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Energy efficiency and greenhouse gas emissions during transition to organic and reduced-input practices: Student farm case study SEAN CLARK, Agriculture and Natural Resources Program, Berea College, KY 40404. BENYAMIN KHOSHNEVISAN and PARIA SEFEEDPARI, Department of Agricultural Machinery Engineering, Faculty of Agricultural Engineering and Technology, University of Tehran, Karaj, Iran. Background The Berea College Farm operates as an educational laboratory, providing students with opportunities to learn practical skills while testing and demonstrating appropriate methods for sustainable food production in the region. It is the oldest continuously- operating student farm in the US and includes forage and pasture crops, ruminant and monogastric livestock, grains, fruits and vegetables (Figure 1). Students are involved in all aspects of the daily farm operations and play managerial as well as labor roles. Figure 1. The Berea College Farm: enterprises, system boundaries, inputs and outputs. Objective To measure the changes in the farm’s energy efficiency and GHG emissions resulting from the implementation of a set of coordinated initiatives to improve sustainability. Sustainability Initiatives Students, staff and faculty affiliated with the Berea College Farm began to put into place several operational changes in 2009 aimed at improving the farm’s economic and environmental performance. They were fully in place by 2011. The initiatives included: 1) expansion of organic crop production 2) expansion of unheated hoophouses 3) transition from natural gas to wood to heat greenhouse 4) shift toward more crop production and a reduction in livestock production 5) transition from conventional indoor to outdoor pastured-based hog production 6) transition from grain-finishing to grass-finishing cattle 7) more direct marketing of food products to replace selling commodities Diesel Biodiesel Gasoline Electricity Natural gas Fertilizers Lime Seeds Herbicides Soybean meal Hay Water Wood Plastic Metals Vegetables Fruits Herbs Pork Beef Goat Chicken Eggs Grains Hay Ruminant livestock (cattle and goats) Monogastric livestock (pigs and chickens) Forages (pasture and hay) Horticultural crops (vegetables and fruits) Grains (for livestock and humans) FARM SYSTEM BOUNDARY (inc. 157 ha) MATERIAL INPUTS OUTPUTS LABOR MACHINERY AND INFRASTRUCTURE Methods Farm-management records provided all information on all material inputs and outputs from 2007 to 2013. Human labor was not included. Appropriate energy and GHG coefficients were identified in the literature and used to calculate energy inputs and outputs and GHG emissions (Table 1). Soil carbon was assumed to remain unchanged during the study period. Energy Efficiency Total annual farm production (Figure 2) and food-energy output remained relatively stable during throughout the study period (Figure 3). Greenhouse Gas Emissions Whole-farm GHG emissions declined during the study period (Figure 6). Because production output remained steady, the GHG emissions per unit of output, measured as t CO2,eq/GJ food-energy-output, also declined. Conclusion Overall energy input and output levels remained relatively constant over the study period but the farm’s dependence on non-renewable energy sources declined as renewable sources were incorporated. As a result, GHG emissions declined, largely due to a shift to outdoor hog production, a reduction in N fertilizer use, and fewer total livestock. Measurement Energy unit Energy coefficient (MJ unit -1 ) GHG unit GHG coefficient (kg CO 2,eq unit -1 ) Description/notes Inputs Diesel L 47.8 MJ 0.03 Fuel for tractors, combine, and truck Biodiesel L 33.3 kg 0.42 Alternative fuel for farm equipment from used vegetable oil Gasoline L 46.3 MJ 0.09 Fuel for rototillers and vans for transporting student workers Electricity kWh 12.0 kWh 1.19 Used in all buildings Natural gas m 3 49.5 MJ 0.07 Heat for confinement hog houses and greenhouse Nitrogen (N) kg 78.1 kg 5.88 Fertilizer, mainly for corn production Phosphate (P 2 O 5 ) kg 17.4 kg 1.01 Fertilizer Potassium (K 2 O) kg 13.7 kg 0.58 Fertilizer Lime (CaCO 3 ) kg 1.2 kg 0.11 Soil amendment for pH Herbicides (a.i.) kg 238.0 kg 10.97 Plant biocides, mainly for corn production Seed (agronomic) kg 13.0-230.0 kg 7.63 Grain crops, cover crops and forage crops Seed (horticultural) kg 0.8-5.6 kg 1.99 Vegetable and fruit crops Hay kg 2.8 kg 0.10 Harvested and baled forage crops for ruminant livestock Soybean meal kg 5.9 kg 0.27 Protein source for hog ration Water m 3 1.0 m 3 128.00 Livestock consumption and irrigation Wood kg 18.9 MJ 0.03 Dead trees from farm and campus burned to heat greenhouse Plastic kg 100.0 kg 7.63 Covering on hoop houses (unheated greenhouses) Aluminum kg 716.0 kg 5.80 Structure for hoop houses Tractor kg 138.0 kg 12.80 Purchased a single tractor during the study period Outputs Vegetables + fruits kg 0.8-5.6 NA NA Weight of horticultural crops sold Goat/Sheep kg 10.7 kg 2.88 Carcass weights of animals sold; enteric and manure emissions Pigs kg 9.8 kg 3.68 Carcass weights of animals sold; enteric and manure emissions Pig manure (07-09) kg NA kg 2.37 Manure lagoon emissions during confinement; Cattle (07-08) kg 10.7 kg 10.00 Carcass weight; enteric and manure emissions; grass and grain Cattle (09-13) kg 10.7 kg 12.00 Carcass weights; enteric and manure emissions; grass-fed only Chicken kg 10.3 kg 0.02 Carcass weights; manure emissions Eggs kg 6.1 kg 0.06 Weight sold; manure emissions Hay kg 2.8 NA NA Weight sold Corn grain kg 15.5 NA NA Weight sold Table 1. Energy and GHG coefficients used for farm inputs and outputs. 0 5 10 15 20 25 2007 2009 2011 2013 (Energy output/ input)*100 Renewable Energy Non-renewable energy inputs steadily declined during the study period as renewable energy inputs were incorporated, particularly during the last two years (Figures 4 & 5). Figure 2. Energy outputs as a percentage of energy inputs. - 500,000 1,000,000 1,500,000 2,000,000 2,500,000 3,000,000 3,500,000 2007 2009 2011 2013 Energy Inputs (MJ) Renewable energy Non renewable energy Figure 4. Renewable and non-renewable energy inputs to the farm. 0 5 10 15 20 25 30 35 2007 2009 2011 2013 (Energy Output/ Non- Renewable Input)*100 Figure 5. Food energy outputs as a percentage of non-renewable energy inputs. 0 400 800 1200 2007 2008 2009 2010 2011 2012 2013 Total GHG emissions (t CO2.eq) Enteric fermentation N Manure stored in lagoons Electricity Gasoline Natural gas Diesel Hay Lime Soybean meal Seed Water K2O Herbicide P2O5 Plastic Wood Aluminum Biodiesel Chickens & eggs Tractor Figure 6. Whole-farm GHG emissions declined over the study period. Shown in order of magnitude left to right 0 40 80 120 2007 2009 2011 2013 Metric tons Pigs Cattle Goats/sheep Chicken Eggs Vegetables/fruits Hay Corn grain Figure 2. Farm production output (metric tons).

