nutrient management strategies for ca ludhiana july 2011

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    Nutrient Management Strategies forConservation Agriculture Systems:Nutrient Expert

    Conservation Agriculture: Nurturing Sustainable Production Systems in South Asia, Ludhiana, July 5, 2011

    Kaushik Majumdar,Director, IPNI-South Asia Program

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    Conservation Agriculture and nutrientmanagement

    Challenges of nutrient management in CA

    Nutrient Expert

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    Conservation Agriculture systems of production aredefined by three key principal elements

    No mechanical tillage and minimal soil disturbance;

    Permanent organic soil cover specially by plant organicmatter and cover crops;

    Diversified crop rotations in the case of annual crops orcrop associations in case of perennial crops, includinglegumes

    These three elements in various combinations aim at establishing

    and sustaining healthy soil systems that can offer the best crop andlivestock productivities and environmental services within theprevailing ecological and socio-economic conditions whileoptimizing the use of agrochemicals with biological interventions

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    Framework of Nutrient management practices in CAsystems :

    (i) the biological processes of the soil are enhanced and protected sothat all the soil biota and microorganisms are privileged and that soilorganic matter and soil porosity are built up and maintained;

    (ii) there is adequate biomass production and biological nitrogenfixation for keeping soil energy and nutrient stocks sufficient tosupport higher levels of biological activity, and for covering the soil;

    (iii) there is an adequate access to all nutrients by plant roots in the

    soil, from natural and synthetic sources, to meet crop needs;

    (iv) the soil acidity is kept within acceptable range for all key soilchemical and biological processes to function effectively.

    Kassam and Friedrich, 2009

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    Soil Physical properties and CA

    Lower bulk density in CA systems as compared toconventionally tilled plots

    Wet tillage increases bulk density

    Destruction of soil aggregates

    Filling of micropores with finer soil particles

    Direct physical compaction caused by implements

    Lesser soil penetration resistance in CA systems

    Support higher soil aggregation

    Reduced soil disturbance

    Increased soil organic matter

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    Other changes associated with CA

    Greater crop residues accumulate on soil surface

    Minimized wind and water erosion

    Reduced nutrient loss through erosion

    Reduced evaporation loss

    Increased water infiltration

    Lower surface temperature

    Cooler soil temperature

    Slow nutrient release from soil organic matter

    Reduced diffusion of nutrients to the plant roots

    Slower mineralization

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    Effect of conventional tillage and no-till on grain yieldand N uptake by maize (Moschler & Martens, 1975)

    The grain yield response curvesare typical of what is obtained inseveral studies

    No till yields are higher at highernitrogen levels

    More efficient utilization ofnutrients in no till production

    Lower grain yields and N uptakewith no-till at lower N rates canresult from greater immobilization of

    fertilizer N, losses of N fromdenitrification and leaching, lowermineralization of N or a combinationof these factors.

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    Average yield (kg/ha) and yield loss (kg/ha) in PuddledTransplanted Rice (PTR) and Direct Seeded Rice (DSR) inthe hubs of Indo-Gangetic Plain (2010)

    NPK Reduced N

    Full PK

    N Omission Reduced P

    Full NK

    P Omission Reduced K

    Full NP

    K Omission Reduced

    PK Full N

    Zn

    OmissionHaryana PTR (n=8)

    Yield 4871 4063 3569 4413 4172 4306 4124 4264 4642

    Yield

    loss

    _ 808 1302 458 699 565 747 607 229

    Haryana DSR (n=8)

    Yield 5132 4132 3528 4438 4260 4646 4354 4344 4911

    Yield

    loss

    _ 1000 1604 694 872 486 778 788 221

    Punjab PTR (n=5)

    Yield 4396 3576 2647 3622 3478 3751 3700 3691 3873

    Yield

    loss

    _ 820 1749 774 918 645 696 705 523

    Punjab DSR (n=4)

    Yield 6053 4625 3775 4683 4572 4989 4889 4556 5219

    Yield

    loss

    _ 1428 2278 1370 1481 1063 1164 1497 834

    NPK NOmission

    Reduced PFull NK

    P Omission Reduced KFull NP

    K Omission Reduced PKFull N

    Addnl. NP

    Bihar PTR (n=6)

    Yield 3418 1883 3234 3164 3273 3213 3196 3358

    Yield

    loss

    _ 1535 184 254 145 205 222 60

    Bihar DSR (n=6)

    Yield 3507 1937 3308 3246 3327 3293 3246 3422

    Yieldloss _ 1570 199 261 180 214 261 85

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    Challenges in nutrientmanagement in CA

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    Challenges

    High organic matter

    Higher microbial population (immobilization of nutrients) Lower mineralization as less surface area is exposed to microbial action (residue

    exists as undisturbed mulch)

    High microbial population

    High population of nitrifiers but higher population of denitrifiers (gaseous N loss) Requirement of denitrification

    Easily available organic substrate

    Nitrate

    Suitable organism

    Existence of large aggregates

    High moisture content

    Better soil aggregation

    Deep penetration and leaching of water

    Loss of NO3- and K+ with water

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    Nitrogen

    Immobilization

    Residue load

    C:N ratio of residue

    Mineralization

    Soil temperature

    Exposure of organic matter for decomposition

    Denitrification

    Population of denitrifier

    Microsites of oxygen deficit

    Leaching

    Higher moisture content

    Larger aggregate sizes

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    N immobilization and mineralization followingaddition of residue to soil (Havlin et al., 2005)

    Rapid increase in the number ofheterotrophic organisms at initial stage offresh organic matterdecomposition.elevated CO2 evolution.

