NITROGEN FERTIGATION OF SUBSURFACE DRIP IRRIGATED BERMUDAGRASS M.A. Maurer* 1, J.A. Moken 2 and J.L. Young 1 1 Department of Agriculture, Stephen F. Austin.

Slides:



Advertisements
Similar presentations
Research Methodology Statistics Maha Omair Teaching Assistant Department of Statistics, College of science King Saud University.
Advertisements

Do In and Post-Season Plant-Based Measurements Predict Corn Performance and/ or Residual Soil Nitrate? Patrick J. Forrestal, R. Kratochvil, J.J Meisinger.
Pesticide Downward Movement in a Bermudagrass System Compared with Movement in a Fallow System H.D. Cummings*, J.B. Weber, R.B. Leidy, F.H. Yelverton,
Phosphorus and Potassium. How is P managed? Key to managing soil and fertilizer P: Knowledge of whether or not the level of soil solution P is adequate.
Interaction of Phosphorus and Dissolved Organic Carbon in Runoff and Drainage Water Ronnie Schnell 1, Donald Vietor 1, Clyde L. Munster 2, Tony Provin.
Irrigation techniques in tomato Previous NextEnd.
Responses of Sweet Cherry Productivity and Soil Quality to Alternate Groundcover and Irrigation Systems Xinhua Yin 1, Xiaolan Huang 1, and Lynn Long 2.
INTRODUCTION Figure 1: Seedling germination success by planting technique plus rainfall amount and date at the Poolesville location during fall BC.
EVALUATION OF PERCOLATION AND NITROGEN LEACHING FROM A SWEET PEPPER CROP GROWN ON AN OXISOL SOIL IN NORTHWEST PUERTO RICO Eric Harmsen, Joel Colon, Carmen.
Nitrate Leaching From Turf Fertilization- A Summary of FDEP-Funded Research Laurie E. Trenholm Urban Turfgrass BMP Specialist UF-IFAS.
Optimizing Crop Management Practices with DSSAT. Our Goal With increasing population and climate change, the ability to maximize crop production is essential.
Mineralization of high-N organic fertilizers L. Sonon, D. Kissel, U. Saha, and SPW Lab Staff Agricultural and Environmental Services Labs. University of.
Using Adapt-N On-farm strip trials on Long Island, NY: Above: A = 93 lb N, G = 159 lb N Below: A = 132 lb N, G = 175 lb N AG AG Incorporating Local Weather.
EFFECT OF HARVEST REMOVAL ON PRODUCTIVITY OF A 15-YEAR-OLD DOUGLAS-FIR PLANTATION. by Dale W. Cole and Jana E. Compton University of Washington and Harvard.
Oklahoma State University Department of Plant and Soil Sciences Oklahoma State University Department of Plant and Soil Sciences Nitrogen Loss from Urea.
Comparison of Granular and Liquid Nitrogen Fertility on 'TifEagle' Bermudagrass F.W. Totten, H. Liu, L.B. McCarty, J. Toler, and C. Baldwin Objective Determine.
Evaluation of Combinations of Bispyribac-Sodium or Amicarbazone with Trinexapac-Ethyl or Paclobutrazol for Annual Bluegrass Control On Creeping Bentgrass.
The Impact of Nanophase Iron-Oxide Coated Clinoptilotite Zeolite On Nutrient Retention in A Sand-Based Root Zone Mix Peter Ampim 1, John Sloan 1, Rajan.
Ministry of Agriculture
NITRATE CONCENTRATION IN DRINKING WATER FROM WELLS AT THREE DIFFERENT LOCATIONS IN NORTHWEST CROATIA Jasna NEMCIC JUREC Milan MESIC Ferdo BASIC Ivica KISIC.
The Purpose of a Fertilizer is to Supply Nutrients.
Introduction Agriculture is a large contributor of non-point source pollution to surface water. Field surface application of manure as a soil amendment.
Plant tissue analysis for testing nutrients deficiency in Mango
Table 4: Percent green cover for trinexapac-ethyl (TE) treated, overseeded plots Number of Simulated Games PGR † Turfgrass Cover (%) A - No.
Residuals and Manure Management for Environmental and Agronomic Benefits Olawale O. Oladeji Soil and Water Science Department University of Florida.
