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Ohio State University Extension


Determining Location of Cellulosic Ethanol Plants in Ohio Based on Availability of Crop Residues

Agriculture and Natural Resources
Yebo Li, Assistant Professor
Randall Reeder, Extension Agricultural Engineer, Department of Food, Agricultural, and Biological Engineering, The Ohio State University

The availability of corn and wheat crop residues was analyzed for each county in Ohio. Results showed that two clusters in western Ohio, each encompassing 17 counties with a collection radius of 50 miles, could provide feedstock for two ethanol plants at a capacity of 5,000 dry tons per day each. This calculation assumes that 35 percent of the corn stover and wheat straw per acre would be removed. These two plants could produce a total of 240 million gallons of ethanol per year.

A big hay bale in an open field.

This fact sheet illustrates the process of evaluating where such facilities might be feasible. Naturally, not every acre of corn or wheat residue in a county would be available, nor would every acre have 35 percent of the residue removed.

World oil prices are the major factor in the demand for ethanol in the U.S. Although low prices for gasoline reduce the demand for ethanol and other bio-based fuels, the long-range prospects are for higher prices; therefore, there is good market potential for these alternative fuels.

Approximately 30 percent of U.S. corn grain is used in ethanol production. Research is continuing on using crop residues (cellulose in corn fodder and wheat straw, for example) as another economical source of ethanol. Crop residues suitable for cellulosic ethanol production will likely be in high demand in the future.

Other regions of Ohio with fewer acres of corn and wheat could grow energy crops such as switchgrass and poplar trees, and could provide mixed feedstocks for a cellulosic ethanol plant. Wood waste and municipal solid waste could also be a feedstock.

Crop Data

Ohio corn production for grain in 2005 and 2006 was about 470 million bushels per year. Among Ohio crops, corn has the greatest potential for cellulosic ethanol production. Corn stover includes stalks, leaves, cobs, and husks and contains approximately 35 percent cellulose, 22 percent hemicellulose, and 18 percent lignin (EERE, 2007). Nationally, the amount of corn stover that can be sustainably collected is estimated to be 80–100 million dry tons per year (Kadam and McMillan, 2003).

Soybean is the second major crop in Ohio, with an annual average harvest of 209 million bushels, but the relatively small amount of residue rapidly degrades in the field and is not considered as a potential feedstock for ethanol production.

Wheat is the third major crop, with 62 million bushels produced per year in 2005 and 2006. Wheat straw contains approximately 33 percent cellulose, 23 percent hemicellulose, and 17 percent lignin and is the second best source among grain crops for cellulosic ethanol production.

OSU researchers studied the distribution of usable crop residues among Ohio counties and calculated amounts of wheat straw and corn stover for each Ohio county (Jeanty et al., 2004).

This fact sheet summarizes the availability of major crop residues (sustainable amount per square mile) in Ohio at the county level (Table 1). The sustainable amount of crop residue in each county was calculated based on the residue yield and a collection factor of 35 percent. Counties were clustered for the purpose of identifying potential feedstock supply areas for future cellulosic ethanol plants.

Sustainable Crop Residue

Crop residues play an important role in protecting the soil surface from water and wind erosion and in helping to maintain nutrient levels, so removing them comes at a cost. Currently in the U.S., most corn stover is tilled or left undisturbed on the field. Previous research has estimated that 20–35 percent can be removed without unduly harming the soil (Nelson, 2002). A collection factor (percentage of crop residue removed from the field) of 35 percent was used in this study.

To estimate the crop residue available, the ratio of corn grain to corn stover was assumed to be 1:1. For wheat, the ratio of grain to straw was assumed to be 1:0.8. Average grain production in 2005 and 2006 was used in our calculations. Accurately estimating the amount of biomass available is essential to evaluate the collection cost for ethanol production.

Ethanol Production Potential

How much ethanol can be produced from a ton of corn stover or wheat straw? The amount varies depending on the composition of the crop residues and the ethanol production technologies.

The National Renewable Energy Laboratory (NREL, 2007) estimates the theoretical ethanol yield for corn stover at 113 gallons per dry ton for an average corn stover composition and assuming that both hexose and pentose sugars are fermented. For this analysis, we assumed an ethanol yield of 73 gallons per dry ton, which is about 64 percent of the theoretical yield. For wheat straw, we used an ethanol yield of 70 gallons per dry ton, based on a study by Kadam and McMillan (2003).

Table 1 summarizes the data for the 43 counties in Ohio with the greatest potential to support cellulosic ethanol production. The hydrolysis technologies assumed are either dilute acid hydrolysis or enzymatic hydrolysis. The fermentation process should be able to convert hexose and some of the pentose.

Biomass Availability

The total sustainable amount of corn stover and wheat straw in Ohio is estimated to be 4.6 and 0.7 million dry tons per year, respectively. The majority (85 percent, or 4.5 million tons) of these crop residues are located in 43 counties in northwestern and west central Ohio.

