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Software for Evaluating the
Environmental Impact of Dairy
and Beef Production Systems
USDA, Agricultural Research Service
University Park, Pennsylvania
C. Alan Rotz
 Economic concerns
 Environmental concerns
 Social concerns
 Production costs continue to increase more
rapidly than the value of farm produce
 This is forcing our farms to become more
efficient and often larger
 Larger farms tend to exacerbate
environmental concerns
 Groundwater
 Surface water
 Air quality
 Process-level simulation provides
an effective tool
 Relatively rapid, inexpensive,
and comprehensive evaluations
 Supported with field
data, provides the best
assessment possible
 Life Cycle Assessment: an environmental
accounting program
 Process-based model: a simulation of the
production system
 Combined simulation and LCA:
Simulation is used to provide the
parameters for the LCA
 Integrated Farm Systems
Model, IFSM
 Dairy Greenhouse Gas
Model, DairyGHG
 Dairy Gas Emissions
Model, DairyGEM
Integrated Farm System Model
Process-Level Farm Simulation
Soil
Establish
Crop Harvest
Storage
AnimalManure
Grazing
Volatile loss
Exported manure
Purchased feed,
bedding, etc.
Feed sold
Volatile loss
Fixed
nutrients
Volatile loss
Purchased
fertilizer
Runoff &
Leaching loss
Milk and
animals
Engine exhaust
 Crop yields and quality
 Feeds produced
 Feeds bought and sold
 Milk or meat produced
 Manure produced
 Labor, fuel and equipment use
 Annual production costs (crop
production, harvest, storage, feeding,
etc.)
 Annual income from milk, animals, and
feed sold
 Net return or profitability
 Ammonia emission
 Hydrogen sulfide emission
 Denitrification N loss
 Leached N and N concentration in groundwater
 Erosion, soluble and sediment P runoff losses
 Greenhouse gas emissions
 N, P, K and C balance
 Carbon emission
 Energy use
 Water use
 Reactive nitrogen loss
Feed Production
Animal Production
Manure Handling
Resource inputs
Fuel
Electricity
Fertilizer
Pesticide
Plastic
Machinery
Off-farm heifers
Purchased feed
Imported manure
Milk sold
Animals sold
Feed sold
Exported manure
Direct Sinks and Sources
Fixed CO2 CO2 N2O CH4 CO2 CH4 CO2 N2O
Farm
Pre-chain Sources
CO2 CH4 N2O
Emissions
allocated to
other farm
products
(Cradle-to-farm gate)
 A research tool for evaluating and comparing
the economic and environmental
sustainability of crop, dairy and beef
production systems
 An educational tool for individual, workshop
and classroom evaluation of production
systems
 Limited value as a decision
support tool
Dairy Gas Emission Model
Soil
Establish
Crop Harvest
Storage
AnimalManure
Grazing
Volatile loss
Exported manure
Purchased feed,
bedding, etc.
Feed sold
Volatile loss
Fixed
nutrients
Volatile loss
Purchased
fertilizer
Runoff &
Leaching loss
Milk and
animals
Engine exhaust
 A simpler tool with fewer inputs and more
graphical output
 Primarily developed as an educational aid
for individual, workshop and classroom
evaluation of dairy production systems
 Can be used as a decision
support tool, but caution
is advised
 Verification of components
 Process-level evaluation
 Farm level evaluation
0
20
40
60
80
100
120
140
0 50 100 150 200 250 300 350 400 450 500 550 600 650 700
Day of year
Ammoniaemission,g/cow-day
Measured
Simulated
Storage type Anaerobic digester
Incorporation
 Herd of 1100 cows plus 925 replacement heifers
producing 26,000 lb of milk (3.5% fat) per cow
 2500 acres of shallow loam soil (840 acres
alfalfa, 1200 acres corn, 200 acres wheat, 120 acre
soybean, and 150 acres grass)
 Manure handling includes anaerobic
digestion, liquid/solid separation, rapid
incorporation, export of 12% of manure solids
 Simulated for 25 years of Syracuse, NY weather
 Slurry storage, surface application, and no-till
crop establishment with no manure incorporation
 Liquid/solid separation, recycling of solids for
bedding, open storage, rapid incorporation of
stored liquid following surface application, export
of 12% of manure solids
 Same as 2, except manure storage is enclosed and
