Net energy of cellulosic ethanol from switchgrass

Schmer et al. 10.1073/pnas.0704767105.

Supporting Tables

Files in this Data Supplement:

SI Table 1
SI Table 2
SI Table 3
SI Table 4
SI Table 5
SI Table 6
SI Table 7




Table 1. Summary of total agricultural energy inputs for switchgrass fields grown for bioenergy for 5 years in Nebraska, South Dakota, and North Dakota

Location

Seeding*

Fertilizer

Herbicide

Packaging

Transportation

Diesel

Machinery and Labor

Total

 

--------------------------------------------------MJ ha-1--------------------------------------------------

Lawrence, NE

88

3665

309

21

50

698

239

5070

Douglas, NE

114

3994

399

24

56

901

268

5756

Atkinson, NE

175

2238

208

14

32

720

286

3673

Crofton, NE

88

2307

737

14

34

844

289

4313

Ethan, SD

88

4072

253

23

55

844

279

5613

Huron, SD

88

1504

784

9

22

1070

346

3822

Highmore, SD

88

1207

156

7

17

652

213

2340

Bristol, SD

88

3891

736

23

70

1298

316

6451

Streeter, ND

88

2700

379

16

37

827

276

4323

Munich, ND

88

3422

775

20

48

965

321

5637

Mean

99

2900

474

17

42

882

283

4700

*A partial reseeding was done in areas at the Douglas farm. The Atkinson farm was reseeded in 2001 because of stand failure caused by drought in 2000.





Table 2. Agriculture and biorefinery inputs and respective energy values used to determine the energy balance of switchgrass grown for cellulosic ethanol

Inputs

Energy values

Source(s) (refs)

Notes

Agriculture

     
 

MJ kg-1

   

Seed

45.1

-

See Table 5.

Nitrogen Fertilizer

49.0

1, 2

 

Herbicide

322.3

1, 2

 

Electricity*

NA

   

Material Transport

0.65

1, 2

 

Packaging

0.27

3

 

Embodied energy†

MJ ha-1

   

Tillage

46

4-6

 

Sprayer

37

4-6

 

Fertilizer cart

14

4-6

 

No-till drill

98

4-6

 

Harvest and transport

251

4-6

Cut, bale, and transport bales to edge of field

Diesel use

-

 

See Table 7.

Biorefinery

     
 

MJ L-1

   

Feedstock transport

0.63

1, 2

Transport bales from field to cellulosic plant

Nonrenewable power

0

1, 2

Biorefinery uses lignin for steam and electricity

Diesel use

0.06

1, 2

 

Plant capital and equip.

0.44

2, 7

 

Process water

0.29

2, 7

 

Sewage effluent

0.29

2, 7

 
       
 

L kg-1

   

Ethanol yield

0.38

2

 

* Agricultural electricity use for switchgrass biomass production was not estimated in this study. EBAMM uses a value of 46 MJ Mg-1 from GREET 1.6 that is based on estimated electrical rates for switchgrass production (1, 2),which are higher than electrical rates for corn grown in rain-fed regions (8, 9). The main use for electricity for corn production is for grain drying and/or in irrigation (9). Switchgrass will not require electricity for drying and projected land areas for switchgrass production will be non-irrigated fields. There is no direct agricultural application that would require electricity usage to vary by biomass yield (1).

† Farm Machinery Energy (MJ ha-1) = [Total operational cost (dollar hectare-1) ´ (35.9 MJ

dollar-1 iron and steel manufacturing + 7.95 MJ dollar-1 farm machinery and equipment manufacturing)/15 years] (4, 5). Farm machinery energy inputs from this study were similar to estimates in previous reports (2, 3, 6, 10).





Table 3. Net energy values [output energy (MJFuel literFuel-1) - input energy (MJInput literFuel-1)] for switchgrass fields

 

Harvest year

 

1*

2

3

4

5

Mean

Location

-----------------MJ L-1-----------------

Lawrence, NE

NH

19.9

21.0

22.1

21.9

21.2

Douglas, NE

NH

20.7

19.9

22.3

21.6

21.1

Atkinson, NE

NH

17.0

18.7

21.7

21.7

19.8

Crofton, NE

NH

20.1

20.4

22.5

22.0

21.3

Ethan, SD

NH

18.8

21.5

22.8

21.2

21.1

Huron, SD

23.0

23.6

22.4

23.2

21.4

22.7

Highmore, SD

NH

NH

22.4

22.9

23.2

22.8

Bristol, SD

21.9

20.2

22.8

22.6

23.7

22.3

Streeter, ND

NH

23.0

22.1

21.9

21.1

22.0

Munich, ND

14.3

21.5

21.6

21.9

22.7

20.4

Mean

19.7

20.5

21.3

22.5

22.0

21.5

*NH, no harvest.





