### ORNL/TM-2007/109



# Historical Perspective on How and Why Switchgrass was Selected as a “Model” High-Potential Energy Crop

July 2007

Prepared by Lynn Wright Consultant to Bioenergy Resources and Engineering Systems
Environmental Sciences DivisionDOCUMENT AVAILABILITY

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### ORNL/TM-2007/109

.

Environmental Sciences Division



## HISTORICAL PERSPECTIVE ON HOW AND WHY SWITCHGRASS

WAS SELECTED AS A "MODEL" HIGH-POTENTIAL ENERGY

CROP

Lynn Wright, Consultant to Bioenergy Resources and Engineering Systems

Date Published: August 2007

Prepared by

OAK RIDGE NATIONAL LABORATORY Oak Ridge, Tennessee 37831-6283 managed by UT-BATTELLE, LLC

for the

U.S. DEPARTMENT OF ENERGY

under contract DE-AC05-00OR22725

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### CONTENTS

Page

LIST OF FIGURES................................................................................................................ ................ v LIST OF TABLES ................................................................................................................. ..............vii

EXECUTIVE SUMMARY.............................................................................................................. ..... ix

ABSTRACT ....................................................................................................................... .................... 1

1. INTRODUCTION ................................................................................................................ ........... 1

1.1 BIOFUELS FEEDSTOCK DEVELOPMENT PROGRAM BACKGROUND .................... 2

1.2 GOALS OF THE HERBACEOUS CROPS PROGRAM SOLICITATION ......................... 2

2. HERBACEOUS CROP SCREENING ............................................................................................ 4

2.1 DESCRIPTION OF THE HERBACEOUS SCREENING PROJECTS ................................ 4

2.2 SCREENING TRIAL RESU LTS AND RECOMMENDATIONS ....................................... 7 2.1.1 Virginia Tech - Virginia............................................................................................ 8 2.1.2 Auburn University - Alabama................................................................................... 9 2.1.3 Geophyta - Ohio........................................................................................................ 9 2.1.4 Cornell University – New York .............................................................................. 10 2.1.5 Purdue University - Indiana .................................................................................... 11 2.1.6 Iowa State University - Iowa................................................................................... 11 2.1.7 North Dakota State University – North Dakota ...................................................... 12 2.1.8 Oak Ridge National Laboratory - Tennessee .......................................................... 14

3. HERBACEOUS CROP PROGR AM CONSIDERATIONS ......................................................... 15 3.1 HECP GOALS, ANALYSIS AND DATA SYNTHESIS ................................................... 15

3.2 BFDP FUNDING EFFECTS ON MODEL SPECIES SELECTION .................................. 18

4. HIGH POTENTIAL FEEDSTOCKS ............................................................................................ 20

4.1 HERBACEOUS CROPS CONSIDERED HIGH POTENTIAL IN 2006 ........................... 20

4.2 BIOFUELS FEEDSTOCK SELECTION CRITERIA......................................................... 21

4.2.1 1980s Selection criteria........................................................................................... 21

4.2.2 1990s Selection criteria........................................................................................... 22

4.2.3 2000s Selection criteria .......................................................................................... 23

5. CHARACTERISTICS OF TH E SWITCHGRASS “MODEL”..................................................... 26

6. CONCLUSION.................................................................................................................. ............ 30

7. REFERENCES .................................................................................................................. ............ 31 Appendix A: AUBURN UNIVE RSITY YIELD RESULTS ............................................................... 35 Appendix B: GEOPHYTA YIELD RESULTS.................................................................................... 37 Appendix C: PURDUE UNIVERSITY YIELD RESULTS ................................................................ 39 Appendix D: IOWA STATE UNIVERSITY YIELD RESULTS........................................................ 41 Appendix E: NORTH DAKOTA STATE UNIVERSITY YIELD RESULTS.................................... 43



### iii

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### LIST OF FIGURES

Figure Page

1 Location of herbaceous cr ops field testing sites ................................................................. 4 2 Woody and herbaceous species considered by the Department of Energy’s Biofuels Feedstock Development Program in 1991 as having high potential as energy crop

feedstocks..................................................................................................................... ..... 18 3 Funding History of the Biofuels F eedstock Development Program between 1978

and 1998....................................................................................................................... ..... 19



### v

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### LIST OF TABLES

Table Page

1 Species screened by the Herbaceous Crops Program between 1986 and 1992 .................. 5 2 Descriptions of herbaceous crop screening test sites .......................................................... 6 3 Mean biomass yield averaged across 12 sites for eight herbaceous biomass species on three soil types in the Piedmont of Virginia .................................................................. 8 4 Average yields of the three highest-yield consecutive years during the first 5 years of production of perennial biomass crops gr own in the eastern Great Lakes Region....... 10 5 Yields of herbaceous biomass crops grown at four sites in Indiana during the drought year of 1988......................................................................................................... 12 6 Costs and break-even prices of the crop production systems evaluated in Iowa

1988-1992 ...................................................................................................................... ... 13 7 Computed soil loss (mean of three sites) of eight no-till-planted species at four locations (three soils) in the Piedmont.............................................................................. 16 8 Estimated soil loss under thirteen crop systems at two Iowa locations using the Universal Soil Loss Equation (USLE).............................................................................. 16 9 Species recommended for further development or study by the seven herbaceous screening projects . ........................................................................................................... 17 10 Feedstock criteria, criteria relevance categories, and ranking (high, medium and low) of the capability of switchgrass to m eet those criteria for cellulosic ethanol production systems ........................................................................................................... 26



### vii

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### ACKNOWLEDGMENTS

Thanks to Anthony Turhollow, Shahabaddine Sokha nsanj, Ethan Davis, Robert Perlack and Mark Downing for their reviews of the document. Much credit goes to Janet Cushman, Anthony Turhollow, Sandy McLaughlin and Lynn Kszos for th e many reports and pape rs on herbaceous crops they prepared during their tenures as manager and/or project leaders of herbaceous crops research at ORNL during the 1980s and 1990s. Those documents provided a great deal of the information summarized in this paper. Much credit also goes to the many researchers who carried out the herbaceous crops screening trials and concluded those trials with excellent report documenting the results. I thank the current managers of the biom ass research effort at Oak Ridge National Laboratory (ORNL), Jonathon Mielenz and Mark Downing, fo r allowing me the opportunity to continue to contribute to the biomass effort by providing historical documentation of a significant decision made by the program during my tenure as a biomass research leader at ORNL. Most importantly, I would also like to acknowledge the long term support of energy crops research since 1978 by the Department of Energy’s Biomass Program within the office of Energy Efficiency and Renewable Energy and particularly the support of John Ferrell, Sarah Sprague and other feedstock program

managers.

EXECUTIVE SUMMARY

The screening trials funded by the U.S. Departme nt of Energy in the late 1980s to early 1990s assessed a wide range of about 34 species with trials being conducted on a wide range of soil types in 31 different sites spread over seven states in crop producing regions of the U.S. While several species were identified as having merit for further developmen t, the majority of institutions involved in the herbaceous species screening studies identified switchgrass as having high priority for further development. Six of the seven institutions e ither included switchgrass among the 2-3 species with highest potential in their region, or recommended that further research be done on switchgrass in their region. All institutions recommended that perenni al grasses be given high research priority. The Virginia and Alabama projects, had the most su ccess with switchgrass and produced some of the most persuasive information showing the merits of sw itchgrass – especially the potential for high yields, its deep rooting characteristics, and its potential value in carbon sequestration. The projects in Indiana, Iowa, and North Dakota all came to the conclusion that switchgrass merited further development as a bioenergy crop primarily after conducting economic anal ysis, since visual results of crop yields most often led toward favoring sorghum systems. In some cases, additional characteristics such as more

favorable conversion characteristics or lower erosi on potential increased the interest in switchgrass. In the case of the projects in Ohio and New York, bot h with several poorly drained test sites, the case for switchgrass was not as strong due to problems with establishment and weed control. The New York project did conclude that switchgrass had d esirable characteristics and should receive more evaluation in the region. The Geophyta project did not include switchgrass among the top three yielding crops in their trials, but it was the 4 th 

### best performer and was achieving yields equivalent to or greater than other crops by the 4 th 

### year of the study. The other crop(s) which were identified as having high potential by several of the projects included some type of sorghum (sweet sorghum, forage sorghum or sorghum x sudangrass) and reed canarygrass. Additionally, there were a few species or species mixtures unique to a single site that appeared to merit further consideration such as sericea lespedeza and energy cane in Alabama and al falfa/bromegrass in New York. The Oak Ridge project and at least three of the screening projects also identified mixed species “meadow”, “old field” or “weed” trials as possibly being economically vi able production systems even though yields were relatively low.



### ix

### Economic and environmental assessments by Oak Ri dge National Laboratory’s Biofuels Feedstock Development Program staff together with the screen ing project results and funding limitations lead to making the decision in 1991 to invest future Department of Energy research funds primarily in switchgrass as a “model” or “prototype” bioenergy cr op. This selection was justified in the 1992 Annual Progress Report (1) 

### of the Department of Energy’s Bi ofuels Feedstock Development Program (BFDP) with the following statement:

“ In 1984, a series of ten herbaceous research projects began at widespread locations across the eastern and Midwestern United States. A total of 35 species was examined in these initial screening studies, which were designed to examine yield potential, biochemical composition, and best management practices across a wide diversity of sites. The completion of several of these studies and the examination of data on yield potential, production economics, and regional site potential, led in 1991 to the selecti on of a perennial forage grass switchgrass as a model species for further research.

The rational for selection of a single species was to concentrate and thereby improve the overall efficiency of the many interrelated asp ects of research that were seen as requisite for biofuels production. Although more than one species will certainly be required ultimately, switchgrass was seen as an excellent beginning with the available programmatic resources.

