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Investigation of Soil Amendments for Use in USGA Putting Greens

Investigating soil amendments and surfactant-modified amendments to reduce nutrient leaching on Tifdwarf bermudagrass in USGA putting greens. Includes methods, results, and practical implications.

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Investigation of Soil Amendments for Use in USGA Putting Greens

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  1. Investigation of Soil Amendments for Use in USGA Putting Greens T.W. Shaddox

  2. Problem Assessment • Droughts from 1997 to 2000 have brought about consumptive use permits for many superintendents • Superintendents have less water to maintain the same quality turfgrass

  3. Case Study • Colbert Hills GC – Manhattan, KS (Fry, 2002) • 120 million gallons year-1 = 374 acre feet • 374 / 365 days ≈ 1 acre foot day-1 • 1 acre foot / 150 acres = 0.08 inches day-1 !!

  4. Problem Assessment • Greens receive 2-3 X more N than Fairways • Greens typically receive daily irrigation • Low nutrient retention in sand-based greens • 27% of applied P may leach (Shuman, 2001) • 56% of applied N may leach (Snyder, 1984)

  5. Literature Review

  6. Surfactant • HDTMA CH3(CH2)15N(CH3)3

  7. 26-28 Å Sorption Process

  8. Objective:To determine the influence of soil amendments and incorporation method on water use efficiency (WUE) of Tifdwarf bermudagrass Ho: Soil amendments and incorporation method do not increase Tifdwarf WUE above sand:peat

  9. Objective:To determine the influence of surfactant-modified amendments (SMSAs) on N and P leaching in a simulated USGA putting green Ho: SMSAs do not reduce N and P leaching in USGA putting greens

  10. Materials and Methods Water Use

  11. Methods • All pots in each study were maintained at 90% pot capacity • Sprigged with Tifdwarf • Pots were havested and weighed weekly for 18 weeks • WUE = dry matter / applied water • Turf Quality taken weekly (1 to 9) • 10 trts 4 reps RCBD • Duncans MRT α = 0.05

  12. Treatments

  13. Incorporation Method Mixed Profile (85:15) • Aerification (50:50) • 9 Cores • 4 Cores Sand + Amendment Sand + Peat

  14. Materials and Methods N and P leaching

  15. PUMP H2O 30 cm 5 cm 2.54 cm Materials and Methods • Columns • Pb = 1.5 g cm-3 • pH = 7.1 • Injection Solution • pH = 2.5 • NO3-N = 2300 ppm • NH4-N = 2480 ppm • P = 4400 ppm • 10 mL Pump H2O 30 cm Sand/Peat Treatment Layer 5 cm 2.5 cm

  16. Materials and Methods • Treatments: • Sand • Sand/Peat • Ecosand • Soil Master • Profile • HDTMA Ecosand • HDTMA Soil Master • HDTMA Profile • Treatment = 8 • Rep = 3 • Duncans MRT α = 0.05

  17. SMSA Characteristics

  18. Results Water Use

  19. Rootzone Chemical and Physical Characteristics

  20. ANOVA Turf Quality

  21. Turf Quality Full Incorporation a minimum acceptable quality b b c c c c d d e CV = 4.3

  22. Turf Quality 9 Tine Aerification minimum acceptable quality a b bc bc cd de de de ef f CV = 1.9

  23. Turf Quality 4 Tine Aerification minimum acceptable quality a b bc bc bcd d d cd d d CV = 1.8

  24. ANOVA Turf WUE

  25. WUE Full Incorporation a a ab ab b b c c d d CV = 6.8

  26. WUE 9 Tine Aerification a b bc bc bc bc bc bc c c CV = 8.3

  27. WUE 4 Tine Aerification a b b b b b b b b b CV = 9.2

  28. WUE by Incorporation Method CV = 3.5

  29. WUE Summary • Only CCs and Fe Humate increased turf quality • Individually, PAW and CEC are not good indicators of an amendment’s influence on WUE • Fe Humate, CCs, and diatomaceous earths increased WUE above peat • Fe Humate produced the greatest increase in WUE • Amendment influence was decreased after aerification

  30. WUE Conclusion • WUE • Reject Ho and conclude: • Calcined clays, Diat. Earths, smectite, and Fe Humate increased Tifdwarf WUE above sand:peat • Quality • Reject Ho and conclude: • Calcined clays and Fe Humate increased Tifdwarf quality above sand:peat

  31. Practical Implications • When WUE and turf quality are of concern, calcined clays and fe humate are plausible options to peat

  32. Results N and P Leaching

  33. NO3--N Breakthrough Curves Sand Sand/Peat HDTMA-Soil Master AEC = 11.3 Soil Master HDTMA-Profile AEC = 9.7 Profile HDTMA-Clinoptilolite AEC = 4.1 Clinoptilolite

  34. Total NO3-N Leached CV = 9.8 Columns with same letter are not significantly different according to DMRT > 0.05

  35. NH4+-N Breakthrough Curves Sand Sand/Peat HDTMA-Soil Master AEC = 11.3 Soil Master HDTMA-Profile AEC = 9.7 Profile HDTMA-Clinoptilolite AEC = 4.1 Clinoptilolite

  36. Total NH4-N Leached CV = 12.9 Columns with same letter are not significantly different according to DMRT > 0.05

  37. P Breakthrough Curves Sand Sand/Peat HDTMA-Soil Master AEC = 11.3 Soil Master HDTMA-Profile AEC = 9.7 Profile HDTMA-Clinoptilolite AEC = 4.1 Clinoptilolite

  38. Total Phosphorous Leached CV = 6.9 Columns with same letter are not significantly different according to DMRT > 0.05

  39. Leaching Summary • Uncoated amendments: • did not retard or decrease NO3- leaching • eliminated NH4+ leaching • retarded but did not decrease P leaching. • SMSAs reduced NO3-, NH4+, and P leaching

  40. Leaching Conclusion • Reject Ho and conclude: • SMSAs reduce N and P leaching

  41. Future Research • Long-term influence on leaching and stability • Microbial degradation • Influence on turf growth

  42. Acknowledgments • Committee • Jerry Sartain (Chair) • Donald Graetz • Peter Nkedi-Kizza • James Bonczek • Grady Miller • SWSD Grad Students • E. Brown, R. Snyder, K. Makris • Lab Personnel • Ed Hopwood, Nahid Varshovi, Shawron Weingarten, Brian Owens, Martin Sandquist • Florida Turfgrass Association

  43. Questions

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