Soil Nutrient Availability Following Application of Biosolids to Forests in Virginia. Eduardo C. Arellano and Thomas R. Fox Department of Forestry, Blacksburg,
Abstract: Low temperature injury, winterkill, and slow spring green-up are common problems facing managers of warm-season putting greens in the transition.
Provide aesthetic and environmental advantages in urban environments Science around the country has provided the best management practices for achieving.
Evaluation of Foliar UAN and Timing on Wheat Grain Yield and Protein Department of Plant and Soil Sciences, Oklahoma State University, 371 Agricultural.
Lawn Turf Color and Density in Relation to Soil Nitrate Concentration Xingyuan Geng, Karl Guillard and Thomas Morris Department of Plant Science and Landscape.
Introduction Proper nutrition at nursery stage is important for desired growth and berry production in grapevine. There are 13 mineral nutrients found.
MODELING THE IMPACT OF IRRIGATION ON NUTRIENT EXPORT FROM AGRICULTURAL FIELDS IN THE SOUTHEASTERN UNITED STATES W. Lee Ellenburg Graduate Research Assistant.
Mandana Tayefe, Ebrahim Amiri, and Azin Nasrollah Zade
St. Augustine Grass Phosphorus Requirement Min Liu Advisor: J. B. Sartain Soil and Water Science The University of Florida May 27, 2005.
Results of Long-Term Experiments With Conservation Tillage in Austria Introduction On-site and off-site damages of soil erosion cause serious problems.
Citrus production in Florida accounts for 68 % of national production. Citrus trees must be irrigated to reach maximum production owing to: 1) uneven rainfall.
Consequences of Aluminum or Ferrous Sulfate Amended Poultry Litter on Concentrations of Aluminum in Plant and Soil Sosten Lungu, Haile Tewolde and Dennis.
Unit Factors Affecting Nitrates in Groundwater.. 1. Examine the processes of the nitrogen cycle. 2. Identify the source for most chemical nitrogen fertilizers.
Projected Deliverables: Estimates of N losses due to leaching, volatilization, and uptake by competing understory vegetation Determine the relative efficiency.
Optimizing Nitrogen and Irrigation Timing for Corn Fertigation Applications Using Remote Sensing Ray Asebedo, David Mengel, and Randall Nelson Kansas State.
IRRIGATION SCHEDULING AND TECHNIQUES IN BANANA NextEnd.
Soil Nitrogen Unit: Soil Science.
Savoy,*H.J. 1, Leib, B. 1, and Joines, D. 2 1 Associate Professors, University of Tennessee, Biosystems Engineering and Soil Science, Extension 2. Manager,
Development of Vegetation Indices as Economic Thresholds for Control of Defoliating Insects of Soybean James BoardVijay MakaRandy PriceDina KnightMatthew.
Mixture of Saline and Non-Saline Irrigation Water Influences Growth and Yield of Lettuce Cultivars under Greenhouse Conditions A. A. Alsadon, M. A. Wahb-allah,
Figure 3. Concentration of NO3 N in soil water at 1.5 m depth. Evaluation of Best Management Practices on N Dynamics for a North China Plain C. Hu 1, J.A.
Effect of Compaction of Soil Surface to Increase Herbicide Effect in Upland Rice Cultivation By THAN TOE DEPUTY SUPERVISOR MYANMAR AGRICULTURE SERVICE.
Figure 2. Main effects for perennial ryegrass overseeding on trafficked ‘Tifway’ bermudagrass, Knoxville, TN LSD (0.05) = ns LSD (0.05) = 6.5 LSD.
LATE SEASON N APPLICATIONS FOR IRRIGATED HARD RED WHEAT PROTEIN ENHANCEMENT. S.E. Petrie*, Oregon State Univ, B.D. Brown, Univ. of Idaho. Introduction.
EVALUATION OF LAMBDA STAR IN THE CONTROL OF APHIDS ON KALE. BY JOSPHINE W. NJOGU REG NO.A138/10309/2007.
The nitrogen cycle in turfgrass can be quite complex. Nitrate is taken up through the roots, converted into protein in the leaves, recycled as ammonium.
IRRIGATION TECHNIQUES IN TOMATO
Branka Bračič Železnik 1, Barbara Čenčur Curk 2 THE INFLUENCE OF CLIMATE VARIATIONS ON NATURAL BACKGROUND OF NITRATE IN PERCOLATED WATER 1 Public Water.