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Page 1: Energy efficiency and greenhouse gas emissions …Energy efficiency and greenhouse gas emissions during transition to organic and reduced-input practices: Student farm case study SEAN

Energy efficiency and greenhouse gas emissions during transition to organic and reduced-input practices:Student farm case study

SEAN CLARK, Agriculture and Natural Resources Program, Berea College, KY 40404. BENYAMIN KHOSHNEVISAN and PARIA SEFEEDPARI, Department of Agricultural Machinery Engineering, Faculty of Agricultural Engineering and Technology, University of Tehran, Karaj, Iran.

Background

The Berea College Farm operates as an educational laboratory, providing students with

opportunities to learn practical skills while testing and demonstrating appropriate

methods for sustainable food production in the region. It is the oldest continuously-

operating student farm in the US and includes forage and pasture crops, ruminant and

monogastric livestock, grains, fruits and vegetables (Figure 1). Students are involved in all

aspects of the daily farm operations and play managerial as well as labor roles.

Figure 1. The Berea College Farm: enterprises, system boundaries, inputs and outputs.

Objective

To measure the changes in the farm’s energy efficiency and GHG emissions resulting

from the implementation of a set of coordinated initiatives to improve sustainability.

Sustainability Initiatives

Students, staff and faculty affiliated with the Berea College Farm began to put into place

several operational changes in 2009 aimed at improving the farm’s economic and

environmental performance. They were fully in place by 2011. The initiatives included:

1) expansion of organic crop production

2) expansion of unheated hoophouses

3) transition from natural gas to wood to heat greenhouse

4) shift toward more crop production and a reduction in livestock production

5) transition from conventional indoor to outdoor pastured-based hog production

6) transition from grain-finishing to grass-finishing cattle

7) more direct marketing of food products to replace selling commodities

DieselBiodieselGasolineElectricityNatural gasFertilizersLimeSeedsHerbicidesSoybean mealHayWaterWoodPlasticMetals

VegetablesFruitsHerbsPorkBeefGoatChickenEggsGrainsHay

Ruminant livestock(cattle andgoats)

Monogastriclivestock(pigs and chickens)

Forages (pasture and hay)

Horticultural crops(vegetables and fruits)

Grains(for livestock and humans)

FARM SYSTEM BOUNDARY (inc. 157 ha)MATERIALINPUTS

OUTPUTS

LABOR

MACHINERY AND INFRASTRUCTURE

Methods

• Farm-management records provided all information on all material inputs and

outputs from 2007 to 2013. Human labor was not included.

• Appropriate energy and GHG coefficients were identified in the literature and used to

calculate energy inputs and outputs and GHG emissions (Table 1).

• Soil carbon was assumed to remain unchanged during the study period.

