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This study examines the effects of nitrogen fertilization and different irrigation practices on the quality of St. Augustinegrass and the leaching of NO3-N in South Florida. The research involves analyzing various nitrogen sources and rates and their impact on turfgrass growth, water usage, and nitrogen leaching. Given the concerns over water quality and resource management, the objective is to find optimal combinations of nitrogen application and irrigation to minimize environmental impact while maintaining healthy turf.
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Evaluation of nitrogen fertilization and irrigation on St. Augustinegrass: NO3-N leaching and turfgrass quality D. M. Park
Use of St. Augustinegrass • ~52,000 acres harvested in 2000 • 43,775 acres for new residential starts • Right-of-ways, re-sodding, recreation, commercial Types of grass in Florida shown as a percent of total production for 2000 From Haydu et al., 2002
Sun-Sentinel Sep 26, 1999 Palm Beach Post May 17, 1998 The Orlando Sentinel May 9, 1998
Rationale • South West Florida Water Management District concerned over pollution • Decline in water quality • Overuse of water resources
Literature review: N sources • No N leaching differences from different sources (Geron et al., 1993) • Cultural practices: (ex. irrigation and mowing) (Snyder et al., 1976, 1980) (Cisar et al., 1991) • Comparison of coated AN versus non-coated AN in Myakka sand (Alva, 1992) • N requirement by different grass species (Sartain, 1992)
Literature review: N rates • Increase N rate, increase N leaching (Brown et al., 1977) (Cisar et al., 1991)
Literature review: Irrigation • Scheduled irrigation reduced [N] and leaching(Morton et al., 1988) • Increased N leaching from sand soils from initial simulated rainfall events(Wang and Alva, 1996)
Literature review: St. Augustinegrass • Focus on cool season grasses and bermudagrass • Minor information on St. Augustinegrass • Greater root density (Bowman et al., 2002) • Only field scale study in South Florida (Erickson et al., 2001) • 0.4% N loss of applied (Erickson et al., 2001)
Objectives • The effect of N rate on NO3-N leaching, St. Augustinegrass quality and clipping growth. • The effect of N sources on NO3-N leaching, St. Augustinegrass quality and clipping growth. • The effect of irrigation rate and frequency on NO3-N leaching, St. Augustinegrass quality and clipping growth.
Hypotheses N leaching will be minimized while maintaining satisfactory turf quality: H1 = Combining of soluble and controlled release N products H2 = Applying an optimum N rate H3 = Applying optimum irrigation
Margate fine sand soil • siliceous, hyperthermic Mollic Psamnaquent
Experimental design: Split Plot Repeated Measure Irrigation treatments (main plot) X N sources X (subplots) N rates X 4 Reps
40 cm Ceramic- cup sampler Install sample collection equipment
Location of ceramic-cup samplers, tubing, and sprinklers Cup samplers Vacuum & sample lines Sprinkler heads
Grass selection Top four St. Augustinegrass types grown in Florida in 2000 Palmetto 7% Floralawn 6% Bitterblue 3% Other 6% Floratam79% From Haydu et al., 2002 • Stenotaphrum secundatum (walt.) kuntze cv. ‘Floratam’
YEAR 1 (EXP.I) 2 irrigation schedules 4 N sources 3 N rates Two experiments YEAR 2 (EXP.II) • 2 irrigation schedules • 6 N sources • 2 N rates • Six, 2 month fertilization cycles
EXP. I: M&M Irrigation treatments (2) Excessive: 125% maximum weekly ETp over three applications per week (M-W-F). Conservative: 125% weekly ETp adjusted by month, over three applications per week (M-W-F). • If rain event = 8.4mm of rain, then next irrigation was voided.
ETP = KW(T-32) Where: K = 0.01 W = 1.07 T = mean temperature in oF. • Over predicts ET during temperatures > 70 oF • Uses a daily ET limiter of 7.6mm (Stewart and Mills, 1967) ETp calculated (McCloud, 1955)
Comparison of methods for calculating ETp for Miami, Florida ET Models M= McCloud P= Penman T= Thornwaite From Augustine, 1983
Exp. I: M&M UREA SCU
Exp. I:Observations & Measurements: • 1. Water budget: • Irrigation • Rainfall • ETp • Percolate Percolate = Rainfall + Irrigation – ET (Snyder et al., 1984)
3. Growth: • Dry weights • Clippings from a 2m2 area • Tissue N analysis • 0-15cm and 15-30cm cores Exp. I:Observations & Measurements: • 2. Visual turfgrass quality: • Scale from 1-10
Exp. I:Observations & Measurements: • 4. NO3-N concentrations and leaching • Vadose zone pore water collected when percolate is predicted • Flow injection analysis using a Cd-Cu reduction column • Daily loadings = [NO3-N] X percolate volume • (over 24h) • Total cycle loadings • Average cycle loadings • Annual loadings
Exp. I:Observations & Measurements: • 5. Percent N leached of applied N • Cycle • Annual
EXP. II: M&M Irrigation treatments (2) Excessive: 125% weekly ETp adjusted by month, over three applications per week (M-W-F). • If rain event = 8.4mm of rain, then next irrigation was voided. Conservative: Irrigate as above when visual wilt is present.
Exp. II: M&M IBDU SCU UREA
Exp. II: M&M * = 50% UREA/ 50% SCU will not be tested at this rate.
Exp. II:Observations & Measurements: • Water Budget • Visual turfgrass quality • Growth • N tissue analysis • NO3-N concentrations and leaching • Percent N leached of applied N • Visual turfgrass wilt
Statistical analysis • General linear model • SAS Inc. software
Anticipated Results Different combinations will result in different N leaching amounts and turfgrass quality
Implications • Less demand on water supply • Greater water use efficiency • Reduce risk of contamination to ground water supply • Basis for new BMP’s for St. Augustinegrass in South Florida