Figure 1 shows the amount of corn stover for each Ohio county. Figure 2 shows the total amount of corn stover and wheat straw by county.

The corn and wheat biomass availability of each county is distinguished with a different color based on the sustainable amount of crop residue per square mile of total area. Fulton County has the highest total biomass availability at 380 dry tons per square mile. The biomass availability in seven other counties (Henry, Crawford, Mercer, Darke, Van Wert, Wood, and Putnam) exceeds 300 dry tons per square mile.

Bioethanol Production Potential

Total bioethanol potential from crop residues in Ohio was estimated to be about 340 million gallons per year. The bioethanol potential from crop residues in the 43 northwestern and west central counties of Ohio was estimated to be about 300 million gallons per year, or about 85 percent of the total ethanol potential from crop residues in Ohio.

The delivery cost of biomass is the most important factor for the bioethanol producer. Nearly one-third of the biomass ethanol production costs is attributed to the costs of the feedstock, which includes handling costs and payments to the landowner/tenant. Perlack and Turhollow (2003) estimated that corn stover can be collected, stored, and transported to ethanol facilities for about $43–$60 per dry ton using conventional baling equipment. Transportation, collection, baling, and farmer payments accounted for over 90 percent of that total cost.

The scale of the bioethanol conversion facilities is relatively significant for the economy of bioethanol production. Generally, capital costs for ethanol plants increase by 60–70 percent for each doubling of output capacity (Perlack and Turhollow, 2003). As plants increase in capacity, the cost saving from economies of scale will be offset somewhat by increased transportation costs associated with hauling feedstock greater distances. Consequently, determining the ideal location of an ethanol plant involves striking a balance between larger handling capacities and higher feedstock costs.

Based on considerations of economies of scale and biomass availability, the optimal locations of potential ethanol plants in Ohio were determined. Counties with high biomass availability were clustered to provide two ethanol plants with feedstock demands of 6,800 and 5,700 dry tons per day, respectively (Figure 3).

Cluster 1 consists of 17 counties: Crawford, Fulton, Henry, Van Wert, Wood, Putnam, Hardin, Wyandot, Hancock, Sandusky, Seneca, Paulding, Allen, Williams, Defiance, Ottawa, and Lucas. These 17 counties can sustainably produce almost 7,000 dry tons of residues per day, which can supply an ethanol plant with a capacity of 130 million gallons of ethanol per year. The equivalent collection radius for this ethanol plant was estimated to be 50 miles. The equivalent collection radius was calculated based on the total area of the counties in the cluster. The transportation cost for this cluster was estimated to be about $33.75 per ton. Naturally, the actual cost is affected by current fuel prices.

Cluster 2 consists of 17 counties: Mercer, Darke, Auglaize, Madison, Preble, Shelby, Fayette, Miami, Warren, Champaign, Clinton, Clark, Logan, Greene, Union, Montgomery, and Butler. These 17 counties can sustainably produce close to 6,000 dry tons of residues per day, which can supply an ethanol plant with a capacity of 110 million gallons of ethanol per year. The equivalent collection radius for this cluster was estimated to be 50 miles. The transportation cost for this cluster was estimated to be about $34.50 per ton.

These clusters of counties are examples of how to combine counties to provide feedstock for a potential ethanol plant. The location of any future ethanol plant should be determined using the biomass availability of each county.

Ohio counties with fewer crop acres might have other cellulosic biomass such as wood waste or municipal solid waste. It is possible to provide mixed feedstock for a cellulosic ethanol plant in those areas.

A key to improving the economics of transporting the crop residue will be the development of a packing system that increases the density above that of a conventional baler. If the stover and straw were packed to a density of, say, double that of the current big square bales, then the feasible distance to the ethanol plant could be increased and the farmer might receive a higher return.