Table 4. Biomass yields from established (2 years after planting) switchgrass fields in the midcontinental US

 

Harvest year

 

3

4

5

Mean

Location

--------------Mg ha-1-------------

Lawrence, NE

5.2

7.1

6.2

6.2

Douglas, NE

3.9

8.8

7.5

6.7

Atkinson, NE

4.9

5.5

-

5.2

Crofton, NE

4.8

7.2

6.3

6.1

Ethan, SD

8.0

6.9

6.1

7.0

Huron, SD

6.6

10.5

5.5

7.5

Highmore, SD

8.4

8.3

3.7

6.8

Bristol, SD

9.9

11.4

12.1

11.1

Streeter, ND

5.0

8.3

6.1

6.5

Munich, ND

8.2

8.4

6.9

7.8

Mean

6.5

8.2

6.7

7.1

Ethanol conversion efficiency was estimated at 0.38 liters kg-1 (2).





Table 5. Summary of estimated greenhouse gas (GHG) emissions of ethanol derived from switchgrass

 

 

Estimated GHG emissions by location and harvest year*

 

Estab.†

2

3

4

5

Mean

Location

g CO2equivalent MJ-1 ethanol produced‡

Lawrence, NE

NH

17

16

4

7

11

Douglas, NE

NH

12

27

1

8

12

Atkinson, NE

7

37

8

9

-

15

Crofton, NE

NH

6

20

(2)

0

6

Ethan, SD

NH

31

11

(3)

13

13

Huron, SD

(11)

(12)

(3)

(6)

7

(5)

Highmore, SD

NH

NH

(1)

(4)

(11)

(5)

Bristol, SD

(7)

22

(2)

0

(13)

0

Streeter, ND

NH

(10)

3

6

13

3

Munich, ND

17

8

8

6

(2)

8

Mean

1

12

9

1

3

6

Estimated GHG emissions are based on switchgrass production inputs, cellulosic ethanol production requirements and ethanol distribution (2).

*Negative values (in parentheses) indicate displaced and sequestered CO2 equivalents exceeded total CO2 equivalents in the production of ethanol derived from switchgrass.

†NH, no harvest. All agricultural GHG emissions on nonharvested years were added to the first harvested year. The Atkinson, NE, farm was analyzed as having 2 establishment years.

‡GHG displaced by ethanol (Fig. 5) = [g CO2 equivalent MJ-1 ethanol (Table 5) - 94g CO2 equivalent MJ-1 petroleum]/ 94g CO2 equivalent MJ-1 petroleum (2),

where

g CO2 equivalent MJ-1 ethanol = [Net GHG emissions g CO2 equivalent liter-1/ethanol low heating value (21.2 MJ liter-1)] - ethanol distribution (1.4 g CO2 equivalent MJ-1), where

Net GHG emissions (g CO2 equivalent liter-1) = [agriculture sector GHG emissions (kg CO2 equivalent ha-1)/switchgrass biomass yield (kg ha-1) ´2.63 (kg biomass liter-1 ethanol) ´ 1,000 g kg-1] + [Biorefinery sector GHG emissions (124 g CO2 equivalent liter-1) - coproduct credit (106 g CO2 equivalent liter-1)] (2), where

Agriculture sector GHG emissions (kg CO2 equivalent ha-1) = [Nitrogen fertilizer emissions + herbicide emissions + transportation emissions + diesel emissions + packaging emissions + farm machinery emissions (2) - CO2 sequestered (138.1 kg CO2 per Mg of aboveground biomass; 11)].





Table 6. Energy inputs for switchgrass seed production using typical management practices for USDA-ARS Grain, Forage, and Bioenergy Research Unit (Lincoln, NE)

Seed inputs

Energy values

Source(s) (refs)

Notes

 

MJ ha-1

   

Fertilizer

     

Nitrogen

5488

1, 2

 

Phosphorus

128

1, 2

Amortized for 5 years

Herbicides

2627

1, 2

 

Diesel use

     

Tandem disk

35

5

Amortized for 5 years

Roller harrow

23

5

Amortized for 5 years

Seed drill

45

5

Amortized for 5 years

Fertilizer cart

53

12

 

Sprayer

35

5

 

Row-crop cultivator

227

5

High-residue cultivator

Combine w/grain header

465

5

 

Packaging and Transport

158

1, 2

 

Machinery and labor energy

335

4, 5, 12

 

Electricity

10

1, 2

Processing, cleaning, and storage

Total

9628

   

Seed energy (MJ/kg)

43.8

 

220 kg ha-1 seed yield*

The seed field was assumed to be in production for 5 years.

*Switchgrass seed yields range from 220 to > 1,000 kg ha-1 (13, 14). A seed yield of 220 kg ha-1 was used to give a conservative seed energy value.





Table 7. Diesel use estimates for agricultural field applications in the production of switchgrass

Field application

Diesel use

Source (ref.)

Notes

 

Fixed

   
 

Liter ha-1-

   

Tandem disk

4.59

5

6.4-m rigid tandem disk

Roller harrow

2.99

5

8.5-m packing width

Land roller

3.07

6

12-m rolling width

No-till drill

7.98

5

4.8-m planting width

Fertilizer cart