The selection of switchgrass as a model species was based on several important considerations. As a widely adapted endemic species of the tall grass prairies, switchgrass has demonstrated a capacity for high yields on relative poor quality sites. Maximum annual yields on test plots in Auburn, Alabama, have been 33 dry Mg ha -1 

### , well above the production level considered prerequisite for a successful biof uels industry. A large and deep root system is the key to high production and soil improvement on poor quality sites. Research at Virginia Polytechnic Institute and State Uni versity has shown that soil organic carbon was increased by 30% during a 4-year cycle, indicating that switchgrass has a significant capacity to improve soil quality by sequest ering carbon belowground. Improved erosion control, reduced fertilizer and pesticide requi rements and a capacity for providing wildlife cover are additional positive environmental attributes. An important quality of switchgrass is its strong potential appeal to landowners, for whom cultivation of a perennial crop that can be grown, harvested, and stored with conventional equipment represents an easy interface with current agricultural practices.”

It should be noted that the exceptionally high yield of 33 dry Mg ha -1 

### was not an outcome of the original herbaceous screening trials, but was observed in 1989 in a 2 nd 

### year switchgrass variety trial established by Auburn University in 1988, mid-way during the screening trial phase of work. The results were published in 1991. (2) 

### This variety trial showed that the original switchgrass variety chosen for the screening trials (Cave-in-Rock) w as probably not the best selection for many of the screening locations. The high yield potential of the new variety, Alamo, was first identified by the

Auburn trial.

Selection of switchgrass as a model species in 1991 lead to a switchgrass specific solicitation and then to 10 years of switchgrass development at ten institutions under the management of Sandy McLaughlin and others at ORNL. (3) 

### More recently switchgrass has been the focus of investigations at several additional universities and private institutions. New varieties have been developed and released, management techniques have been impr oved, and much more is now known about how switchgrass can be harvested, handled, stored and c onverted to ethanol or used to produce power. Now, in 2007, it is very apparent that while sw itchgrass may not be a perfect energy crop (and there may not be a perfect crop), it has many valuable char acteristics that will result in its continuing to be



### x

### xi not only a “model or prototype” for crop development, but also one of the more sustainable feedstocks for the production of renewable alternative fuels in the U.S.

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### ABSTRACT

A review of several publications of the Biofuels Feedstock Development Program, and final reports from the herbaceous crop screening trials suggests that there were several technical and non-technical

factors that influenced the decision to focus on one herbaceous “model” crop species. The screening trials funded by the U.S. Department of Energy in the late 1980s to early 1990s assessed a wide range of about 34 species with trials being conducted on a wide range of soil types in 31 different sites spread over seven states in crop producing regions of the U.S. While several species, including sorghums, reed canarygrass and other crops, were id entified as having merit for further development, the majority of institutions involved in the he rbaceous species screening studies identified switchgrass as having high priority for further development. Six of the seven institutions included switchgrass among the species recommended for further devel opment in their region and all institutions recommended that perennial grasses be given high r esearch priority. Reasons for the selection of switchgrass included the demonstration of relativ ely high, reliable productivity across a wide geographical range, suitability for marginal quality land, low water and nutrient requirements, and positive environmental attributes. Economic and environmental assessments by Oak Ridge National Laboratory’s Biofuels Feedstock Development Program staff together with the screening project results, and funding limitations lead to making th e decision to further develop only switchgrass as a “model” or “prototype” species in about 1990. Th is paper describes the conditions under which the herbaceous species were screened, summarizes results from those trials, discusses the various factors which influenced the selection of switchgrass, and provides a brief evaluation of switchgrass with respect to criteria that should be considered wh en selecting and developing a crop for biofuels and bioproducts.

1. INTRODUCTION

Switchgrass was selected as a “model” energy crop species deserving of further research in 1991. This selection was briefly explained and justified in at least three previous publications of Oak Ridge National Laboratory including the 1992 Annual Progress Report (1) 

### of the BFDP, a proceedings paper published in 1992, (4) 

### and the switchgrass research summary paper published in 2005. (3)



### The 1992 proceedings paper by McLaughlin (4) 

### described several important considerations for selecting switchgrass as the model species. A very important one was that the land base for switchgrass was believed to be quite large and va ried because of demonstrated high yields on relatively poor quality sites and because of its deep rooting characteristic. McLaughlin noted that the land most likely to be used for herbaceous crop production is the approximately 48 million acres of marginal land that has severe restrictions for conventional crop production. Given the assumption that such land would be utilized for production of sw itchgrass, then a wide range of environmental benefits could occur including improvement of soil carbon by sequestering carbon belowground, improved erosion control, reduced fertilizer and pesticide requirements (relative to conventional annual crops), and a capacity for providing wildlife c over. Similar reasons were described in the 1982 Annual Progress Report of the BFDP and quoted in the executive summary of this document.

The focus on a single species was a departure from the original strategy envisioned by the managers of the Herbaceous Crops Program (HECP) at Oa k Ridge National Laboratory (ORNL). A 1991 paper presented by the ORNL Herbaceous Crops Progr am managers at a national biomass meeting (5)


### described the desirability of selecting at least one annual, one perennial, and one legume for further

research.



### 1

### A review of several publications of the Biofuels Feedstock Development Program, and final reports from the Herbaceous Crop screening trials suggests th at there were both technical and non-technical

factors that influenced the decision to focus on one herbaceous “model” crop species. This paper will summarize reported results, discuss the various factor s which influenced the selection of switchgrass, and provide a brief updated evaluation of switchgrass with respect to selection criteria considered important then and now.

1.1 BIOFUELS FEEDSTOCK DEVELOPMENT PROGRAM BACKGROUND

The Department of Energy became involved in supporting the development of biomass resources as early as 1976 when DOE’s Biomass Systems Branch initially funded several systems analysis studies on sugar crops, agricultural residues, wood energy farms, grains and grasses and aquatic plant production. DOE’s first funded field studies on bioe nergy crops in 1977 by co-funding work that had been initiated by USDA on woody crops, sugar cane, and tropical grasses. DOE quickly established its own energy crop research effort with the issuance of two Program Research and Development Announcements on “Fuels from Woody Biomass” and “Fuels from Aquatic Species”. Oak Ridge National Laboratory was asked by DOE in 1978 to provide advice and support in the selection and management of the woody biomass projects and th e Solar Energy Research Institute supported the aquatic research effort. By 1982, DOE had fu lly transferred technical and administrative management of the Short Rotation Woody Crops Program to ORNL and by 1984, DOE provided funds to ORNL to develop an He rbaceous Energy Crops Program.

Prevailing assumptions in the early 1980s about best potential herbaceous energy crops species are documented by a publication entitled “The Producti on of Herbaceous Feedstocks for Renewable Energy”, published September 1986 by the Solar Energy Research Institute. (6) 

### This document described the major reasons for in terest in herbaceous crops including: (1) the idea that it would be relatively easy for the agricultural production sector to switch to production of herbaceous biomass crops, (2) the assumption that alternative crops coul d be attractive to a depressed farm economy, and (3) that herbaceous crops might be more suitabl e than woody crops as feedstocks for fermentation alcohol and anaerobic digestion. However, it is interesting that the twelve “representative” herbaceous crops described by the SERI document (6) 

### included crops grown for both carbohydrate and cellulosic components. The carbohydrate crops in cluded sugarcane, sweet sorghum, sweet-stemmed grain sorghum, Jerusalem artichoke, sugar beets, and fodder beets. The lignocellulosic crops described included kenaf, napiergrass, alfalfa, reed canarygrass, common reed, and water hyacinth. After reviewing all of the pros and cons of various approaches, the Herbaceous Crops Program Managers at ORNL chose to develop a program so licitation that excluded crops grown primarily for carbohydrates and instead chose to solicit proposals limited to research on cellulosic crops. The goals of the original program solicitation were very importa nt to setting the agenda and the basic criteria for selecting species for further development.

1.2 GOALS OF THE HERBACEOUS CROPS PROGRAM SOLICITATION

The Herbaceous Energy Crops Program (HECP) w as initiated in 1984 with a request for proposals (RFP) focused on the southeast (exclusive of subtropical areas) and the Midwest/lake States. (7) 

### The focus on grass and legume herbage was based on a government report (8) 

### that had identified these biomass resources as second in size only to wood. The overall goal of the HECP was stated to be “to develop data and information that will lead to comm ercially viable systems for producing herbaceous biomass for fuels and energy feedstocks .” A very important element of the HECP was the desire to achieve the goal in ways that would minimize adverse environmental effects. (9) 

### The direction of the



### 2

### HECP and some of the important criteria were clearly established in the technical discussion section

of the initial RFP (7) 

### as evidenced by the following wo rds in the proposal description:

“ Three major factors influ enced the initial focus of research in the program. First was the desire to increase the production of biomass for energy without significantly reducing food production. This led to the decision to concentrate on species for marginal croplands and on species that can be grown as winter crops. Second was the decision to produce fuels or energy feedstocks rather than chem icals. This meant the progr am would initially include a minimum of research on hydrocarbon crops, bec ause evaluations of hydrocarbon-producing species that will grow in the United States ha ve concluded that the hydrocarbon productions will be more valuable as specialty chemicals, pr imarily lubricants, than fuels. Third was the desire to have the greatest possible impact on to tal biomass energy use. This led to the decision to emphasize lignocellulosic crops. ”

Proposals were scored on the basis of (1) demons tration of a through understanding of the proposed work, (2) application of the proposed work of the Herbaceous Energy Crops Program to the targeted regions, (3) the degree of private sector participa tion, (4) qualifications of the personnel, and (5) availability of facilities and equipment.

While the initial work focused on screening species to identify high-potential candidates, the

solicitation’s statement of work (7) 

### recommended that different intens ities of management be part of the initial screening process. The statement of work also clarified that while the focus was on marginal land, the proposals should include a range of site types, including some good agricultural land, so that relationships among site quality, management inputs, and yields could be established. Land was considered to be marginal if it w as limited by erosiveness, excessive wetness, soil chemistry constraints, rooting constraints, or climate issues. While the original RFP (7) 

### did not explicitly state that environmental concerns would be a factor in the selection of species for further research, the fact that an evaluation of soil loss potential was a required component of the proposals demonstrated a concern for environmental effects of the cropping systems.

