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Methods to Improve Nutrient Use Efficiency in Rice 6R2/Room 4 Tuesday 11:1011:56 Wednesday 10:1010:56 Timothy W. Walker, Ph. D. Associate Agronomist 6628222291

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  • Methods to Improve Nutrient Use Efficiency in Rice

    6R‐2/Room 4Tuesday 11:10‐11:56

    Wednesday 10:10‐10:56

    Timothy W. Walker, Ph. D.Associate Agronomist

    662‐822‐2291

  • Nitrogen Use Efficiency

    NUE =          Grain yield (lb/acre)Nitrogen applied (lb/acre)

  • Nitrogen Use Efficiency

    Yield

    Genetics

    Variety Selection Breeding

    Management

    Agronomic Pest

  • Nitrogen Use Efficiency

    N Rate

    Decrease N Rate

    Account for Soil Supply

    N‐ST*R (U of A)

    Rate Response

    Account for Plant Need

    Chlorophyll Plant Area BoardSensor‐based

    Maintain N Rate

    Prevent Loss

    Ammonia

    Agrotain Water

    Nitrate

    Water Nitrification Inhibitors

  • Nitrogen Use EfficiencyMaintain N 

    Rate

    Prevent Loss

    Ammonia

    Agrotain Water

    Nitrate

    Water Nitrification Inhibitors

  • Urea’s Reaction ProducesNH3 Gas

    2 NH3 ammonia gas on soil surfaceor in flood

    - H2O & CO2

    CO(NH2)2 (NH4)2CO3 2 NH4+ + 2 OH-

    urea urease (pH ~ alkaline) ammonium salt in soil

    Note: Urea’s reaction in soil initially is alkaline and increases soil pH causing ammonia volatilization loss if not incorporated in soil quickly.

    Slide borrowed from R. Norman

  • Ammonia Volatilization of Urea Applied to a Conventional Tilled and a Stale-Seedbed Silt loam soil (RREC, 2001)

    [N source LSD0.05 = 3.1% of applied N]

    0

    5

    10

    15

    20

    25

    30

    35

    0 5 10 15 20 25

    Time (days)

    Vola

    tiliz

    atio

    n (%

    of a

    pplie

    d N

    )

    Ammonia VolatilizationEnds at ~10 Days

    ↓Stale-Seedbed

    Conventional Till

    Griggs etal., 2007; SSSAJ

    Slide borrowed from R. Norman

  • Ammonia Volatilization of 15N-labeled Urea and Ammonium Sulfate From a Perry Clay Soil14 Days before Flooding (SEREC, 2000)

    0

    5

    10

    15

    20

    25

    30

    0 2 4 6 8 10 12 14 16 18 20 22

    Time (days)

    Vol

    atili

    zatio

    n (%

    of a

    pplie

    d N

    )

    Ammonium Sulfate Urea

    Urea

    Ammonium Sulfate

    Ammonia Volatilization Losses(Clay soil)

    Flood

    Griggs et al., 2007; SSSAJ

    Slide borrowed from R. Norman

  • Rice Research Station – fertility and Agronomy Project

    i

    e-h d-h

    a

    a-d a-da-e a-c

    y = 520.4x + 6697.5

    5000

    5500

    6000

    6500

    7000

    7500

    8000

    8500

    9000

    9500

    10 DPF 7 DPF 4 DPF 1 DPF

    Yie

    ld (l

    b/A

    )

    Application time (Days Prior to Flooding)

    UreaAgrotain-UreaLinear (Urea)

    581 lbs7 %

    1238 lbs15 %

  • Rice Research Station – fertility and Agronomy Project

    0

    5

    10

    15

    20

    25

    3 6 9 12 15 18 21

    NH4‐N lo

    ss (%

     of t

    otal 

    applied)

    Time (days)

    UreaAS‐UreaASSuper‐UAgrotain‐Urea

  • Rice Research Station – fertility and Agronomy Project

    (Urease inhibitor only) (Urease and nitrification inhibitors)

    a-d a-da-e a-c

    c-gb-f b-f

    a-c

    5000

    5500

    6000

    6500

    7000

    7500

    8000

    8500

    9000

    10 DPF 7 DPF 4 DPF 1 DPF

    Yie

    ld (l

    b/A

    )

    Application time (Days Prior to Flooding)

    Agrotain-UreaSuper-U

  • Ammonia Volatilization

    0

    2

    4

    6

    8

    10

    12

    0 5 10 15 20

    % of a

    pplied

    Days

    NH3 Volatilization Loss

    urea

    ams

    agrotain

    Data from Tunica clay.  Dillon and Walker, unpublished

  • Urea vs Agrotain

    LSD = 7Source x Timing (P = 0.0024)

    8224

    8566

    8269

    8599

    7806

    8361

    8500 8452

    7400

    7600

    7800

    8000

    8200

    8400

    8600

    8800

    10 7 4 1

    lb/acre

    AgrotainUrea

    LSD = 453

  • Urea vs Agrotain

    LSD = 7Source x Timing (P = 0.0024)

    7420

    7818

    7586

    7155

    7860

    7710

    6800

    7000

    7200

    7400

    7600

    7800

    8000

    10 7 2

    AgrotainUrea

    LSD = 361

  • Agrotain vs Super U

    LSD = 7Source x Timing (P = 0.0024)

    8224

    8566

    8269

    8599

    8056

    8488

    8113

    8331

    7700

    7800

    7900

    8000

    8100

    8200

    8300

    8400

    8500

    8600

    8700

    10 7 4 1

    AgrotainSuper U

    LSD = 453

  • Testing the Mechanism – Product Evaluation

    • Agrotain is the only ureaseinhibitor recommended in Arkansas.