    High C:N.insufficient N in thesubstratemicrobes will draw on the

    mineral nitrogen leading to immobilization

    C:N ratio will start decreasing as thedecay proceeds.C released as CO2while N immobilized from soilsolution.mineralization of N

    A combination of high C:N ratio and lowsoil N is expected to reduce N availabilityto plants at initial stages of crop growth

    Crops planted immediately after cerealresidue retention will require sufficient

    external N application

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    Residue decomposing and N, P and K releaseat three wheat growth stages

    Yadvinder Singh et al., 2010

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    Phosphorus and Potassium

    Soil P and K tend to be immobile in the soil Nutrient stratification is an important concern in the

    management of P and K in zero-till systems.

    Without tillage and soil mixing, P and K may accumulate

    at the soils surface (0-5 cm) at the depth of application When soil conditions are dry, nutrients near the surface

    may be positionally unavailable for plant uptake

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    Effect of zero and conventional tillage on distributionof P and K in a silty clay soil in Manitoba (adapted fromGrant and Bailey 1994)

    0 5 10 15 20 25 30 35 40 45

    300

    400

    500

    600

    700

    800

    9001000

    1100

    1200

    1300

    Depth, cm.

    Potassium,m

    g/kg

    Silty Clay Soil

    Conventional Till

    Zero Till

    0 5 10 15 20 25 30 35 40 45

    0

    10

    20

    30

    40

    50

    60

    70

    Conventional Till

    Zero Till

    Depth, cm.

    Phosphorus

    ,mg/kg

    Silty Clay Soil

    0 5 10 15 20 25 30 35 40 45

    300

    400

    500

    600

    700

    800

    9001000

    1100

    1200

    1300

    300

    400

    500

    600

    700

    800

    9001000

    1100

    1200

    1300

    Depth, cm.

    Potassium,m

    g/kg

    Silty Clay Soil

    Conventional Till

    Zero Till

    0 5 10 15 20 25 30 35 40 45

    0

    10

    20

    30

    40

    50

    60

    70

    Conventional Till

    Zero Till

    Depth, cm.

    Phosphorus

    ,mg/kg

    Silty Clay Soil

    Soil samples were taken at the end of a 4-year study where P was banded (58 kgP2O5/ha) and K was broadcast (120 kg K2O/ha)

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    Nutrient Management in ConservationAgriculture

    Soil physical, chemical and biological environment ofconservation systems are different from conventional system

    High residueextra N demand by microorganisms for decomposition

    of residues and have the potential of higher immobilization and slowermineralization of N

    P supply may not be adequate at initial stages and may depend onexternal supply

    Greater supply of K from residues are expected but losses throughleaching must be accounted for while estimating requirement

    Wetter and cooler soils will influence rate and mechanism of nutrientrelease/loss

    Additional stored water increases yield potential and will require greatersupply of nutrients

    Data from long term stabilized systems are lacking

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    Indigenous Nutrient Supply in ZT & CT

    State Haryana Punjab

    Scenarios ZT CT ZT CT

    Treatments Wheat Yield (kg/ha)

    Full NPK yield 5078 4800 4741 4865

    Yield loss due to N 3155 2994 1355 1457

    Yield loss due to P 1002 711 518 714

    Yield loss due to K 817 675 270 852

    Nutrient rates(kg/ha)

    N P2O5 K2O

    180 90 100

    ZT Zero tillage with residue retentionCT Conventional tillage with complete residue removal

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    Fertilizer Placement

    Fertilizer placement decision is critical to optimizefertilizer use efficiency by the crop in no-till conditions

    Broadcasting N onto the residue covered surface is notthe most efficient method of application

    potential for immobilization by surface residues volatilization losses of N

    In-soil band placement of N is usually the most effectivemeans of minimizing immobilization of N in no-till crops

    The application of P and K in bands either with, or closeto the seed minimizes tie-up by the soil and increasesearly season uptake by the crop

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    Applying the crops entire fertilizer requirements

    at seeding can be challenging

    Placement of high amounts of nutrients directly with the seed oftencauses reduced germination and delayed emergence resulting inpoor stands and yield loss.