Responsive proposals were required to screen at least two species, one of which had to be a forage or hay crop commonly grown in the test site region. The other crop(s) could be annual or perennial and they could be common or less common species, howev er their inclusion had to be explained and justified. Thirteen proposals were received from a to tal of twelve institutions. Several of those were deemed not responsive to the RFP (7) 

### either because of the species proposed or because the trials would be located in sub-tropical regions of the country. Thus, only seven proposals merited serious review. Five organizations were selected to pa rticipate in the southeastern and Midwest species screening trials that began in 1985. The HECP annual report for 1985 (10) 

### described the recently initiated herbaceous crop screening research projects and defended the rational for focusing the research in the southeast and Midwest/lake areas. Those regions were chosen for study because large areas of marginal cropland are potentially availa ble and there are relatively few environmental restrictions on productivity. In 1988, two additiona l institutions were added to the species screening effort to achieve a broader coverage of potentially available site types.



### 3

### 2. HERBACEOUS CROP SCREENING

2.1 DESCRIPTIONS OF THE HERBACEOUS SCREENING PROJECTS

Six universities and one private company were select ed to participate in the herbaceous screening projects (Fig. 1). The universities included Cornell University, Virginia Polytechnic Institute and State University (referred to as Virginia Tech), Auburn University, Purdue University, Iowa State University, and North Dakota State University. The seventh research group was a small company in Ohio named Geophyta.

Figure 1. Location of herba ceous crop field testing sites



### The proposals included the testing of warm season, cool season, and leguminous perennials in each

area as well as several annuals. Annuals were also planted for comparison purposes. Table 1 shows the full range of species tested by each instituti on involved in herbaceous screening research. Table 2 provides information about each of the test sites used for the screening trials in the southeast, Midwest/Lake, and Great Plains regions respectively.



### 4

### Table 1. Species screened by Herbaceous Crops Program 1986-1992

Species Institution and year of project start

VA Tech Auburn Geophyta Cornell Purdue ISU 1 NDSU 2

1985 1985 1985 1985 1985 1988 1988
Grasses: Annual Corn (w) X X X X Pearl millet (w) X 4 Foxtail millet (w) X Rye (c) X 3 X 3 X 3 X 3 Sorghum, Forage (w) X X Sorghum, Sweet (w) X 4 X X Sorghum x sudangrass (w) X X X Sudangrass (w) X
Grasses:Perennial Bahiagrass (w) X Bermudagrass (w) X 4 Big bluestem (w) X X Crested wheatgrass (c) X CRP mixture of grasses (c/w) X Eastern gamagrass (c) X Energy Cane (w) X Intermediate wheatgrass (c) X Johnsongrass (w) X 4 Napiergrass (w) Redtop (c) X Reed canarygrass (c) X X X 5 X X Smooth bromegrass (c) X Switchgrass (w) X X X X X X X Tall Fescue (c) X X X X 5 Timothy (c) /redtop (c)/ clover X X Weeping lovegrass (w) X X Wheatgrass mixture (c) X Legumes: Annual Soybeans X Legumes: Perennial

Alfalfa X X 6 X X 7 X 6

Birdsfoot trefoil X X X X
Crownvetch X Flatpea X X Serecia lespedeza X X X
Sweet clover X X
Other Forage brassica X
Kale X Meadow (mixed grasses & legumes) X Note: The grasses are designated as either cool season (c) or wa rm season (w) crops.

1 ISU = Iowa State University

2 NDSU = North Dakota State University

3 Rye was always interseeded among other sp ecies or as the cool seas on species in a double crop system – most often with sorghums

4 These crops were frequently the base speci es in a double-cropping or intercropping systems

5 Reed canary grass and tall fescue were gr own alone and interseeded with sorghum

6 Alfalfa was intercropped with bromegrass at both Cornell and NDSU, and also grown alone at NDSU

7 Alfalfa was intercropped with sorghum and sorghum x sudangrass



### 5Table 2. Descriptions of herb aceous crop screening test sites

Location name Soil type Slope and class Quality Limitation(s) Virginia Tech (Virginia) 3 locations, __ sites, soils representa tive of the piedmont region of the southeastern U.S., sloping, southw est facing (hot and dry) (11,12) Lunenberg County Appling sandy loam 6 & 7% slopes Poor,

Coarse textured Strongly acidic highly erosive

low nutrient Amelia County NE facing slopes

3 sites Cecil 8 & 9% slopes Poor, Long-term erosion Acidic highly erosive

Orange County Davison 9 &10% slopes Not quite as poor Strongly acidic, highly erosive Auburn (Alabama) 4 sites represent the physiographic provinces of AL, “all soils good for crop production if erosion minimized on slopes” (13)

Camden – Lower coastal plain Mabis fine sandy loam NA NA Fragipan and acidic subsoil,

erosive Winfield – Upper coastal plain Savannah

loam 2-10% slopes NA Fragipan and

erosive Camp Hill- Piedmont Cecil sandy loam NA NA Acidic, erosive

Crossville- Sand

Mountain site Hartsells fine sandy loam 2-5% slopes NA Erosive on slopes

Geophyta (Ohio) 3 sites in northeast part of stat e with varying levels of wetness compared (14)

Site 1 Toledo or Lucus silty clay 0-2% Adequate soil pH and high fertility Occasional wetness

Site 2 Toledo or Lucus silty clay 2-6% Adequate soil pH and fertility Moderate wetness,

no tile

Site 3 Toledo or Lucus silty clay 0-2% Low soil pH, low

available P Frequent wetness,

no tile Purdue (Indiana) 3 regions of state, range of soil qualities and slope effects compared (15) Purdue Agronomy

Farm Chalmers silty clay loam 0-2% slope Good Minimal

SIPAC (Southern Purdue Agricultural Center) Zanesville

silt loam 8-12% slope Marginal, Previous crop tall fescue Fragipan, erosion, droughty

SEPAC (Southeastern Purdue Agricultural Center) Cincinnati

silt loam 8-10% slope Marginal, Previous crop tilled corn Erosion, fragipan, poor drainage

T-FLAT (West central

Throckmorton Purdue Agricultural Center) Slidell

silt loam 0-2% slope Excellent, Previous crop tilled corn Minimal

T-SLOPE (West central

Throckmorton Purdue Agricultural Center) Slidell

silt loam 6-8% slope Excellent, Previous crop tilled corn Erosion

Cornell (New York) 8 sites with 6 soil series, each a unique combination of use and production limitations (16)
Poole farm Geneva, Honeoye, 10% slope Excellent Erosion



### 6NY silt loam Aurora, NY Finger

Lakes area Kendia,

silt loam Minimal Prime None

Mt Pleasant farm, Freeville, NY

Mid-south NY Mardin, acid glacial till Minimal Marginal Strongly acid, low fertility, fragipan
Halme farm, Ithaca, NY Finger lakes Erie soil,

fine silt Minimal Marginal Wetness, acidity, stones, low-fertility
Caldwell farm, Ithaca,

NY Collamar,

fine textured Less slope Marginal Erodible

Caldwell farm, Ithaca,

NY Collamar,

fine textured More slope Marginal Erodible

Willsboro farm Northeast, NY Rhinebeck, fine texture clay Minimal Marginal Wetness

Willsboro farm Northeast, NY Mardin, fine texture clay Minimal Marginal Wetness

Iowa State (Iowa) 2 regions of state plus good and marginal soils compared (17)

Ames –central Iowa Harps soil Silty clay loam 0-1% slope

Class I

SOM = 7% Highly productive Corn/soybean/oat

rotation in 1987 pH of 8.0 2 m rooting depth

Chariton – southern

Iowa Clarinda, Cearfield and Grundy soils 2-7% slope

Class III

SOM 4% Lower productivity

soil

Conventional red clover prior use Erosive Droughty pH of 6.8

North Dakota State Univ (ND) 5 dryland sites and 1 irrigated site representing 3 major soil areas in North Dakota (18) (1) Prosper Red River Valley Gardena

Silt loam level Productive,

Lacustrine sediments Moderate rainfall

(2) Hettinger

Missouri Plateau Shambo

Silt loam 0-2% Productive, Alluvium Very low rainfall

(3) Glenfield a

Drift Prairie Barnes loam to

Siva loam NA Productive, Glacial

till Low rainfall

(4) Leonard Red River Valley Hecla Loamy fine sand Nearly level Marginal,CRP land Wind erosion

Moderate rainfall (5) Glenfield b

Drift Prairie Buse loam Crests of hills Marginal, CRP land,

Glacial till Low rainfall

(6) Carrington Emrick loam level Productive with irrigation; glacial till Requires irrigation



### 2.2 SCREENING TRIAL RESULTS AND RECOMMENDATIONS

Yields of each crop were quite variable between i nvestigators, sites, and years representing not only site and climate variations but also a lack of experience in growing some of the perennial grasses as crops. Yield results derived from tables in the fina l reports of the herbaceous crop screening trials are either included in the descriptions below (if short) or provided in the appendixes (if long). Because climate conditions had a large effect on establishm ent success and yield results, particular notice is made of the principal investigators comments about climate conditions during their trials. When final reports included recommendations for further resear ch, an effort is made to capture those

recommendations in the discussion below about each of the herbaceous crop screening projects. An eighth project, a study of the potential of successional ve getation to be a bioenergy feedstock, is also

described.



