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Crop Residue Considerations for
Sustainable Biomass Feedstock Supplies
Douglas L. Karlen, USDA-ARS
National Laboratory for Agriculture & the Environment
Presented at the Minnesota Bioenergy Feedstock
Development Forum
December 8, 2014
 An overview of the USDA-ARS REAP – DOE
Regional Corn Stover – Sun Grant Partnership
 What has been learned regarding sustainable
corn stover harvest?
 Landscape management strategies for
increasing the quantity of corn stover that can
be harvested in a sustainable manner
Presentation Overview
REAP/Regional Partnership Sites
Utilized Multiple Harvest Technologies
University Park
Lincoln
Ames, Morris & St. Paul Florence Industry Collaborators
Compiled 239 site-years of stover harvest data
Effects on subsequent grain and stover yields
Effects on soil organic carbon (C) & aggregation
Effects on microbial community
Effects on GHG emissions
Prepared a special 2014 issue of BioEnergy Research
Developed the Landscape Environmental Assessment
Framework (LEAF) and other tools to:
Estimate available residue
Quantify economics
Ensure ecosystem service benefits are sustained
What has the REAP/Regional Partnership Done?
This involved ARS, DOE, university, and private industry partners
What has the Partnership learned?
 Corn grain yields ranged from 5.0 to 14.3 Mg ha-1 (80
to 227 bu/acre)
 Average grain yield response to stover harvest was
minimal:
 9.8, 10.1, and 10.1 Mg ha-1 (156, 160, and 160 bu/acre) for:
 No, moderate (3.9 Mg ha-1 or 1.7 tons/acre), or high removal
(7.2 Mg ha-1 or 3.2 tons/acre)
 Sustainable stover harvest rates are site specific –
averages are meaningless
 Diversifying the Midwestern landscape can increase
sustainable quantities of harvestable biomass
BUT-- Excessive Stover Harvest Can:
Compaction & crusting
Degrade structure & aggregation causing –
Water & wind erosion
Reduced plant growth
Impaired soil biology
Decreased yield
Reduced Soil Productivity
Stover is also important for soil health!
2013 winter erosion in Story County, Iowa
“Excessive” stover harvest in Iowa and Wisconsin
Other Lessons
 Compared to harvesting only grain – N, P, and K removal
are increased by at least 16, 2, and 18 kg Mg-1 of stover
 Minimum residue return projections for 35 studies were
6.38 ± 2.19 Mg stover ha-1 yr-1
 For grain yields ≤ 11 Mg ha-1 (175 bu ac-1), ten years of
stover harvest, even with no-tillage, resulted in reduced
POM (particulate organic matter) accumulation
 Low corn yields shifted the dry aggregate distribution
toward smaller soil aggregates
 Insufficient yields resulted in undesirable shifts in the
microbial community
 Overall, sustainable supplies of corn stover may be lower
than initially projected because of weather-induced yield
variability
 Designing Sustainable Landscapes
 Multi-objective approaches to targeting areas of the
field based on:
 Subfield profit
 Grain production
 Soil erosion
 Nitrate Leaching
 Soil organic carbon gain
Sustainable Bioenergy Land Use –
Integrated Landscape Management
County Level Approach
 Subfield allocation of county level grain production
 Field boundaries & subfield soils for Hardin County,
Iowa
Source: Bonner et al (2014) doi:10.3390/en7106509
County Level Approach
 Subfield allocation of county level grain production
 Field boundaries & subfield soils for Hardin
County, Iowa
Source: Bonner et al (2014) doi:10.3390/en7106509
County Level Approach
 Subfield allocation of county level grain production
 Field boundaries & subfield soils for Hardin
County, Iowa
Source: Bonner et al (2014) doi:10.3390/en7106509
County Level Approach
 Subfield allocation of county level grain production
 Field boundaries & subfield soils for Hardin County, Iowa
 Over 4,000 fields producing corn within the county
 Over 77,000 subfield areas
Source: Bonner et al (2014) doi:10.3390/en7106509
County Level Subfield Profit
Average profit based on productivity, crop rotation,
and grain price
Source: Bonner et al (2014) doi:10.3390/en7106509
 Identification of areas for conversion to
energy crops
 Depending on the profitability of an
energy crop, county level impacts
can be quite dramatic.
 Impacting up to 85% of field
 22% land conversion
 99% increase in sustainable
biomass availability
 21% reduction in nutrient loss
 158% increase in soil organic
matter
 27% reduced risk to surface
waters
County Level Impacts
Source: Bonner et al (2014) doi:10.3390/en7106509
Soil and Water
Quality Effects
U.W. Platteville
Pioneer Farm
Soil profile &
water quality
data is being
collected in 2
watersheds to
establish a
baseline as
we scale up
for future full-
scale studies
Another strategy – an alfalfa paradigm shift
REAP goal – diversify landscape, provide feedstock,
improve soil health, & protect water quality
Alfalfa Leaf Protein Collection & Extraction
Create market-pull for perennials by starting with a familiar crop
Summary & Conclusions
REAP/Regional Partnership recommendations
Develop sub-field stover harvest practices
Decrease tillage intensities
Utilize cover crops
Diversify the landscape with perennials, cover
crops, oilseed crops, or where feasible by
double-cropping
Continue research and development of
diversified management plans using the
Landscape Environmental Assessment
Framework (LEAF)
Developing Sustainable Stover Harvest
Strategies is the First Step Toward Solving
Landscape Energy and Ecosystem Challenges
Any Questions?