 Greater flexibility in application of fertilizers does not depend on the climatic conditions such as rain and soil condition.  Frequent and small applications.
Categorizing Nitrogen Availability for Corn Fields Using Field History and Cornstalk Nitrate Test Haiying Tao 1, Thomas Morris 1, Suzy Friedman 2, Richard.
IRRIGATED CORN RESPONSE TO NITROGEN FERTILIZATION IN THE COLORADO ARKANSAS VALLEY Ardell Halvorson 1, Frank Schweissing 2, Michael Bartolo 2, and Curtis.
NITROGEN FERTILIZATION SOURCE and MICRONUTRENTS IMPACT on CARROT (Daucus carota L.) YIELD Mohamed A. Soliman 1, Mohamed W. M. Elwan 1, Khalid E. Abd El-Hamed.
N, P, and K Uptake in Bread Wheat ‘Pavon 76’ and Its 1RS Translocation Lines J.Giles Waines, Bahman Ehdaie, Toan Khuong, and Andrew P. Layne Department.
Nitrogen Spatial Distribution in a Sandy Soil Cropped with Tomatoes under Seepage Irrigation Shinjiro Sato Monica Ozores-Hampton.
Hero Gollany USDA-ARS Pendleton, OR NUE Conference - August 8-10, 2016.
Integrated Nutrient Management (Nutrient Management Plan ) A Series of Lecture By Mr. Allah Dad Khan.
Li Li and Dr. Joseph Young Preliminary conclusion
NDVI Active Sensors in Sugarbeet Production for In-Season and Whole Rotation Nitrogen Management.
Fig 1: Nitrogen fertilizer application at V7.
Dhurba Neupane1, Juan Solomon2 and Jay Davison3
C. Kallenbach1. , W. Horwath1, Z. Kabir1, J. Mitchell2, D
Soil Formation Soil horizons - layers of soil renewal
WM869 Results: Nitrate-N Leaching Losses from Lawngrasses
Evaluation of Midseason UAN Application Depth in Winter Wheat
E.V. Lukina, K.W. Freeman,K.J. Wynn, W.E. Thomason, G.V. Johnson,
Presentation transcript:

NITROGEN FERTIGATION OF SUBSURFACE DRIP IRRIGATED BERMUDAGRASS M.A. Maurer* 1, J.A. Moken 2 and J.L. Young 1 1 Department of Agriculture, Stephen F. Austin State University, P.O. Box 13000, SFA Station, Nacogdoches, TX Department of Environmental Science, Stephen F. Austin State University, P.O. Box SFA Station, Nacogdoches, TX ABSTRACT The effects of five nitrogen fertigation rates (0, 12.2, 24.4, 48.8, 97.7 kg N·ha -1 ·month -1 ) and three fertigation frequencies (weekly, bi-monthly, monthly) on 'Tifway 419' hybrid bermudagrass (Cynodon dactylon x C. transvaalensis) were studied, using a combination of subsurface drip irrigation (SDI) and fertigation with urea ammonium nitrate (UAN, ) as the nitrogen source. Soil analysis showed soil nitrate levels to exceed 10 mg·L -1 in the 48.8 and 97.7 kg N·ha -1 ·month -1 rates. This led to excessive leaching in nitrate and nitrite over EPA limits at these rates as well as the 24.4 kg N·ha -1 ·month- 1 rate. Leaf tissue analysis showed the fertigation rates of 12.2 kg N·ha -1 ·month -1 and up had nitrogen levels between the 3-5% sufficiency range. This research indicates that a fertigation rate of 12.2 kg N·ha -1 ·month -1 produced sufficient quality turfgrass and maintained leachate levels below EPA limits. Even though frequency did not play a statistically significant role in this study, it is recommended that a frequency of 7 to 14 days be used when sandy or sandy-loam soil is being used. INTRODUCTION Irrigation and fertilization are two essential processes for obtaining optimum quality turfgrass. However, resulting environmental impact and increasing droughts call for more efficient and less polluting means of fertilization and irrigation. Subsurface drip irrigation in combination with fertigation may be the answer. When compared to conventional irrigation methods, SDI has been shown to reduce water usage by 33-55%. Fertigation can reduce nitrogen leaching through smaller and exact applications and when applied through SDI it can reduce fertilizer loss through surface runoff. This combination places both water and nutrients directly at the root zone of the turfgrass increasing efficiency and maximizing uptake. This study was designed to look at a wide range of fertigation rate and frequency combinations to minimize nitrate leaching levels below EPA limits while still producing quality turfgrass. MATERIALS & METHODS The study was conducted at the Stephen F. Austin State University (SFASU) Mast Arboretum with the experimental set up and sodding of the ‘Tifway 419’ hybrid bermudagrass in the Fall of 2007 