### 7

### 2.1.1 Virginia Tech - Virginia

Parrish et al. reported in 1990 (11) 

### that initial screening results were heavily affected by the severe drought that occurred during the first 4 weeks after the initial planting in 1985. Warm season perennial grasses survived but cool season grasses had to be reseeded several times in 1986 and grew poorly in 1987. These were both years with a moisture deficit. Rainfall was more nearly adequate in 1988 and 1989, resulting in the cool season grasses and legumes showing a good response to the rainfall. However, across the 4 post-establishment years (86-89) with 2 years of drought and 2 years of average or above average rain, switchgrass clearly outperformed all the other species being tested including sorghum x sudangrass on 3 marginal agricultu ral soils (Table 3). Yields of sorghum x sudangrass were 3 times that of switchgrass in the est ablishment year (1985) and slightly higher in 1986, but through the rest of the study sorghum x sudangrass yields trended downward while switchgrass yields continued to increase. On one site sorghum x sudangrass experienced near or complete failure in 2 years. Averaged over sites and years, the cool season grasses achieved an average of between 5 and 6 Mg ha -1 

### yr -1 

### . Switchgrass averaged 10.6 Mg ha -1 

### yr -1 

### , and weeping lovegrass, also a warm season grass, averaged 9.3 Mg ha -1 

### yr -1 

### . These two species were recommended for further study by the Virginia Tech investigators. Following their own recommendations, Virginia Tech researchers initiated management studies focusing on switchgrass and weeping lovegrass in 1988. (12) 

### While both species continued to show promise as relatively low input energy crops, yields and stand vigor declined in the weeping lovegrass trials after 4 years, thus switchgrass seemed to be the most promising species. More detailed studies on switchgrass by Virginia Tech demonstrated that no-till management could be successfully used to establish perennial grasses and to reduce soil loss on sloping marginal land and that the deep rooting depth of switchgrass was a contributor to its productivity and to soil carbon enhancement.

Table 3. Mean annual biomass yield averaged across 12 sites for eight herbaceo us biomass species on three soil types in the Piedmont of Virginia.

Species 1986 1987 1988 1989 4-Year Avg

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

------------------------------------------

Warm-Season

Sorghum-sudan 8.6 7.9 9.5 4.7 7.7 Lovegrass 8.7 8.9 11.2 8.2 9.3 Switchgrass 7.8 10.8 11.9 11.8 10.6

Sericea 3.1 6.4 7.7 7.4 6.1

Cool-Season

Tall fescue 1.9 7.1 5.2 5.9 5.0

Crownvetch 0.9 4.1 8.2 9.7 5.7

Trefoil 1.0 6.5 6.0 7.4 5.2 Flatpea 1.6 3.5 4.9 10.7 5.2

Note: Table reproduced from Parish et al. (11)



### 8

### 2.1.2 Auburn University – Alabama

The rainfall data reported by Bransby et al. (13) 

### showed that across 4 physiographic regions in Alabama, growing season rainfall was near normal in the first two years (1985 and 1986), substantially below normal in 1987, and normal in 1988 and above normal in 1989. Yields of annual species were some to much higher than perennials in years of moderate to good rainfall but lower than perennials in lower rainfall years (Appendix A) . For example, sweet sorghum yields varied from a mean of 17.93 Mg

ha -1 

### yr -1 

### in 1985 to a low of 3.8 ha -1 

### yr -1 

### in 1987. Although switchgrass yields were low in the establishment year (2.44 Mg ha -1 

### ), yields increased over the next 4 years showing relatively little response to precipitation. The higher yield vari ability plus higher production costs of the annuals lead to the recommendation to drop annuals and to focus on perennials for future crop development. Johnsongrass, a warm season perennial “weed”, performed better than other perennials in the first two seasons. This was attributed to its larger seed size but johnsongrass growth decreased over time and

was correlated with an increase in disease and soil compaction. All other warm season perennials, switchgrass, bermudagrass, and sericea lespedeza established more slowly but continued to increase yields over the 5 years achieving an average of 9 Mg ha -1 

### yr -1 

### . The success and reliability of the perennials encouraged the Auburn University inves tigators to add evaluations of sub-tropical tall grasses in 1987 and a variety trial of switchgrass to the project in 1988. The tall grasses quickly achieved very high annual yields ranging from 12.2 up to 32.4 Mg ha -1 

### with energy cane showing the highest yields (16.5 to 32.4 Mg ha -1 

### ). The switchgrass established quickly in the normal rainfall year of 1988 and by 1989 the variety, Alamo, had achieved yields of 17.5 Mg ha -1 

### , double that of the original test variety, Cave-in-Rock. The final report (13) recommended that further research should focus on only a few perennial species such as switchgrass, lespedeza, and energy cane. The advantages of switchgrass were described as: (a ) it can be established from seed, (b) it can be harvested and stored as hay, (c) it can be used for both biomass and forage, (d) it has relatively low lignin content, and (e) the high genetic variability with the species provides excellent opportunities for improvement by selection and breeding. Bransby’s discovery of the high yield potential of the switchgrass variety, Alamo, was a major factor in the acceptance of switchgrass as a suitable model species. (2)



### 2.1.3 Geophyta – Ohio

Wright reported in 1990 (14) 

### that planting efforts in 1985 and 1986 were affected by a combination of heavy rains initially followed by no or low amounts of rain. Wetness was a problem for only long enough to negatively affecting planting. Rainfa ll was not mentioned for 1987 and 1989, thus was

assumed to be normal. 1988 was described as extremel y dry. The investigator identified the most promising energy crops of the 10 evaluated in a wet area of northern Ohio as forage sorghum, rye cropped with sorghum x sudangrass, and reed canaryg rass. However an investigation of the data, (Appendix C) shows that switchgrass showed the ne xt highest average yields and demonstrated greater reliability. The switchgrass did establish at a ll three sites (which the reed canarygrass did not) and the switchgrass yields (4.1 – 9.0 Mg ha -1 

### ) were only a little less than those of reed canarygrass (5.1-10.3 Mg ha -1 

### ) on the two sites where both crops could be compared. Both of these grasses had their best yields in the 4 th 

### year (1989) when forage sorghum yiel ds were very poor. Rye cropped with sorghum x sudangrass (yields ranging from 7.9 to 23 Mg ha -1 

### ) produced more reliable yields than forage sorghum alone, which had establishment failu res in 1988 and 1989. The investigator did note that the cool season grasses (including reed canarygrass) always had green leaves (higher nutrient levels) at fall harvest, while switchgrass and sorghum had the lowest nutrient concentrations at fall harvest (suggesting greater potential for sustainable production).



### 9

### An interesting side observation of the study was that in control plots with no weed control it was noted that weed growth provided the majority of the biomass and weed-only plots provided respectable yields. Weed plots fertilized at the same level as the double crop of rye and sorghum x sudangrass produced yields in the range of 3.5 to 4.2 Mg ha -1 

### . While the rye/sorghum x sudangrass combination produced much higher yields, the inves tigator noted that compared to the complete establishment failures that occurred with some crops in some years the idea of fertilizing abandoned

fields merited further consideration. (14)



### 2.1.4 Cornell University – New York

Precipitation patterns in the Cornell University tr ials varied among the seven locations where crops

were evaluated (15, 19) 

### but followed a similar pattern to that experienced at other screening trials. The years of 1985 and 1988 experienced somewhat to seriously below normal precipitation, 1986 was closer to normal, 1987 had above and below nor mal precipitation depending on location, and 1989 was generally normal or above for all sites. Eight energy crop species plus a “meadow” trial were evaluated. Yield results were relatively similar for most of the species tested (in the range of 4 to 10 Mg ha -1 

### ) during the 3 best years (out of 5) of yield results (Table 4). Evaluation of the potential for energy crops in the region was based on modeling studies as well as on field trials. The investigators concluded that “careful management of better-dra ined” soil resources and proper selection of plant species grown for biomass will provide an annual yield of dry matter in the Great Lakes Region on the order of 10-12 Mg ha -1 

### . The recommendations for the species with highest potential as a bioenergy crop varied for well drained versus the poorly drained soils.

On moderately to well drained soils, the legume mixtures, alfalfa-bromegrass and timothy-redtop-red clover were considered to be the most promising. (19) 

### Switchgrass was identified as showing promise for well-drained sites, but the establishment problems and weed competition experienced in the trials were a concern. The investigators did suggest that the variety used in the trials (Cave-in-Rock) was possibly not the best choice for the area and that more work on switchgrass was merited for the Great Lakes Region. On poorly drained soils, reed can arygrass out yielded all other species with average yields of about 7 Mg ha -1 

### yr -1 

### . It was recommended as a high potential species for poorly drained soils under a one-cut harvest system timed to coincide with drier soil conditions. The relatively low-input meadow plots were also observed to have potential fo r wet soils where tillage is not possible, with an average yield potential of 5 to 7 Mg ha -1 

### yr -1 

### with one or two harvests/year.

Table 4. Average yields of the three highest-yield co nsecutive years during the first 5 years of production for perennial biomass crops grown in the eastern Great lakes Region Moderately to well drained sites Poorly drained sites

Collamer Collamer (eroded) Honeoye (eroded) Mardin Madalin Rhinebeck Erie

Species or

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

-------------------------------------------------------

Alfalfa/ smooth bromegrass 8.88ab 10.01a 11.30a

Eastern

gamagrass 6.07b

Flatpea 9.48a 8.66b 9.49b 7.45a

Naturalized

meadow 5.53ab 5.25ab 5.61b

Reed canarygrass 7.13a 6.80a 9.02a Switchgrass 8.76ab 8.53b 5.79d 4.36b 4.85b 4.17b Timothy mixture 8.15b 10.14a 7. 04c 7.35a 5.62ab 5.16ab 5.83b
Note: means within a column followed by the sa me letter are not significantly different (P> 0.05).