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Crop Residue Considerations for Sustainable Biomass Feedstock Supplies

  • 1. Crop Residue Considerations for Sustainable Biomass Feedstock Supplies Douglas L. Karlen, USDA-ARS National Laboratory for Agriculture & the Environment Presented at the Minnesota Bioenergy Feedstock Development Forum December 8, 2014
  • 2.  An overview of the USDA-ARS REAP – DOE Regional Corn Stover – Sun Grant Partnership  What has been learned regarding sustainable corn stover harvest?  Landscape management strategies for increasing the quantity of corn stover that can be harvested in a sustainable manner Presentation Overview
  • 4. Utilized Multiple Harvest Technologies University Park Lincoln Ames, Morris & St. Paul Florence Industry Collaborators
  • 5. Compiled 239 site-years of stover harvest data Effects on subsequent grain and stover yields Effects on soil organic carbon (C) & aggregation Effects on microbial community Effects on GHG emissions Prepared a special 2014 issue of BioEnergy Research Developed the Landscape Environmental Assessment Framework (LEAF) and other tools to: Estimate available residue Quantify economics Ensure ecosystem service benefits are sustained What has the REAP/Regional Partnership Done? This involved ARS, DOE, university, and private industry partners
  • 6. What has the Partnership learned?  Corn grain yields ranged from 5.0 to 14.3 Mg ha-1 (80 to 227 bu/acre)  Average grain yield response to stover harvest was minimal:  9.8, 10.1, and 10.1 Mg ha-1 (156, 160, and 160 bu/acre) for:  No, moderate (3.9 Mg ha-1 or 1.7 tons/acre), or high removal (7.2 Mg ha-1 or 3.2 tons/acre)  Sustainable stover harvest rates are site specific – averages are meaningless  Diversifying the Midwestern landscape can increase sustainable quantities of harvestable biomass
  • 7. BUT-- Excessive Stover Harvest Can: Compaction & crusting Degrade structure & aggregation causing – Water & wind erosion Reduced plant growth Impaired soil biology Decreased yield Reduced Soil Productivity
  • 8. Stover is also important for soil health! 2013 winter erosion in Story County, Iowa “Excessive” stover harvest in Iowa and Wisconsin
  • 9. Other Lessons  Compared to harvesting only grain – N, P, and K removal are increased by at least 16, 2, and 18 kg Mg-1 of stover  Minimum residue return projections for 35 studies were 6.38 ± 2.19 Mg stover ha-1 yr-1  For grain yields ≤ 11 Mg ha-1 (175 bu ac-1), ten years of stover harvest, even with no-tillage, resulted in reduced POM (particulate organic matter) accumulation  Low corn yields shifted the dry aggregate distribution toward smaller soil aggregates  Insufficient yields resulted in undesirable shifts in the microbial community  Overall, sustainable supplies of corn stover may be lower than initially projected because of weather-induced yield variability
  • 10.  Designing Sustainable Landscapes  Multi-objective approaches to targeting areas of the field based on:  Subfield profit  Grain production  Soil erosion  Nitrate Leaching  Soil organic carbon gain Sustainable Bioenergy Land Use – Integrated Landscape Management
  • 11. County Level Approach  Subfield allocation of county level grain production  Field boundaries & subfield soils for Hardin County, Iowa Source: Bonner et al (2014) doi:10.3390/en7106509
  • 12. County Level Approach  Subfield allocation of county level grain production  Field boundaries & subfield soils for Hardin County, Iowa Source: Bonner et al (2014) doi:10.3390/en7106509
  • 13. County Level Approach  Subfield allocation of county level grain production  Field boundaries & subfield soils for Hardin County, Iowa Source: Bonner et al (2014) doi:10.3390/en7106509
  • 14. County Level Approach  Subfield allocation of county level grain production  Field boundaries & subfield soils for Hardin County, Iowa  Over 4,000 fields producing corn within the county  Over 77,000 subfield areas Source: Bonner et al (2014) doi:10.3390/en7106509
  • 15. County Level Subfield Profit Average profit based on productivity, crop rotation, and grain price Source: Bonner et al (2014) doi:10.3390/en7106509
  • 16.  Identification of areas for conversion to energy crops  Depending on the profitability of an energy crop, county level impacts can be quite dramatic.  Impacting up to 85% of field  22% land conversion  99% increase in sustainable biomass availability  21% reduction in nutrient loss  158% increase in soil organic matter  27% reduced risk to surface waters County Level Impacts Source: Bonner et al (2014) doi:10.3390/en7106509
  • 17. Soil and Water Quality Effects U.W. Platteville Pioneer Farm Soil profile & water quality data is being collected in 2 watersheds to establish a baseline as we scale up for future full- scale studies
  • 18. Another strategy – an alfalfa paradigm shift REAP goal – diversify landscape, provide feedstock, improve soil health, & protect water quality
  • 19. Alfalfa Leaf Protein Collection & Extraction Create market-pull for perennials by starting with a familiar crop
  • 20. Summary & Conclusions REAP/Regional Partnership recommendations Develop sub-field stover harvest practices Decrease tillage intensities Utilize cover crops Diversify the landscape with perennials, cover crops, oilseed crops, or where feasible by double-cropping Continue research and development of diversified management plans using the Landscape Environmental Assessment Framework (LEAF)
  • 21. Developing Sustainable Stover Harvest Strategies is the First Step Toward Solving Landscape Energy and Ecosystem Challenges Any Questions?