wachee Springs: Nitrate increase = 1,500% since 1970 Concentration mg/l 0.8 0.7 0.6 0.5 0.4 0.3 0.2 0.1 NO2/NO3-N PO3-P DEP s max. allowed concentration Frydenburg 2008 0 1970 1983 1997
Rising Nitrate Silver Springs NO3 >2000% increase since 1907 1.20 1.00 Nitrate-N (mg/l) 0.80 0.60 0.40 FDEP s safe level = NO3-N < 0.35 mg/l 0.20 0.00 1/1/1950 9/10/1963 5/19/1977 1/26/1991 10/4/2004
Projected Nitrate in Silver Springs year (source) nitrate-n concentration (mg/l) 1907 USGS 0.04 1946 USGS 0.29 1953 Odum 0.46 (average) 1979 USGS 0.71 1995 USGS 0.90 2005 this study 1.07 2055 (projected) this study 2.02
mg/l Florida Groundwater Nitrate Concentrations (2000-2004)
Groundwater = Surface Water Sunlight NO3-N Spring
Nitrogen in Springs = More Algae Weeki Wachee, circa 1950s Weeki Wachee 2001
Agricultural and Urban Development are Resulting in Elevated Nitrate Nitrogen Concentrations throughout North and Central Florida (and Many Other Areas of the U.S.) Nitrogen Sources
Silver Springs Two-Year Capture Zone Land Use (1949) (SJRWMD 2007)
Silver Springs Two-Year Capture Zone Land Use (2005) (SJRWMD 2007)
Agricultural/Urban Development vs. Silver Spring Nitrate 1.20 1.00 y = 0.0181x - 0.1002 R 2 = 0.9569 NOx-N (mg/l) 0.80 0.60 0.40 0.20 0.00 0 20 40 60 80 % Developed
Land Use Nitrogen Loading Nitrate-N concentration (mg/l) in ground-water samples grouped by land use at well locations (From: Phelps 2004). Land use N Minimum Maximum Median Urban 29 <0.02 5.9 1.15 Agriculture 13 0.05 12 1.7 Rangeland & forest 11 <0.02 2.2 0.09 Unmanaged forestry is the most protective land use
Alachua County Floridan Aquifer Degree of Confinement
GW Nitrate Concentration is a Function of Aquifer Confinement Alachua County Nitrate-N mg/l
Groundwater Nitrate as a Function of Land Use and Aquifer Vulnerability Groundwater Nitrate (mg/l) Land Use Less Vulnerable Vulnerable More Vulnerable Urban 0.50 1.03 1.20 Agriculture 0.54 0.66 1.56 Rangeland 0.32 0.44 0.87 Upland Forest 0.35 0.44 0.70 Groundwater nitrate data from 2000-2004; land use from SJRWMD, SRWMD, NWFWMD, and SWFWMD; aquifer vulnerability from FDEP; data compiled by the Florida Springs Institute.
Rainbow Springs Nitrogen Sources (Jones et al. 1996) Agriculture = 95%
Agricultural Practices Fertilizer use and animal wastewater management are resulting is nitrate contamination of the Floridan Aquifer System
Wakulla Springs Nitrogen Sources Municipal and Domestic Wastewater = 61% Total estimated load 889 metric tons per year Chellete et al. 2002 (data for 1990-1999)
Municipal Wastewater Disposal City of Tallahassee sprayfield estimated nitrogen load to groundwater was 356 metric tons per year
So What Can Be Done? L.V. Korhnak
Fix The Fundamental Disconnect The background nitrate concentration in groundwater and springs is 0.05 mg/l The groundwater nitrate standard = 10 mg/l (200 times higher!)
Rainbow Springs Total Maximum Daily Loads (TMDL) for Spring Water Quality Protection
TMDL Establishes Pollutant Load Goals TMDL for Fanning Springs and Lower Santa Fe River is 0.35 mg/l, requiring a 35 to 51% reduction in nitrogen loads
BMAP is a Roadmap for Restoration Basin Management Action Plan (BMAP) will be developed for all impaired springs In urban watersheds BMAP implementations is relatively fast (5 to 10 years) In agricultural watersheds compliance is expected to be slow (>20 years)
Wastewater Nitrogen Loads: GRW Wetlands Offer a Reasonable Alternative A groundwater recharge constructed treatment wetland (GRW) removes nutrients and other pollutants and infiltrates clean water into the groundwater at a lower cost than other treatment options Green Cay Wetland, Palm Beach Co.
Agriculture Nitrogen Loads: Forestry is the Best Alternative Minimal water use Minimal nitrogen use Provides economic return while protecting water resources!
Wetlands and Forests Provide Multiple Benefits Groundwater protection Surface water protection Air quality protection Carbon sequestration Wildlife habitat Economic savings
Nitrate in Springs: A Problem With a Solution Eliminate fertilizer use in moderate and high vulnerability areas Convert row crop agriculture to forestry Use constructed wetlands to costeffectively remove nitrogen in human and animal wastes Silver Springs 2005
Nitrate in Springs: A Clear Future? Challenges Public education and support Slow regulatory process Cost of making agricultural land use changes Cost of providing advanced nitrogen removal for wastewaters Silver Springs circa 1950s