### 10

### 2.1.5 Purdue University - Indiana

Cherney et al. reported in 1990 (16) 

### that climate included both normal and droughty conditions during the years of 1985-1989 at all four sites used in t esting, but no details were provided. The study evaluated 12 herbaceous crop species with some bei ng considered both alone and as intercrop species. Of the perennial species investigated, switchgrass w as deemed to have the greatest biomass potential yielding up to 16 Mg ha -1 

### in one season with two cuttings. When grown with minimal fertilizer inputs and one harvest per year, switchgrass was superior in yield to tall fescue, reed canarygrass, alfalfa, birdsfoot trefoil, weeping lovegrass, big bluestem, and sericea lespedeza. Annual yields of the switchgrass (Cave-in-Rock) were in the range of 7-16 Mg ha -1 

### with the lowest yield occurring in the drought year of 1988. Comparison of yields am ong crops in 1988 (a drought year) highlights the relative similarity of yields of several perenni al grasses across good and poor sites in comparison with alfalfa and sorghums (Table 5). Advantages of switchgrass were described to be its minimum fertilizer input requirements, its persistence, and its effectiveness in reducing soil erosion. Establishment problems did occur with switchgrass at the poorest site. Response of switchgrass to fertilizer varied from year to year, but the greatest response was always between 0 and 50 kg N ha -1


### with higher levels producing some to little additional response (Appendix D).

Of the annual species evaluated, sweet sorghum produced higher yields than sorghum-sundangrass and corn, attaining up to 32 Mg ha -1 

### with one harvest in 1989. Seve ral varieties of sorghum were tested with some attaining high yields on some sites even during the extreme drought year of 1988 (Table 5). Average yields across the 4 sites for sweet sorghum were 22.2, 19.1, 15.8 and 8.9 Mg ha -1



### , respectively for the years 1985, 1986, 1987, and 1988. The large decline in 1988 was due to very low yields at 2 of the 4 testing sites. But additionally Cherney et al. (16) 

### expressed concern that the decline in yields observed over the 4 year period was related to continuous sorghum culture as well as droughty conditions. Sorghum double cropped with rye was a very productive management option but required more inputs than switchgrass. Interseeding sorghum into perennial grasses was not a viable option due to its great dependence on envi ronmental variables. However, no-till culture of sorghums did appear to be viable. Sweet sorghum yield response to fertilizer varied with year (Appendix D) .

A separate analysis of the Purdue University screening results by Dobbins et al. (20) 

### considered the economic potential of the crops in Indiana. The analysis indicated that biomass feedstock production could be economically viable on marginal land in the Midwest and could compete favorably for land with traditional crops. Sorghum-sudangrass, sweet sorghum, reed canarygrass, and switchgrass were all identified as promising crops for Midwest pr oduction. Based on production costs alone, the most promising crops appeared to be switchgrass and sweet sorghum. The results of a whole farm analysis suggested that reed canarygrass, switchgrass, and sw eet sorghum were the alternatives that provided the best returns for the land, labor , and machinery resources available.

2.1.6 Iowa State University - Iowa

Anderson et al. (17) 

### reported in 1994 that in the first two y ears of field trials rainfall was either significantly (1988) or somewhat (1989) below normal early in the season. During the rest of the screening period through 1992 rainfall was either significantly above normal (1990) or relatively normal. At the Chariton (a marginal site), reed canarygrass totally failed to establish in 1988, big bluestem established very poorly, and switchgrass and al falfa had very low yields in the first year, though all perennials were re-established in 1989. Ho wever, several sorghum varieties and even corn did establish and produce acceptable yields at Chariton even in 1988. All crops successfully established at the Ames site. Yield results from both sites are summarized in Appendix E. The



### 11

### agronomic report from Iowa State University (17) 

### provided an excellent summary of the screening
Table 5. Yields of herbaceous biomass crops grown at four sites in Indiana during the drought year of

1988. a

Site T-Flat (excellent cropland) T-Slope (excellent cropland) SEPAC (marginal cropland) SIPAC (marginal cropland) Species ---------------------------------------------Mg ha -1

---------------------------------------

Alfalfa 17.36 13.28 9.98 1.62

Birdsfoot trefoil 8.03 6.31 5.88 5.25

Tall fescue 6.22 3.52 4.28 6.73

Reed canarygrass 5.99 4.10 5.12 6.27 Switchgrass 9.90 6.49 8.58 7.13 Rye 3.88 3.29 3.42 2.42 Sorghum x sudangrass 4.86 4.26 11.19 12.77

Sweet sorghum 2.20 1.70 12.77 21.03

a Yields averaged across fertilizer levels.



### results, but did not specifically make a recommendation for further energy crop research. Certainly the sweet sorghum and sorghum x sudangrass hybrids in a variety of cropping systems produced higher yields than any other annual or perennial species and maintained good yields under a variety

of climate conditions.

The economic report from Iowa State University showed that based on costs alone, the annual sorghums dominated the perennials grasses in both locations tested. (21) 

### However, the economic analysis (Table 6) showed that the highest yi elding perennial, switchgrass, competed well from an economic perspective with the sorghums, particul arly with the intercropped sorghums which come closer to meeting environmental criteria. These results are bolded and highlighted by italics in

Table 6.

The Iowa State University economic report summary states:

“ The results for intercropped sorghum are mixed and depend on whether sufficient acres are produced to allow optimum equipment use. With optimum equipment use, intercropped sorghums are cheaper than switchgrass in central Iowa, but not southern Iowa. Soil conservation considerations clearly favor the perennial grasses or the intercrops. ”

2.1.7 North Dakota State University – North Dakota

Meyer et al. (18) 

### reported in 1994 that the establishment year of 1988 experienced record drought at all test locations. All perennial crops had to be reseeded with cool season grasses reseeded in fall 1988 and warm season grasses reseeded the following spring and watered through summer to aid germination. Watering was necessary because 1989 al so received below normal rainfall conditions. By September reasonable to good stands of gr asses had been obtained but the legumes were not successful. Annuals successfully established even in 1988 but did not set grain in the driest site and produced low yields at most other sites. All sites but the most westerly one received above normal or

normal rainfall in 1990 and 1991 and 1992 was a near normal rainfall year for 4 of the 6 sites. (22)



### 12Table 6. Costs and break –even prices of the cro p production systems evaluated in Iowa 1988-1992 (from

Anderson et al. (21) with English units converted to metric).

Crop Systems Ames ($283 ha -1 land cost) 1 Chariton ($197 ha -1 land 1

cost)

Yield ASC 2 AC 3 Yield ASC 2 AC 3

Monocrops dry Mg

ha -1 (dollar/dry Mg -1 ) dry Mg

ha -1 (dollar/dry Mg -1 )

Alfalfa 9.86 41.05 69.81 7.77 52.78 Reed Canarygrass 7.46 51.68 89.67 10.60 36.94 55.54 Switchgrass 10.08 25.87 53.99 10.51 24.27 43.03 Big bluestem 8.60 33.13 66.08 7.95 35.33 60.12 Sweet sorghum 15.86 27.53 45.41 16.31 27.24 39.33 Sorghum x sudangrass 14.47 29.51 49.09 14.25 30.26 44.10 Double Crops Sweet sorghum/rye 15.72 36.52 54.54 13.89 41.99 56.18 Sorghum x sudangrass/Rye 14.52 38.98 58.51 13.87 41.80 56.02 Sweet sorghum 3 14.96 26.48 45.42 16.02 25.40 37.71 Sweet Sorghum/Rye 4 18.21 29.77 45.33 19.67 28.75 38.78 Intercrop Sweet sorghum/Alfalfa 13.89 31.48 51.89 9.61 45.03 65.55 Sorghum x sudangrass/Alfalf a 13.66 31.72 52.47 11.56 37.98 55.18 Sweet sorghum/Reed Canary grass 9.74 50.89 79.97

-- -- -- Sorghum x sudangrass/Reed canarygrass 9.88 49.98 78.67

-- -- -- Note: the four crops with lowest costs are highlighted for emphasis.

1 Estimated based on average Iowa equipment use.

2 ASC = average specified cost (total specified cost divided by yield) includes all costs excluding land costs. ASC does include fixed expenses such as interest payments on and depreciation of machinery and on capital investments.

3 AC = average cost (total costs divided by yield) include d the land cost and is the equivalent of break-even price.

4 Sweet sorghum and sweet sorghum rye double crop in rotation with corn and soybean.



### Perennial biomass yields averaged over all years and all fertilization levels was highest at Leonard, a “marginal” sandy site with wind erosion limitations. Prosper, the second site in the eastern Red River Valley area, produced the next highest perennial crop yields. The highest yielding biomass perennial crop at both sites was switchgrass (at 9 to 11 Mg ha -1 

### ). Intermediate wheatgrass, crested wheatgrass, a CRP mixture (consisting of wheatgrasses), and reed canarygrass followed close behind at about 7-9 dry Mg ha -1 

### . The warm season grasses did not establish well at the other sites to report yields, thus the most robust grass performance across all sites was demonstrated by the wheat grasses and CRP mixtures – though yields decreased to between 3-5 dry Mg ha -1 

### except where irrigated. All annual crop yields were highest at the irrigated site in the drift prairie region, with the very highest multiyear average yield obtained by forage sorghum (16.9 Mg ha -1 

### ). Sorghum x sudangrass had very similar yields to that of forage sorghum in most years. Both the forage sorghum and sorghum x sudangrass displayed yields higher than the perennials in a ll locations. An annual weed, Kochia, provided the most surprising results. While it did not succeed as a volunteering species, in annually seeded plots, the yield of Kochia had yields nearly as high as the sorghums on the better sites and performed much better than all other species at the poorest site. (18)



### Economic analysis, done on a whole-farm basis, was reported separately in a 1993 paper by Johnson

et al. (23) 

### Kochia was the first crop to be included on farm plans in all regions, due to its very low input cost. However, there are problems in the ma nagement of Kochia. For instance, it must be harvested prior to frost to prevent large biom ass losses and seed drop must be prevented to avoid infesting subsequent crops. If Kochia was exclude d, then forage sorghum and sorghum x sudangrass



### 13

### were the most profitable biomass crops. Switchgrass was more profitable than the common small grains grown in the Red River Valley area.

While the performance of switchgrass in the North Da kota screening trials was limited due to its poor establishment at most sites, where adequate stands were obtained, it did show potential. Thus, the final report recommended that further research s hould be done on switchgrass in the Northern Great

Plains.

2.1.8 Oak Ridge National Laboratory – Tennessee

An “old field” successional vegetation study conducted at ORNL during the same time frame as the herbaceous species screening studies and was affected by the same droughty conditions as many of the other studies. It provides a comparison not only with the species screening results, but also with recent studies in Minnesota on natural vegetation sites.