    • Other products unproven to inhibit NH3 loss include– Nutrisphere– N‐Zone– Extend– Upgrade

  • Lab EvaluationUpgrade

    05

    1015202530354045

    0 5 10 15

    Cumulative NH3Loss 

    (% of a

    pplied N‐fe

    rtilizer)

    Time (days)

    Urea Agrotain‐Urea Upgrade‐Urea

    Source: Norman and Roberts (unpublished data) 

  • Lab EvaluationN‐Zone

    08

    16243240485664

    0 5 10 15

    Cumulative NH3Loss 

    (% of a

    pplied N‐fe

    rtilizer)

    Time (days)

    Urea Agrotain‐Urea N‐Zone‐Urea

    Source: Norman and Roberts (unpublished data) 

  • Lab EvaluationNutrisphere

    08

    16243240485664

    0 5 10 15

    Cumulative NH3Loss 

    (% of a

    pplied N‐fe

    rtilizer)

    Time (days)

    Urea Agrotain+Urea Nutrisphere+Urea Ammonium Sulfate

    Source: Franzen et al. (2011, in press) J. Plant Nutr.0.25% Nutrisphere added

  • Lab EvaluationExtend

    05

    1015202530354045

    0 5 10 15

    Cumulative NH3Loss 

    (% of a

    pplied N‐fe

    rtilizer)

    Time (days)

    Urea Agrotain‐Urea Extend‐Urea

    Source: Norman and Roberts (unpublished data) 

  • Nitrification/Denitrification

    2NH4+ + 3O2 2NO2‐ + 2H2O + 4H+Nitrosomonas

    2NO2‐ + O2 2NO3‐Nitrobacter

    NO3‐ + H2O                             NO, N2O, N2 (gases)Permanent Flood

  • Nitrogen Stabilizers

    113

    131137

    164

    100

    110

    120

    130

    140

    150

    160

    170

    180

    10 DBF 2 DBF

    bu/ac 60120

  • Urea Conversion to NO3‐

    Time (days)

    0 3 6 9 12 15 18 21 24 27

    NH

    4 rem

    aini

    ng (%

    of i

    nitia

    l)

    0102030405060708090

    100110

    DulaneyF13SF14WalkerCircleHLADavis

  • Urea Conversion to NO3‐

    Soil A K T1/2 R2

    ‐‐‐‐‐‐‐‐‐‐%‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐d‐1‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐d‐‐‐‐‐ ‐‐Unit less‐‐

    LA 106.3244 (8.6832) 0.1046 (0.0187) 6.6 0.945

    F13S 98.1749 (5.0216) 0.0840 (0.0095) 8.3 0.971

    Dulaney 92.3076 (8.0813) 0.0708 (0.0139) 9.8 0.910

    Davis 101.8352 (7.4631) 0.1353 (0.0218) 5.1 0.961

    CircleH 103.3625 (7.8772) 0.1447 (0.0242) 4.8 0.960

    F14 105.0458 (7.1418) 0.1573 (0.0236) 4.4 0.970

    Walker 96.3323 (5.5211) 0.1672 (0.0212) 4.1 0.977

  • Nitrification Rate of UreaNitrification of Urea in two Soils

    Days0 5 10 15 20 25 30 35

    % u

    rea-

    N a

    s N

    O3-

    N

    0

    20

    40

    60

    80

    100

    120

    Calhoun soilDewitt soil

    Unpublished data: Golden et al. (2009)Slide borrowed from R. Norman

  • Grain Yield

    LSD = 7Source x Timing (P = 0.0024)8218

    8071 8041 8069

    8235

    7467

    7642

    7858

    7994

    7000

    7200

    7400

    7600

    7800

    8000

    8200

    8400

    43% Urea ENTEC Super U Agrotain

    2DBF10DBF

    LSD = 421

    Data collected at DREC2010

    Sharkey clay soil

  • Nitrification InhibitorNutrisphere

    05

    101520253035404550

    Soil Inorganic N (p

    pm)

    NO3‐N NH4‐N

    Source: Franzen et al. (2011, in press) J. Plant Nutr.90 lb urea‐N/acre; LSD0.05 (8.4 ppm for NO3 and 4.5 ppm for NH4)Data from Hazelton, North Dakota)

  • Sensor‐based

  • 1NUE Fixed = 35%NUE Sensor = 38%

    $ Fixed = $447$ Sensor = $446

  • Commercially Available Active Sensors

    Photo courtesty of B. Tubana

  • Rice Info on the Webwww.rice.msstate.edu

  • Special Thanks

    • Dr. Dustin Harrell• Dr. Brenda Tubana• Mr. Kevin Dillon• Mr. Paxton Fitts• Dr. Rick Norman• Dr. Nathan Slaton• Dr. Bobby Golden• Dr. Trent Roberts

  • Special Thanks