Energy Efficiency

Total annual farm production (Figure 2) and food-energy output remained relatively

stable during throughout the study period (Figure 3).

Greenhouse Gas Emissions

Whole-farm GHG emissions declined during the study period (Figure 6). Because

production output remained steady, the GHG emissions per unit of output, measured as

t CO2,eq/GJ food-energy-output, also declined.

Conclusion

Overall energy input and output levels remained relatively constant over the study period

but the farm’s dependence on non-renewable energy sources declined as renewable

sources were incorporated. As a result, GHG emissions declined, largely due to a shift to

outdoor hog production, a reduction in N fertilizer use, and fewer total livestock.

Measurement Energy

unit

Energy

coefficient

(MJ unit-1)

GHG

unit

GHG

coefficient

(kg CO2,eq

unit-1)

Description/notes

InputsDiesel L 47.8 MJ 0.03 Fuel for tractors, combine, and truckBiodiesel L 33.3 kg 0.42 Alternative fuel for farm equipment from used vegetable oil Gasoline L 46.3 MJ 0.09 Fuel for rototillers and vans for transporting student workersElectricity kWh 12.0 kWh 1.19 Used in all buildingsNatural gas m3 49.5 MJ 0.07 Heat for confinement hog houses and greenhouseNitrogen (N) kg 78.1 kg 5.88 Fertilizer, mainly for corn productionPhosphate (P2O5) kg 17.4 kg 1.01 FertilizerPotassium (K2O) kg 13.7 kg 0.58 FertilizerLime (CaCO3) kg 1.2 kg 0.11 Soil amendment for pHHerbicides (a.i.) kg 238.0 kg 10.97 Plant biocides, mainly for corn productionSeed (agronomic) kg 13.0-230.0 kg 7.63 Grain crops, cover crops and forage cropsSeed (horticultural) kg 0.8-5.6 kg 1.99 Vegetable and fruit cropsHay kg 2.8 kg 0.10 Harvested and baled forage crops for ruminant livestockSoybean meal kg 5.9 kg 0.27 Protein source for hog rationWater m3 1.0 m3 128.00 Livestock consumption and irrigationWood kg 18.9 MJ 0.03 Dead trees from farm and campus burned to heat greenhouse Plastic kg 100.0 kg 7.63 Covering on hoop houses (unheated greenhouses)Aluminum kg 716.0 kg 5.80 Structure for hoop housesTractor kg 138.0 kg 12.80 Purchased a single tractor during the study period

OutputsVegetables + fruits kg 0.8-5.6 NA NA Weight of horticultural crops soldGoat/Sheep kg 10.7 kg 2.88 Carcass weights of animals sold; enteric and manure emissionsPigs kg 9.8 kg 3.68 Carcass weights of animals sold; enteric and manure emissionsPig manure (07-09) kg NA kg 2.37 Manure lagoon emissions during confinement;Cattle (07-08) kg 10.7 kg 10.00 Carcass weight; enteric and manure emissions; grass and grainCattle (09-13) kg 10.7 kg 12.00 Carcass weights; enteric and manure emissions; grass-fed onlyChicken kg 10.3 kg 0.02 Carcass weights; manure emissionsEggs kg 6.1 kg 0.06 Weight sold; manure emissionsHay kg 2.8 NA NA Weight soldCorn grain kg 15.5 NA NA Weight sold

Table 1. Energy and GHG coefficients used for farm inputs and outputs.

0

5

10

15

20

25

2007 2009 2011 2013

(En

ergy

ou

tpu

t/

inp

ut)

*10

0

Renewable Energy

Non-renewable energy inputs steadily declined during the study period as renewable

energy inputs were incorporated, particularly during the last two years (Figures 4 & 5).

Figure 2. Energy outputs as a percentage of energy inputs.

-

500,000

1,000,000

1,500,000

2,000,000

2,500,000

3,000,000

3,500,000

2007 2009 2011 2013

Ene

rgy

Inp

uts

(M

J)

Renewable energy Non renewable energy

Figure 4. Renewable and non-renewable energy inputs to the farm.

0

5

10

15

20

25

30

35

2007 2009 2011 2013

(En

erg

y O

utp

ut/

No

n-

Re

new

able

Inp

ut)

*10

0

Figure 5. Food energy outputs as a percentage of non-renewable energy inputs.

0

400

800

1200

2007 2008 2009 2010 2011 2012 2013

Tota

l GH

G e

mis

sio

ns

(t C

O2

.eq

)

Enteric fermentation N Manure stored in lagoonsElectricity Gasoline Natural gasDiesel Hay LimeSoybean meal Seed WaterK2O Herbicide P2O5Plastic Wood AluminumBiodiesel Chickens & eggs Tractor

Figure 6. Whole-farm GHG emissions declined over the study period.

Shown in

order of

magnitude

left to right

0

40

80

120

2007 2009 2011 2013

Met

ric

ton

s

Pigs Cattle Goats/sheepChicken Eggs Vegetables/fruitsHay Corn grain

Figure 2. Farm production output (metric tons).