The sites studied by Johnston et al. (24) 

### were located on recently abandoned cropland and long abandoned pasture. Species diversity was high in both areas with the abandoned pasture having a higher percentage of grasses and lespedeza than th e abandoned cropland which had significantly more composites that are typical weeds in cropland. Levels of productivity (~3.0 to 8.0 Mg ha -1 

### ) indicated that successional vegetation harvested during the unusually dry conditions of 1986-1988 was generally as productive as perennial, monocultural ener gy crops established in the southeastern U.S. during the same years. The successional vegetati on was shown to be responsive to liming and fertilizers, although to a lesser extent than crops such as sweet sorghum and switchgrass. The fertilizer response was not sufficiently strong, however, to compensate for the added cost of the fertilizer applications. A preliminary economic assessment suggested that th e most cost-effective treatment was no fertilization for an overall cost of about $10/Mg ($1990). After 3 years of biomass removal, there were no signs of depletion of the pools for the major or minor plant nutrients in the treatments that received no lime or fertilizer at either site. However, it was assumed that over the long term some additional lime treatment and nut rient replacement would be required. Nitrogen removal rates at harvest ranged from ~40 to 60 kg ha -1 

### depending on harvest timing and yield levels.



### 14

### 3.0 HERBACEOUS CROP PROGRAM CONSIDERATIONS

3.1 HECP GOALS, ANALYSIS AND DATA SYNTHESIS

By late 1987 the goals and objectives of the HECP had been refined to clearly state a sensitivity to environmental concerns and to working with indus try. Cushman et al. clarified in the 1987 annual

progress report (25) 

### that the overall goal of the HECP was “to work with industry and university researchers to provide a technology base that will allow industry to develop commercially viable systems for producing herbaceous biomass for fuels a nd energy feedstocks”. The objectives of the HECP were expressed as follows:

1. Identify the biotic and physical resources ava ilable for the production of herbaceous energy

crops. 2. Identify and improve the productivity of the sp ecies most appropriate for herbaceous energy

crops 3. Define cost-effective management techniques for the production of herbaceous energy crops.

4. Establish the environmental acceptability and economic feasibility of herbaceous energy

crops.

Included in the report (25) 

### was an analysis of the problem of erosion on croplands. HECP research managers had noted that the best yields for li gnocellulosic crops were coming from annual grasses but there was substantial concern expressed about the am ount of erosion associated with annual crops. An analysis was conducted by ORNL staff to exam ine the erosion potential of cropland and potential cropland that might be used for energy cr ops. Based on data from the 1982 National Resources Inventory, (26) 

### it was noted that about 50% of the total cropland base had a low erodibility factor of < 10 (based on the Universal Soil Loss Equation (USLE)). Almost any crop can be planted on this land

and water caused erosion will remain less than the 5 tons/acre which was deemed an acceptable level by USDA’s Soil Conservation Service (SCS), but much of that land is susceptible to wind erosion. It was further found that while only 12% of the cr opland base had an erodibility factor of 50+, it

accounted for over 42.5% of water caused erosion on U.S. cropland with 70% of the losses associated with row crops. The USDA/SCS study (26) 

### stated that in the United States (in 1982), annual row crops had an averaged annual soil loss rate of 66 Mg ha -1 

### , while hay crops (perennial and annual) average only 5.5 Mg ha -1 

### ). This analysis indicated an important niche for perennial energy crops and was probably very influential in the final selection of a perennial grass as the single “model” species. Quoted from Cushman et al. (25) 

### is the following statement:

“Annual crops, especially energy crops that will leave little residue on the soil, are not appropriate for significant acreages of cropland. Perennial energy crops, especially grasses, are suitable for almost all cropland and potential cropland. They provide an opportunity to produce a crop on erosive land, yet achieve acceptable levels of soil protection.”

The environmental concerns associated with grow ing annual crops on the types of marginal land included in the herbaceous screening trial studies were verified by analysis conducted by several of the collaborators. Examples of calculated erosion loss results comparing sorghum with perennial crop production systems are shown below (Tables 7 and 8). In Virginia, all species including sorghums were planted using no-till establishment on slopes of 4.5 to 10%. The Virginia no-till management

resulted in much lower levels of estimated eros ion than was found for monoculture sorghums planted with conventional tillage on sloping sites in Chariton, Iowa. Of great interest, however, was the low amount of soil loss estimated when sorghum was inte rcropped with alfalfa or reed canary grass at the Chariton site (Table 8). ORNL had the responsibility of reviewing all of the herbaceous screening



### 15Table 7. Computed soil loss (mean of three sites) of eight no-till-plan ted species at four locations (three soils) in the Piedmont. Table reprodu ced from Virginia Tech final report. (11)

Species/Conditions Amelia South (Cecil) Amelia North (Cecil) Orange (Davidson) Lunenburg (Appling) Average of

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

----------------------------------------------------------- Sericea lespedeza 4.19 2.33 4.55 1.70 3.19 Weeping lovegrass 4.88 2.71 5.63 1.97 3.8 Flatpea 5.07 2.81 5.33 2.06 3.82

Tall fescue 5.27 2.93 5.16 2.15 3.88

Crownvetch 5.12 2.84 5.99 2.07 4.00 Switchgrass 5.87 3.26 6.71 2.39 4.56

Birdsfoot trefoil 7.61 4.22 7.91 3.09 5.70Sorghumsudangrass 13.98 7.75 14.36 5.67 10.44

Undisturbed land 3.99 2.21 4.02 1.62 2.96

Soil loss tolerance a 7 7 11 9 8.5

Soil formation rate b 1 1 1 1 1

a Soil loss tolerance levels were derived fo r soils in the U.S. by soil scientists, agronomists, geologists, soil conservationist s, and federal and state researchers in 1961 and 1962 (see report for references).

b Soil formation rate for environmental sust ainability (see report for references).

Table 8. Estimated soil loss under several crop syst ems in Iowa. Table repro duced from Iowa State University final report. (17)

Cropping system and crop

Monocrop Double crop Rotation Intercrop

_______________________________________ ____________ ________________________ ___________ Year ALF RCG SWG BBS SS SSH SS/R SSH/R Corn SB SS/R SS ALF RCG
---------------------------------------------------Mg ha -1

--------------------------------------------------- ------ Ames

1988 3.79 3.79 3.92 3.92 4.89 4.89 3.06 3.06 4.41 3.92 3.06 4.89 3.79 3.79

1989 0.25 0.04 0.04 0.04 4.89 4.89 3.06 3.06 4.41 4.88 3.06 4.89 0.25 0.04

1990 0.25 0.04 0.04 0.04 4.89 4.89 3.06 3.06 4.41 4.88 3.06 4.89 0.25 0.04

1991 0.25 0.04 0.04 0.04 4.89 4.89 3.06 3.06 4.41 4.88 3.06 4.89 0.25 0.04

1992 0.25 0.04 0.04 0.04 4.89 4.89 3.06 3.06 4.41 4.88 3.06 4.89 0.25 0.04

Chariton

1988 1.90 1.94 1.85 1.99 13.89 13.13 22.27 22.27 13.89 14.53 22.02 11.46 2.02 1.96

1989 0.58 0.39 0.40 0.47 25.65 24.21 22.27 22.27 25.38 26.71 23.27 37.25 1.68 0.41

1990 0.58 0.31 0.33 0.36 35.62 33.62 22.27 22.27 33.52 35.26 22.27 35.62 1.68 0.41

1991 0.58 0.31 0.33 0.36 35.62 33.62 22.27 22.27 32.05 37.25 22.04 35.26 2.02 0.41

1992 0.58 0.31 0.33 0.36 35.62 33.62 22.27 22.27 31.73 35.62 23.27 37.25 2.02 0.41

Note: ALF = alfalfa, RCG = reed canarygrass, SWG = switchgr ass, BBS = big bluestem, SS = sweet sorghum, SSH = sorghum x sudangrass, SS/R = sweet sorghum doublecropped with winter rye, SSH/R = sorghum x sudangrass doublecropped with winter rye, Corn = corn in a corn-soybean -sorghum three year rotation, and Rotation = average factor for plots in the corn-soybean-sorghum rotation.



### 16

### studies and determining the patterns observed both w ithin and between projects. Table 9 shows the crops recommended for further study and/or development by each project.

Table 9. Species recommended for further developm ent or study by the seven herbaceous screening projects

Institution Recommended crops Virginia Tech Switchgrass, weeping lovegrass

Auburn University Switchgrass, sericea lespedeza, and energy cane

Purdue University Switchgrass, reed canar ygrass, sweet sorghum and sorghum-sudangrass

Iowa State University Switchgrass and intercropped sorghums

North Dakota State University Switchgrass, forage sorghum and sorghum x sudangrass

Cornell Switchgrass, alfalfa/bromegrass mixt ure, and timothy/redtop/red clover for the well drained soils; Reed canary grass for the poorly drained soils.

Geophyta Forage sorghum, intercropped sor ghum x sudangrass, and reed canarygrass a

a Switchgrass was the 4 th best performer in terms of yields but was proba bly not identified by Geophyta for further work due to establishment and weed competition probl ems. Even so, over 4 years, switchgrass yi elds continued to increase and nearly equaled that of reed canarygrass in the 4 th year. During the same period sorghum yields dropped dramatically. Note: Switchgrass is listed first in the list of recommended crops, not because it was always considered to be the highest potential crop, but to emphasize that 6 of the 7 projects included it in their recommendations.



### While switchgrass was recommended by six of the sev en projects, and performed reasonably well in the seventh project, it certainly was not always at the top of the recommendation list. Most of the projects that also recommended the sorghums tended to see them as being the more likely choice by farmers in their region. Turhollow et al. (27) 

### reported in the HECP Annual Progress Report for 1988 that the major observation across all screening projects was the superiority of both the sorghums and switchgrass under drought conditions. Switchgrass produced higher yields than sorghums in Virginia but both survived with no-till management in the poor Virginia soils. In Indiana, where late growing season rains did come in, sorghum produced as much as 32 Mg ha -1 

### at one site but, from an economic perspective, switchgrass was judged to have higher potential returns. In northern Ohio, the sorghums produced higher yields than the perennial grasses but yield declines over time were a concern. Sorghums performed well, while warm season perennials performed poorly when established in 1988 during drought conditions in North Dakota and Iowa. From an economic perspective, both sorghums and switchgrass generally stood out as having higher potential than other crop choices. The conclusions of the report (27) 

### indicate the opinion that sorghum may have potential for meeting economic requirements in the Midwest, but not the southeast. The only other crop thatwas recommended by more than one project was reed canarygrass. Energy cane and other subtropical grasses produced some very high yields that suggested further work might be merited in the

south.