a flare is used to burn the biogas produced
 Same as 2, except an anaerobic digester is used
prior to separation and storage
0
300
600
900
lb/ac/yr
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
0.0
0.2
0.4
0.6 Dissolved
Sediment
lb/ac/yr
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
Nitrogen Loss
0
20
40
60
80
100
Volatilization
Leaching
Denitirfication
lb/ac/yr
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
0.000
0.002
0.004
0.006
0.008
lb CO2e/lb FPCM
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
Greenhouse Gas Emissions
0
2
4
6
8
10
12 Secondary
Fuel
Manure
Animal
t CO2e/cow/yr
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
0.0
0.2
0.4
0.6
0.8
lb CO2e/lb FPCM
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
0.0
0.2
0.4
0.6
0.8
1.0
mBtu/lb FPCM
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
0
500
1000
1500
2000
2500
3000
3500
Milk hauling
Energy
Purchased feed
Livestock
Cropping
Machinery
Facilities
Labor
Land
$/cow/yr
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
1000
1100
1200
1300
1400
1500
$/cow/yr
Open Enclosed Anaerobic
Slurry storage storage digester
No-till Liquid/solid separation, tillage incorp.
Provides similar results for:
 Ammonia, hydrogen sulfide, methane, nitrous
oxide and carbon dioxide emissions
 Carbon, energy and water footprints
0.0
0.2
0.4
0.6
0.8
1.0
mBtu/lbFPCM
0.0
0.2
0.4
0.6
0.8
lbCO2e/lbFPCM
0
2
4
6
8
10
12
tCO2e/cow/yr
0
10
20
30
40
50
60
lb/ac/yr
 The Integrated Farm System Model (IFSM)
provides a research tool for evaluating the
environmental impacts and economics of farming
systems
 The Dairy Gas Emissions Model (DairyGEM)
provides an educational aid for studying the
effects of farm management and mitigation
strategies on air emissions and related footprints
USDA
Pasture Systems and Watershed
Management Research Unit
University Park, Pennsylvania
Agricultural Research Service

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Software For Evaluating the Environmental Impact of Dairy and Beef Production Systems

  • 1. Software for Evaluating the Environmental Impact of Dairy and Beef Production Systems USDA, Agricultural Research Service University Park, Pennsylvania C. Alan Rotz
  • 2.  Economic concerns  Environmental concerns  Social concerns
  • 3.  Production costs continue to increase more rapidly than the value of farm produce  This is forcing our farms to become more efficient and often larger  Larger farms tend to exacerbate environmental concerns
  • 4.  Groundwater  Surface water  Air quality
  • 5.
  • 6.
  • 7.  Process-level simulation provides an effective tool  Relatively rapid, inexpensive, and comprehensive evaluations  Supported with field data, provides the best assessment possible
  • 8.  Life Cycle Assessment: an environmental accounting program  Process-based model: a simulation of the production system  Combined simulation and LCA: Simulation is used to provide the parameters for the LCA
  • 9.  Integrated Farm Systems Model, IFSM  Dairy Greenhouse Gas Model, DairyGHG  Dairy Gas Emissions Model, DairyGEM
  • 11. Process-Level Farm Simulation Soil Establish Crop Harvest Storage AnimalManure Grazing Volatile loss Exported manure Purchased feed, bedding, etc. Feed sold Volatile loss Fixed nutrients Volatile loss Purchased fertilizer Runoff & Leaching loss Milk and animals Engine exhaust
  • 12.  Crop yields and quality  Feeds produced  Feeds bought and sold  Milk or meat produced  Manure produced  Labor, fuel and equipment use
  • 13.  Annual production costs (crop production, harvest, storage, feeding, etc.)  Annual income from milk, animals, and feed sold  Net return or profitability
  • 14.  Ammonia emission  Hydrogen sulfide emission  Denitrification N loss  Leached N and N concentration in groundwater  Erosion, soluble and sediment P runoff losses  Greenhouse gas emissions  N, P, K and C balance
  • 15.  Carbon emission  Energy use  Water use  Reactive nitrogen loss
