Iowa Senate Natural Resources Committee February 3, 2015

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Transcription:

Iowa Senate Natural Resources Committee February 3, 2015 Dr. Matthew Helmers Dean s Professor, College of Agriculture & Life Sciences Professor, Department of Agricultural & Biosystems Engineering mhelmers@iastate.edu, (515) 294-6717 Dr. Michael Castellano Assistant Professor, Department of Agronomy castelmj@iastate.edu, (515) 294-3963 1

Soil Nitrogen Cycling & Budgeting Dr. Michael Castellano Department of Agronomy 2

Corn Grain Harvest (~100 lbs N/acre/year) Corn Residue Return (~65 lbs N/acre/year) Corn Nitrogen Cycling & Budget Corn Nitrate Use (~165 lb N/acre) Gaseous Loss (~10 lbs N/acre/year) Fertilizer to Corn (~150 lbs N/acre/year) Native Soil Organic Matter Nitrogen ~ 10,000 lb N/acre Microbial production of nitrate from native soil (100-400 lbs N /acre/year) Microbial re-uptake of nitrate (150-350 lbs N/acre/year) NITRATE Nitrate leaching to water (~30 lbs N/acre/year) 3

Soybean Grain Harvest (~165 lbs N/acre/year) Soybean Residue Return (~65 lbs N/acre/year) Soybean Nitrogen Cycling & Budget Soybean Nitrogen Use (~230 lb N/acre) Soybean Nitrate Use (~130 lb N/acre/year) Atmospheric Fixation (~100 lbs N/acre/year) Gaseous Loss (~2 lbs N/acre/year) Native Soil Organic Matter Nitrogen ~ 10,000 lb N/acre Microbial production of nitrate from native soil (100-400 lbs N /acre/year) Microbial re-uptake of nitrate (150-350 lbs N/acre/year) NITRATE Nitrate leaching to water (~30 lbs N/acre/year) 4

Soil Nitrate Production Rate Is High 5

Soil Nitrate Production vs. Crop Nitrate Uptake Rate of soil nitrate production from native soil organic matter Rate of corn or soybean nitrate uptake The majority of nitrate used by corn and soybean comes from soil nitrate production. Corn gets the difference from fertilizer while soybean gets the difference from legume fixation of atmospheric nitrogen. March February In the shaded areas, the soil produces nitrate, but there is no crop to use it. As a result, some nitrate is lost to waterways. 6

Soil Nitrate Production vs. Crop Nitrate Uptake Addition of a Cover Crop Rate of soil nitrate production from native soil organic matter Rate of corn or soybean nitrate uptake Cover crops can use nitrate when corn and beans are not growing, thus reducing the asynchrony between soil nitrate production and crop nitrate uptake. Cover crop nitrate use Cover crop nitrate use March February In the shaded areas, the soil produces nitrate, but there is no crop to use it. As a result, some nitrate is lost to waterways. 7

Summary: Why Is Nitrate Lost? An average Iowa soil contains 10,000 lbs of nitrogen/acre in organic matter. This organic nitrogen is not susceptible to rapid loss. When the soil is warm and moist (not saturated), microbes transform the organic nitrogen into nitrate. Nitrate is susceptible to rapid loss. If there is no crop to use soil nitrate, it can be lost to waterways (especially during heavy precipitation). Almost all nitrate loss to Iowa waterways occurs when soils are warm and moist and crops are not rapidly using soil nitrate. While both spring and fall periods lack crops, more nitrate loss usually occurs in the spring because soils are also warm and wet. 8

Summary: Why Is Nitrate Lost? Nitrogen fertilizer mismanagement is not the primary reason for nitrate loss. Most nitrate loss to Iowa waterways is caused by a mismatch in timing between nitrate production from native soil organic matter nitrogen and the demand for soil nitrate by crops. Examples: Nitrate loss from fertilized corn and unfertilized soybean is similar. In some situations, cover crops can reduce nitrate loss because they use nitrate in the spring and fall when corn and soybeans are not growing. There is little nitrate loss from perennial plants because they use nitrate when soil microbes are producing nitrate. 9

Drainage and Nitrate Loss Dr. Matthew Helmers Department of Agricultural and Biosystems Engineering 10

Nitrate Loss Pathways Nitrate is leached from the plant/crop root zone Nitrate is primarily transported in subsurface flow pathways In tile-drained lands: Nitrate moves to tile lines and is exported to streams In non-tile drained lands: Nitrate moves to shallow groundwater 11

Water Flow Pathways Naturally Well-Drained Soils Soils with Poor Natural Drainage Land management and land use impact evapotranspiration and infiltration, which in turn impact surface runoff, subsurface drainage, deep percolation 12

Why Drainage? Remove excess water from naturally poorly drained soils to protect crops Reduce yield variation in-field More timely field operations Improve crop yields Crop Yield Benefits of Subsurface Drainage (bushel/acre) Crop Iowa, 1984-1986 Ohio, 1962-1980 Corn 10 to 45 20 to 30 Soybeans 4 to 15 7 to 14 13

What Can We Do to Reduce Nitrate-N Export Systems with Subsurface Drainage Land Use Practices Nitrogen Management Edge-of-Field Practices Systems without Subsurface Drainage Land Use Practices Nitrogen Management 14

What Might It Take to Reach Goals? Example: Combination Scenarios that Achieves N Goal From Non-Point Sources for Nutrient Reduction Strategy Practice/Scenario N management - Maximum Return to Nitrogen Application Rate and 60% of all Corn-Bean and Continuous Corn Acres with Cover Crop Edge-of-Field - 27% of all ag land treated with wetland and 60% of all subsurface drained land with bioreactor Nitrate-N Reduction % (from baseline) 42 15

What Might It Take to Reach Goals? Example: Combination Scenarios that Achieves N Goal From Non-Point Sources for Nutrient Reduction Strategy Practice/Scenario N management - Maximum Return to Nitrogen Application Rate and 25% of all Corn-Bean and Continuous Corn Acres with Cover Crop Land Use - 25% of acreage with Extended Rotations Edge-of-Field - 27% of all ag land treated with wetland and 60% of all subsurface drained land with bioreactor Nitrate-N Reduction % (from baseline) 42 16

Summary: Drainage and Nitrates Nitrate is leached from the plant/crop root zone and is primarily transported through subsurface flow pathways to downstream waters Reaching water quality goals will require broad implementation of many practices 17