The ORNL graphic (Fig. 2), drawn in 1991, showing both the woody and herbaceous crops considered to be high potential included switchgrass, reed canarygrass, sorghum, and tropical grasses as the herbaceous crops of choice. The fact that ORNL scientists/research managers in the early 1990s still considered sorghum to be a high potentia l energy crop for some areas is evidenced by quotes from a 1991 paper presented by Cushman and Turhollow: (5)



### 17

### “ We now feel that sorghums will have an important role as energy crops on good sites, perhaps in rotation with conventional food cr ops where year-to-year flexibility in planting will be an advantage. However, their use on many lower quality sites will be limited by low production and environmental concerns.”

Figure 2. Woody and herbaceous species considered by the Department of Ener gy's Biofuels Feedstock Development Program as having high potential as energy crop feedstocks in 1991. The striped area had not completed herbaceous screening studies.



### Given that ORNL was still identifying several species as having high potential for bioenergy in 1991, the question arises as to what really forced the choice to focus on a single model species. While switchgrass did stand out as an environmentally and economically sound choice for many parts of the country, it was not a clear winner in all locations. It is the opinion of this author that a combination of the original criteria established by the BFDP, the screening results, and funding limitations imposed by the Department of Energy resulted in selection of only a single herbaceous crop species for further development



### .

3.2 BFDP FUNDING EFFECTS ON MODEL SPECIES SELECTION

Funding variations in the program at ORNL in the early 1980s and 1990s (Fig. 3) had to affect

research decisions in some manner. Substantia l funding was received by ORNL to launch the new Herbaceous Energy Crops research effort in 1984. At the outset of the herbaceous program the expectation had been that at least 3 or 4 different types of herbaceous crops would be carried forward to further development after the screening phase. Funding remained relatively steady for 3 years but dropped substantially due to changes in government priorities before the planned end of the herbaceous crop screening phase. The funding drop coincided with the development of plans for



### 18

### further herbaceous and woody crop development. At this critical juncture, the decision was made jointly with DOE to restrict further crop development funding to very few “model” species. By focusing on only one herbaceous crop and one woody crop – it was believed there would be a greater chance for proving the value of genetics and bi otechnology in increasing yields and improving

economics.

0.00 1.00 2.00 3.00 4.00 5.00 6.00DOE funding, $ Million

1978 1980 1982 1984 1986 1988 1990 1992 1994 1996 1998

Year Feedstock Program Funding Distribution

PLN & ASSIST

RES OTHER

HEC SUBS

SRWC SUBS

Figure 3. Funding history of the biofuels F eedstock Development Program between 1978 and 1998.



### While the value of focusing was proven over the next several years, it is interesting to note that as feedstock funding at ORNL rebounded, crop deve lopment funding for both woody and herbaceous crop model species remained level while feedstock research expanded into new areas. In the early 1990s the woody and herbaceous cr op development activities at ORNL were combined under the Biofuels Feedstock Development Program (BFDP) . This joint program was proposed and accepted by DOE as a mission-oriented, national program of research and analysis whose goal was to develop and demonstrate environmentally acceptable cr ops and cropping systems for producing large quantities of low-cost, high quality biomass feedstocks. Thus, the goals of the BFDP went far beyond just developing crops to encompassing systems integration issues, optimizing economics, and considering feedstock quality, carbon sequestration issues, and biotechnology potential. Addressing these issues required close coordination with mana gers and researchers in DOE’s Biofuels and Biopower Programs – responsible for developing technologies to convert biomass feedstocks to energy. Coordination needs also required more investment in outreach and communication and in analytical support to DOE. Thus, when funding increases occurred in the mid-1990s – it was allocated to new research topics, analysis, and outreach, rather than to expanding the number of species being developed.



### 19

### 4. HIGH POTENTIAL FEEDSTOCKS

4.1 

### HERBACEOUS CROPS CONSIDERED HIGH POTENTIAL IN 2006

Research conducted specifically to improve switchgrass as a model biomass energy crop during the 1990s has been very successful in improving its potential as a dedicated biomass energy crop. McLaughlin and Kszos published in 2005 an excellent summary of the results gained by the focus on switchgrass. (3) 

### The research developments and the con tinued national level interest in biofuels development in the U.S. have been successful in attracting industry interest in further developing switchgrass. For instance, the private biotechnology firms, CERES and Mendal Biotechnology are both seriously working on the improvement of switchgrass for bioenergy.

New research conducted over the past 6 years at the University of Illinois has brought a lot of attention in the U.S. to a new crop that was iden tified as having high potential in Europe in the mid

1990s. (28) 

### Varieties of this crop, Miscanthus, have been grown for many years in the U.S. as a landscape plant, but it was never proposed for ev aluation in any of the bioenergy crop screening studies. Because of the very high yields that have been obtained in Europe and which are now being replicated in Illinois with a single sterile hy brid cultivar, Miscanthus x giganteus (or giant Miscanthus), a legitimate question is being asked wh ether it should also be a “model” bioenergy crop and how it compares with switchgrass. Side by side studies in Illinois have certainly demonstrated a considerably higher yield potential for giant Miscanthus at the location tested. (29) 

### However, there is not yet published information discussing the economics and operational issues associated with establishing giant Miscanthus on a commercial scale – so a full comparison with switchgrass is

difficult.

Sorghum continues to attract a lot of interest. Two presentations at the 2007 World BioCongress meetings held in Orlando, Florida, focused on the importance of sorghum as a cellulosic feedstock. The Kansas State University - StrathKirn Sorghum Project, currently focusing on bioconversion research, sees sorghum as the next most important crop (after corn) for ethanol. (30) 

### Geoffrey Thomas of SorBio Energy Systems made a presentation at the conference providing convincing information on why sorghum should be receiving more attention. (31) 

### Some of his arguments were the following:

1. Sorghums could be a starter crop that would fill the gaps in cellulosic feedstock production while perennial crops are becoming fully established. 2. Sorghums can be intercropped with winter cereals for multi-season cellulosic supplies. 3. Sorghums are adaptive to a wide range of so ils conditions with several different varieties available to meet site specific requirements. 4. Low lignin hybrids are available in all key types of sorghum 5. Sorghum has a well known, fairly simple genome 6. The sorghum seed industry is well establishe d and there is a large base of experienced producers 7. Sorghums have a large root system, are efficient water and nutrient users, and are simple and cost-effective to grow. 8. Forage sorghum dry land yields in Texas range from 7 to 22 dry Mg ha -1 

### , sweet sorghum yields are up to ~17 dry Mg ha -1 

### and sorghum-sudangrass yields up to 14 dry Mg ha -1 

### (with 3 cuttings). 9. Opportunities are available for further reducti on in lignin levels and enhanced sugar yields through genetic improvement.

There are also downsides associated with sorghum harvest, handling, and storage that were not



### 20

### mentioned by Dr. Thomas but further considera tion of sorghum appears to be merited.

In 2006, a paper published in Science by Tillman et al. (32) 

### brought a lot of attention to “mixed grassland biomass” as an environmentally preferable, low-cost alternative resource for bioenergy in comparison to all monoculture crops. The paper focused on the energy input/output comparisons between growing corn grain for ethanol, soybeans for biodiesel, and grassland crops for biomass electric, biomass ethanol or biomass synfuels. The grassland crop based systems were shown to have significantly higher net energy balances (NEB) than e ither the corn grain to ethanol or soybeans to biodiesel. Yields of the grassland crops used in the NEB analysis (found in the published backup material) averaged 3.6 Mg ha -1 

### yr -1 

### for the high diversity grassland plots on degraded soils and 6.0 Mg ha -1 

### yr -1 

### on fertile prairie soils, both in Minnesota. These yields were estimated from multiple replicates of very small samples that were harvested in early August of each year. If harvested in late September, yields would have likely been higher. An earlier publication (33) 

### had shown the positive relationship between increasing diversity and increasing yields with the mean yields of the highest diversity plots generally exceeding the highest yielding monoculture plots. However, the switchgrass monoculture plots had not established successfully and were not included in the 2001 comparison.

Some of the BFDP screening studies also noted th e possible potential of mixed species plots (some were simply weeds, (14,18) 

### one was meadow grasses and legumes, (15) 

### and one was old field successional vegetation). (24) 

### Yields were generally in the range of 3 to 8 Mg ha -1 

### . The results in

North Dakota (18) 

### suggested that a low-input weed crop (Kochia) could be more profitable than conventional crops. Also, the old field successional ve getation study suggested the possibility of lowinput systems being profitable. (24) 

### The primary drawback to the low-input “meadow” biomass resource is that very large amounts of land would be required to produce the large supplies that will be needed for the large ethanol production facility sizes that are considered to be most cost-effective.

There are many other herbaceous crops that are still of interest to biomass energy crop developers. A DOE sponsored workshop held in 2006 (34) 

### provided a group of crop experts from the southeast an opportunity to discuss the advantages and issues associated with potential biomass energy crop candidates. Crops that made the list included sev eral annuals and perenni als. Annuals included sorghum-sudangrass, sweet sorghum, johnsongrass, pearl millet, and industrial hemp. Perennials included giant reed, energy cane, switchgrass, giant Miscanthus, bermudagrass, napiergrass, bahiagrass, tall fescue, and sericea lespedeza. It woul d be of interest to evaluate all of the proposed bioenergy crops against a set of common criteria. Suggested criteria are described below.

4.2 BIOFUELS FEEDSTOCK SELECTION CRITERIA

Some important criteria for bioenergy feedstocks were recognized and established early in the screening process. Other criteria or valuable charact eristics of bioenergy feedstocks were identified later as researchers and project developers began to seriously consider the factors necessary for putting together cost-effective feedstock supply systems. In order to maintain a historical perspective on which criteria lead to the selection of switchgrass as high potential “model” species, the criteria have been grouped by the decade in which ther e importance was more clearly recognized.