and data collection being performed during the 2008 growing season. Treatments were arranged as 3 fertigation frequencies (monthly, bi-monthly, weekly) X 5 nitrogen fertigation rates (0, 12.2, 24.4, 48.8, 97.7 kg N·ha -1 ·month -1 ) factorial design with 4 replicates per treatment to form a completely randomized block design experiment. Nitrogen applications began on March 28, 2008 with all treatments receiving their appropriate UAN dosage. To see the variation in nitrate levels due to the UAN application, an intense four-week soil sampling was performed during the 2008 growing season (July 23rd through August 16th 2008). Two leachate collections were made prior to this intense soil sampling (April 1st, and May 7th) and one during (August 12th) to see the amounts of nitrate and nitrite being leached and compare them to the EPA limits of 10 mg·L -1 and 1 mg·L -1 respectively. A biomass collection and several visual quality ratings were performed throughout the 2008 growing season to analyze the health of the turfgrass. Two and three way analysis of variance (ANOVA) were performed on the collected data using the Statistical Analysis Software (SAS ® ) general linear model (GLM) procedure at the 0.05 probability level with the Tukey multiple-comparison test used to determine differences in means between the treatments. RESULTS & DISCUSSION Soil analysis showed large amounts of nitrate-nitrogen being retained in the soil and not being utilized by the turfgrass at rates of 48.8 and 97.7 kg N·ha -1 ·month -1 (Table 1). During a natural rain event (August 18, 2008) resulting in 8.28 cm of precipitation, this large buildup of nitrate-nitrogen in the soil was leached causing excessive nitrate-nitrogen leachate over the EPA limits (Table 2). The first two water samples were taken early in the growing season when the applied nitrate-nitrogen was not being effectively used by the turfgrass. This led to higher nitrate-nitrogen leachate values in the lower 12.2 and 24.4 kg N·ha -1 ·month -1 rates which lowered significantly once the turfgrass was fully established. Leaf tissue analysis showed only the control as having a deficiency in nitrogen. The other four rates had leaf tissue nitrogen percentages between the 3-5% sufficiency range for a fairway turfgrass. Visual quality ratings showed the 24.4 and 48.8 kg N·ha -1 ·month -1 rates having the highest turfgrass color and thickness quality. The 12.2 kg N·ha - 1 ·month -1 showed visual deficiency symptoms and the 97.7 kg N·ha - 1 ·month -1 rate had some leaf firing. Both these rates however did still produce an acceptable quality turfgrass. CONCLUSIONS Results from the study indicate that a fertigation rate of 12.2 kg N·ha - 1 ·month -1 produced a quality turfgrass while minimizing nitrate- nitrogen leaching to a level at or below EPA limits in sandy-loam soil. Optimum quality was obtained at the 24.4 and 48.8 kg N·ha - 1 ·month -1 rates. This range is currently recommended for optimum bermudagrass quality and growth. However, in this study, the 24.4 and 48.8 kg N·ha -1 ·month -1 rates produced nitrate leachate levels that were well above EPA limits. These rates may have produced such high nitrate leaching values due to the limited root zone and soil profile of only 30 cm. If a deeper soil profile of had been used, leachate values may not have been as high. Even though fertigation frequency was not statistically significant in this study, a frequency of 7 to 14 days should be used in order to minimize the amount of nitrate and nitrite that can be leached at any one time. A monthly frequency allows for larger amounts of nitrogen leaching if a rainfall or large irrigation event were to occur right after application. Also, the monthly frequency had excessive nitrate leaching above EPA limits at all rates except the control. Table 1. Weekly soil nitrate-nitrogen levels (mg·L-1) at 0 to 15 and 15 to 30 cm soil depths over a one month fertigation cycle (28 days). Table 2. Levels of nitrate-nitrogen (kg N·ha -1 ·month -1 ) following rainfall events taking place 4, 16, and 26 days after initiation of three separate fertigation cycles (28 days). Blue coloring shows values below EPA limit of 10 mg·L -1 orange exceeds this limit. May 12, 2008