  • 16. Feed Production Animal Production Manure Handling Resource inputs Fuel Electricity Fertilizer Pesticide Plastic Machinery Off-farm heifers Purchased feed Imported manure Milk sold Animals sold Feed sold Exported manure Direct Sinks and Sources Fixed CO2 CO2 N2O CH4 CO2 CH4 CO2 N2O Farm Pre-chain Sources CO2 CH4 N2O Emissions allocated to other farm products (Cradle-to-farm gate)
  • 17.  A research tool for evaluating and comparing the economic and environmental sustainability of crop, dairy and beef production systems  An educational tool for individual, workshop and classroom evaluation of production systems  Limited value as a decision support tool
  • 18. Dairy Gas Emission Model Soil Establish Crop Harvest Storage AnimalManure Grazing Volatile loss Exported manure Purchased feed, bedding, etc. Feed sold Volatile loss Fixed nutrients Volatile loss Purchased fertilizer Runoff & Leaching loss Milk and animals Engine exhaust
  • 19.  A simpler tool with fewer inputs and more graphical output  Primarily developed as an educational aid for individual, workshop and classroom evaluation of dairy production systems  Can be used as a decision support tool, but caution is advised
  • 20.  Verification of components  Process-level evaluation  Farm level evaluation
  • 21. 0 20 40 60 80 100 120 140 0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 Day of year Ammoniaemission,g/cow-day Measured Simulated
  • 22. Storage type Anaerobic digester Incorporation
  • 23.  Herd of 1100 cows plus 925 replacement heifers producing 26,000 lb of milk (3.5% fat) per cow  2500 acres of shallow loam soil (840 acres alfalfa, 1200 acres corn, 200 acres wheat, 120 acre soybean, and 150 acres grass)  Manure handling includes anaerobic digestion, liquid/solid separation, rapid incorporation, export of 12% of manure solids  Simulated for 25 years of Syracuse, NY weather
  • 24.  Slurry storage, surface application, and no-till crop establishment with no manure incorporation  Liquid/solid separation, recycling of solids for bedding, open storage, rapid incorporation of stored liquid following surface application, export of 12% of manure solids  Same as 2, except manure storage is enclosed and a flare is used to burn the biogas produced  Same as 2, except an anaerobic digester is used prior to separation and storage
  • 25. 0 300 600 900 lb/ac/yr Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 26. 0.0 0.2 0.4 0.6 Dissolved Sediment lb/ac/yr Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 27. Nitrogen Loss 0 20 40 60 80 100 Volatilization Leaching Denitirfication lb/ac/yr Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 28. 0.000 0.002 0.004 0.006 0.008 lb CO2e/lb FPCM Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 29. Greenhouse Gas Emissions 0 2 4 6 8 10 12 Secondary Fuel Manure Animal t CO2e/cow/yr Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 30. 0.0 0.2 0.4 0.6 0.8 lb CO2e/lb FPCM Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 31. 0.0 0.2 0.4 0.6 0.8 1.0 mBtu/lb FPCM Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 32. 0 500 1000 1500 2000 2500 3000 3500 Milk hauling Energy Purchased feed Livestock Cropping Machinery Facilities Labor Land $/cow/yr Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 33. 1000 1100 1200 1300 1400 1500 $/cow/yr Open Enclosed Anaerobic Slurry storage storage digester No-till Liquid/solid separation, tillage incorp.
  • 34. Provides similar results for:  Ammonia, hydrogen sulfide, methane, nitrous oxide and carbon dioxide emissions  Carbon, energy and water footprints 0.0 0.2 0.4 0.6 0.8 1.0 mBtu/lbFPCM 0.0 0.2 0.4 0.6 0.8 lbCO2e/lbFPCM 0 2 4 6 8 10 12 tCO2e/cow/yr 0 10 20 30 40 50 60 lb/ac/yr
  • 35.  The Integrated Farm System Model (IFSM) provides a research tool for evaluating the environmental impacts and economics of farming systems  The Dairy Gas Emissions Model (DairyGEM) provides an educational aid for studying the effects of farm management and mitigation strategies on air emissions and related footprints
  • 36. USDA Pasture Systems and Watershed Management Research Unit University Park, Pennsylvania Agricultural Research Service