Table 1. Biomass Availability and Ethanol Potential for the Top 43 Counties of Ohio.
(ranked by biomass/mi2)
Collectable Biomass
Biomass Availability
Ethanol Potential
Corn Stover Wheat Straw Total
1 Fulton 407 136,013 18,714 154,727 380 10,073,000
2 Henry 417 117,285 31,156 148,441 356 9,664,000
3 Crawford 402 118,968 18,841 137,809 343 8,972,000
4 Mercer 463 131,830 19,775 151,605 327 9,870,000
5 Darke 600 172,484 17,480 189,964 317 12,367,000
6 Van Wert 410 109,298 19,425 128,723 314 8,380,000
7 Wood 617 145,284 43,429 188,713 306 12,286,000
8 Putnam 484 107,734 37,974 145,708 301 9,486,000
9 Hardin 470 122,026 14,701 136,727 291 8,901,000
10 Wyandot 406 97,613 19,681 117,294 289 7,636,000
11 Hancock 531 117,459 31,664 149,123 281 9,708,000
12 Auglaize 401 93,257 19,345 112,602 281 7,331,000
13 Madison 465 121,426 8,894 130,320 280 8,484,000
14 Sandusky 409 98,040 16,070 114,110 279 7,429,000
15 Preble 425 113,157 5,210 118,367 279 7,706,000
16 Shelby 409 97,489 13,326 110,816 271 7,214,000
17 Fayette 407 99,173 8,704 107,877 265 7,023,000
18 Miami 407 100,571 6,838 107,409 264 6,993,000
19 Seneca 551 114,389 30,198 144,587 263 9,413,000
20 Pickaway 502 107,669 18,061 125,729 251 8,185,000
21 Paulding 416 70,082 34,103 104,185 250 6,783,000
22 Allen 404 86,146 14,727 100,873 249 6,567,000
23 Champaign 429 101,613 4,863 106,476 248 6,932,000
24 Clinton 411 92,760 4,460 97,220 237 6,329,000
25 Clark 400 88,666 3,381 92,046 230 5,992,000
26 Huron 493 97,161 16,240 113,401 230 7,383,000
27 Marion 404 82,422 10,219 92,641 229 6,031,000
28 Williams 422 75,949 19,466 95,415 226 6,212,000
29 Logan 458 93,897 7,860 101,757 222 6,625,000
30 Greene 415 84,574 4,123 88,697 214 5,774,000
31 Defiance 411 68,667 16,874 85,541 208 5,569,000
32 Erie 255 46,618 6,213 52,830 207 3,439,000
33 Union 437 72,507 10,220 82,727 189 5,386,000
34 Morrow 406 57,296 9,691 66,987 165 4,361,000
35 Ottawa 255 30,470 10,555 41,025 161 2,671,000
36 Fairfield 505 69,638 10,172 79,811 158 5,196,000
37 Delaware 442 52,800 8,830 61,629 139 4,012,000
38 Wayne 555 69,750 7,409 77,159 139 5,023,000
39 Knox 527 65,085 4,002 69,087 131 4,498,000
40 Lucas 340 36,558 5,425 41,983 123 2,733,000
41 Ashland 424 42,678 5,537 48,215 114 3,139,000
42 Montgomery 462 49,708 2,511 52,219 113 3,400,000
43 Licking 687 64,797 4,912 69,709 102 4,538,000
  Total 19,142 3,921,005 621,280 4,542,284 237 295,714,000

Figure 1. Availability of Corn Stover in Ohio on a County Basis.

A map of Ohio showing how much corn stover there is in each county.

Figure 2. Availability of Crop Residues (Corn Stover and Wheat Straw) in Ohio on a County Basis.

A map of Ohio showing how much corn stover and wheat straw there is in each county.

Figure 3. Clusters of Counties for Ethanol Production in Ohio.

A map of Ohio showing how much ethanol is produced in each county.


This analysis was supported by funding from The Ohio State University Department of Food, Agricultural, and Biological Engineering and the Ohio Agricultural Research and Development Center (OARDC). Dr. Harold Keener, Professor of Food, Agricultural, and Biological Engineering, and Mary Wicks, OARDC, assisted with the study. This publication was reviewed by Dr. Erdal Ozkan, Professor of Food, Agricultural, and Biological Engineering.


Energy Efficiency and Renewable Energy Biomass Program. 2007. "Biomass Feedstock Composition and Property Database." Washington, D.C.: U.S. Department of Energy.

Jeanty, P. Wilner, Dave Warren, and Fred Hitzhusen. 2004. "Assessing Ohio's Biomass Resources for Energy Potential Using GIS." Department of Agricultural, Environmental and Development Economics, The Ohio State University. PDF.

Kadam, Kiran L., and James D. McMillan. 2003. "Availability of Corn Stover as a Sustainable Feedstock for Bioethanol Production." Bioresour. Tech., Volume 88, Issue 1: 17–25.

Kerstetter, James D., and John Kim Lyons. 2001. "Logging and Agricultural Residue Supply Curves for the Pacific Northwest." Spokane, WA: Washington State University Energy Program. PDF.

National Renewable Energy Laboratory. 2007. "Theoretical Ethanol Yield Calculator." Washington, D.C.: U.S. Department of Energy.

Nelson, Richard G. 2002. "Resource Assessment and Removal Analysis for Corn Stover and Wheat Straw in the Eastern and Midwestern United States: Rainfall and Wind-induced Soil Erosion Methodology." Biomass Bioenergy, Volume 22, Issue 5: 349–363.

Perlack, R.D., and A.F. Turhollow. 2003. "Feedstock Cost Analysis of Corn Stover Residues for Further Processing." Energy, Volume 28, Issue 14: 1395–1403.

This fact sheet is based on Drs. Yebo Li and Harold Keener's publication titled "County level analysis of crop residues availability for fuel ethanol production in Ohio" published in Transactions of the ASABE 52(1): 313–318.

Originally posted Mar 11, 2011.