    Row spacing, seed bed utilization (SBU), soil texture, soil moisture,soil variability, fertilizer placement, seed furrow opener, fertilizersource, and crop influence how much fertilizer can be safely appliedwith the seed

    The amount of fertilizer that can safely be applied in the seed row decreases asrow spacing increases. With wider rows, at a given rate per hectare the fertilizeris more concentrated and is in greater contact with the seed

    Heavier textured soils tolerate more seed row N because the increased cationexchange and water holding capacity reduce ammonia toxicity

    Ammonium nitrate is less damaging to the seed than urea. It has a higher saltindex than urea, but does not add to ammonia toxicity

    Higher rates of N may be tolerated if CEC is high and seedbed moisture issufficient

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    Nutrient Expert

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    Objectives of CSISA required a focused, time-boundapproach for tool development

    Capability to take forwardimproved nutrient managementrecommendation across largeareas

    Rice-Rice and Rice-Wheat

    accounts for about 16 millionhectares in India only

    Opportunities to work with morepartners and extending soundnutrient management information

    through multiple channels

    Output: Partnerships and dissemination tools in place for reaching numerous farmers

    Indicator of success: Local extension persons contacting farmers with correct message

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    Drivers of Nutrient Expert Developmentin India

    Requirement of dissemination tool for large scaleadoption of SSNM in areas practicing generalizedfertilizer recommendation, including CSISA operationalarea

    Requirement of a nutrient management DSS that canhandle differing tillage and residue managementscenarios

    Scope for developing NE in Rice, Maize and Wheat in asystem perspective

    Support from partner Institutes and scientists for NE

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    How did we proceed to develop NutrientExpert for Wheat and Maize

    Rigorous in-house discussion on the framework of NE

    Field visits across growing areas to understand the productionsystem and growing conditions

    Intensive discussion with NARES, University, CG Institutescientists to modify/improve the developed framework

    Use of local experimental data and one-on-one contact withnational scientists to optimize input parameters

    Validation trials with wide range of partners and in-season fieldvisits to understand performance of the tool against existing

    practices

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    Overview A new, computer-based decision support tool

    developed to assist local experts to quickly formulate

    fertilizer guidelines for wheat and tropical hybrid

    maize

    Follows the principles of site-specific nutrient

    management (SSNM) (Witt et al. 2009)

    Allows scientists and extension experts to jointlydevelop novel nutrient management strategies for

    evaluation

    Nutrient Expert for Wheat and Hybrid Maize

    C. Witt, J.M. Pasuquin, M.F. Pampolino, R.J. Buresh, and A. Dobermann. 2009. A manual for the development and participatory

    evaluation of site-specific nutrient management for maize in tropical, favorable environments. International Plant Nutrition

    Institute, Penang, Malaysia. http://seap.ipni.net

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    Nutrient Expert for wheat and Hybrid Maize helps to: Evaluate farmers current nutrient management practices

    Develop an optimal planting density (Maize) for a location

    Set a meaningful yield goal based on attainable yield

    Estimate fertilizer NPK rates required for the selected yield

    goal

    Translate fertilizer rates into available fertilizer sources

    Develop an application strategy for fertilizers (right rate, right

    source, right location, right time)

    Compare costs and benefits between the farmers current

    practice and the recommended practice

    What can the software do?

    Nutrient Expert for Wheat

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    Nutrient Expert for WheatVersion 1.0 Settings About Help Exit

    Nutrient Expert for wheat helps you to: evaluate current nutrient management practices determine a meaningful yield goal based on attainable yield estimate fertilizer NPK rates required for the selected yield goal translate fertilizer NPK rates into fertilizer sources develop an application strategy for fertilizers (right rate, right source, right location, right time), and compare the expected or actual benefit of current and improved practices.

    CurrentFFP & Yield

    SSNMRates

    Sources &Splitting

    ProfitAnalysis

    To start, click a button

    First time user? Working in a new location? Make sure to have the Settings right!

    Developed in 2010 for validation in 2010-11 wheat season

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    Nutrient Expert for wheat validation

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    Wheat NE Validation Results

    State Tillage Cropping System NutrientExpert

    StateRecommendation

    Farmers

    Practice

    Bihar(n = 11)

    Conventional Rice-Wheat 3898 3267 3632

    UttarPradesh(n = 16)

    Conventional Pearl millet-Wheat 5640 5224 5848#

    Haryana

    (n = 15)

    Conventional Rice-Wheat 4744 4528 4189

    Haryana(n = 15)

    Zero till Rice-Wheat 5072 4722 4439

    Punjab(n = 6)

    Conventional Rice-Wheat 4881 4219 4031

    Punjab

    (n = 8)

    Zero till Rice-Wheat 5050 4404 4198

    Punjab(n = 4)

    Zero till Cotton-Wheat 5700 5050 4583

    Punjab(n = 4)

    Conventional Cotton-Wheat 5117 4867 4208

    # Ample NPK application treatment, part of omission plot studies

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    Nutrient Expert for Hybrid Maize-South Asia

    Ready for validation trials in coming rainy season

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    Farmers yield will be used : as basis for suggesting a yield goal for estimating benefits in Profit Analysis

    Farmers fertilizer practice will be used: for estimating costs in Profit Analysis

    Farmers Fertilizer Practice

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    Suggested fertilizer splitting(rates and timing)

    Fertilizer rates are adjusted to field size

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    [email protected]:www.ipni.net

    mailto:[email protected]://www.ipni.net/http://www.ipni.net/mailto:[email protected]