4.2.1 1980s Selection criteria

In the early 80s, U.S. agricultural exports were at record levels and in 1984 the world became aware

of famine in sub-Saharan Africa. Thus at the initiation of the trials in 1984 there was much more concern about possible conflicts between the producti on of food and fuel than existed at the end of



### 21

### the trials. (5) 

### Accordingly, the “capability of energy crops to perform on marginal cropland” was the broad objective at the time the herbaceous crop solicitation was issued. Crops which can meet that broad objective, however, have several characteristics that can be used as selection criteria. There is not a specific criteria related to conversion technology in this list. In the early 1980s, the conversion technologies were presumed to have equal chance of being either biochemical or thermochemical so

no criteria were established that would favor one type system over another. The only conversion related exclusions in the herbaceous crop screening solicitation (7) 

### were those that eliminated crops whose primary value lie in the production of specific chemical components, resins, latexes, oils, and hydrocarbons, or root, grain, or seed crops. Thus , corn grown primarily for production of grain to ethanol and beets grown for their sugar were not considered for further research by the Herbaceous Energy Crops Program.

4.2.1.1 Profitability on marginal land

The 1984 RFP (7) 

### clarified that the objective of the research being initiated was to result in crop systems that were driven by “cost-effective production, not maximizing productivity per acre”, recognizing that the crops producing the highest yields might not be the most profitable.

4.2.1.2 Adaptability

The trait of adaptability is not only associated with a capability to perform on marginal land, but is a necessary criteria for meeting the Herbaceous Energy Crop Program goal of identifying crops that would have the greatest possible impact on total biomass energy use. This was understood at the time to mean the selection of crops that were highly adap table to production in many U.S. regions. Traits that contribute to adaptability include efficient nutri ent use, efficient water use, tolerance of wet and dry soils, and freeze tolerance.

4.2.1.4 Minimal soil loss

Cropping systems that would minimize erosion were high on the list of desirable traits for an energy crop production system. The 1982 National Res ources Inventory conducted by the USDA’s Soil

Conservation Service had determined that in the southeast and Midwest/Lake states, erosion was the most important restriction on cropland use and wetness was the second most important. (26)



### 4.2.1.3 High yield potential and yield reliability

While profitability, rather than high yields, was th e ultimate goal, the identification of crops (and specific varieties within crops) with the best gene tic potential for high yields and yield reliability was (and still is) important. High yield results from small fi eld trials have to be evaluated in the context of nutrient and water inputs and variability of the crop yield under several years of variable climate conditions. Crops with the lowest input require ments and most stable yields are preferred.

4.2.2 1990s selection criteria

By 1988, crop surpluses and the high costs of federal agricultural programs were emerging as national issues so “food versus fuel” concerns were greatly diminished. Also, late in the 1980s a serious attempt was made to begin linking energy crop production selection criteria to specific conversion technologies. (35)



### 22

### 4.2.2.1 Profitability on productive land

As research transitioned from screening trials to crop development trials, more research was performed on relatively better cropl and and economic analysis using the resulting yields suggested that some crops had more potential than others to compete with conventional crops on cropland currently in production.

4.2.2.2 Feedstock composition

The importance of feedstock composition in affecting the success and cost of conversion technologies took on greater significance in the late 1980s and early 1990s. (5) 

### A literature review and survey published in 1988 (36) 

### concluded that all conversion processes are affected by feedstock characteristics. The effects of composition on biochemical and ther mochemical conversion were, for the most part, predictable – such as the problems caused by high ash contents, the value of high cellulose content for ethanol production, and the value of lignin for pr ocesses where higher btu levels are important. In about 1990, high nitrogen content was found by th e Solar Energy Research Institution (now the National Renewable Energy Laboratory) to create problems for the simultaneous scarification and fermentation (SSF) approach to making ethanol. High nitrogen contributes to undesirable nitrogen compounds in the gases produced by thermochemi cal processes. ORNL funded composition studies showed that legumes had protein concentrations 2 to 4 times that of grass crops. Thus, the cost reductions that might be gained by the reduced fertilizer requirements of leguminous crops had to be weighed against the possible increased costs involved in producing clean fuels. (5) 

### This information led to basically dropping legumes from serious consideration by the ORNL/BFDP team.

4.2.2.3 Reliable stand establishment

The screening studies had shown the difficulty of establishing switchgrass during times of rainfall deficit. Several of the switchgrass crop developm ent projects, focused on identifying causes for the problems and succeeded in developing more reliable methods. Reliability in stand establishment is a function both of crop characteristics and experience of the crop producer.

4.2.2.4 Reliable low-cost propagation

The ability to easily replicate the desired genetic traits using low-cost propagation techniques is important to the ability to reliably produce crops with the desired yield and composition traits. It is also important for facilitating rapid scale-up of the energy crop.

4.2.2.5 Soil carbon sequestration

The potential for herbaceous crops to affect soil carbon sequestration (either positively or negatively) also began to be a large issue in the early 1990s. More attention was given to looking at root systems and to collecting soil carbon da 

### ta

4.2.3 2000s selection criteria

By the early 2000s, the Biofuels Feedstock Progr am had already begun scaling up cultural methods developed in small research trials to larger scale/ pre-commercial trials. Thus, the research community became more aware of crop scale-up and environmental issues, and the opportunity was created for testing a variety of harvesting, handling, storage, and transportation systems as well as collection of

data on environmental effects.



### 23

### 4.2.3.1 Rapid scale-up potential

As the idea of using perennial crop based bioe nergy has moved from a concept to a recognized component of national energy plans, concerns have increased regarding the time it will take to produce sufficient seeds, rhizomes, cuttings, or seedlings to actually get a single large project established, much less, millions of acres of these new crops.

4.2.3.2 Chemical inputs minimal

With greater interest in bioenergy crops more ques tions are being asked about the possible impacts of the crops on the environment. Crops that can perform well with minimal chemical inputs clearly will have more support from environmental groups.

4.2.3.3 Low pest and disease risk

Crop that have few pest and disease problems will have greater potential for yield stability, higher yield potential, and consequently lower costs of production. This is often one of the attractive features of exotic species assuming that they do not have invasive characteristics.

4.2.3.4 Invasive potential is low

Increasing attention is being paid to the invasive ch aracteristics of potential energy crops with several states excluding crops from consideration that have a high potential for becoming an invasive weed. Sometimes, exotic and invasive species are lumped together as though they are the same. In many cases, this is true, but not in all cases. Any potential exotic species should be evaluated to determine whether it has invasive characteristics before being wi dely planted in the U.S. and should be rejected if that potential exists. However, serious consid eration should also be given to the potential yield advantages of exotics that are sterile, for example giant Miscanthus.

4.2.3.5 Sterility

Sterility is desirable, possibly even a requirement, fo r exotic species. Some investigators have also expressed a concern about the genetic contamin ation of wild populations of switchgrass from widespread planting of improved varieties. (37, 38)



### 4.2.3.6 Operational requirements

There are a number of criteria associated with harv est, handling, and storage that can potentially be used in evaluating different species. Some identif ied in the table below include multiple harvest options, broad harvest window, and minimal storag e needed. These are not as “fixed” as are basic plant characteristics but some crop types facilitate mo re options than other types and consequently the possibility of greater supply reliability at lower cost. (39)



### 4.2.3.7 Net energy at feedstock harvest and at point of delivery

A major point of controversy in recent years has been the amount of energy available in the final product versus the energy required to grow, harvest, transport, and convert the crop to its end use. Net energy available both in the harvested feedstock and in the delivered feedstock could be used to evaluate the relative desirability of different feedstock supply systems.



### 24

### 4.2.3.8 Alternate uses

Any energy crop will be more attractive to farmer s if it has the potential of feeding into several possible markets. This will reduce the risk to th e farmer in case a specific energy facility fails.



### 25

### 5. CHARACTERISTICS OF THE SWITCHGRASS “MODEL”

The success that has been achieved in bringing atte ntion to the potential of switchgrass as a feedstock for cellulosic ethanol has lead some to equate the term “model species” to mean “best species”. When other crops have been found to produce higher yi elds in a given location, the first response is often to question the “model species” status given to switchgrass and to begin marketing the new crop

as a “better” alternative. A more useful res ponse would be to consider switchgrass as a “prototype” species that has been deemed cap able of meeting many (though not necessarily all) of the criteria desired of a bioenergy crop.

Switchgrass is a good “prototype” for grass crop genetic improvement research due to its large genetic variability and the fact that recent resear ch has elucidated much about the reproductive characteristics of the species. (40, 41, 42) 

### Switchgrass is a good prototype for harvest, handling, storage, and transport research because it can be grown unde r a wide rage of climate conditions and is amenable to being handled and stored both as a wet or dry feedstock. (39) 

### By focusing the energies of many different researchers on a selected prototype energy species, and facilitating the rapid exchange of information, it is possible to more quickly and fully develop an understanding of the issues involved in developing cost-effective, fully integrat ed crop supply systems for multiple regions of the

U.S.

Table 10 attempts to (1) describe the current char acteristics deemed desirable for bioenergy systems (and why they are desirable), (2) describe how well the switchgrass species and the assumed cropping systems meet those desired characteristics, and (3 ) provide references for further information.

Table 10. Feedstock criteri a, criteria relevance categories, and rank ing (high, medium and low) of the capability of switchgrass to m eet those criteria for cellulosic ethanol production systems.

Criteria Relevance categories Rank Notes and References

Cost- effective production Producer profitability H Screening trials found switchgrass to be more profitable than alternative conventional crops and most grasses on marginal cropland in several parts of

the U.S. (13, 21, 23) Later analysis has demonstrated that profitability depends greatly not only on switchgrass technology (inputs, yields, storage, transport) but also on farm, environmental and energy policies and energy costs, all of which can affect land prices and fertilizer and transport costs. Broad adaptability Producer profitability, Supply reliability H The wide adaptability range of switchgrass was demonstrated by the screening trials described in this paper and by summary papers. (3,4) pH ranges from

4.9 to 7.6 are tolerated. (41)

Tolerant of wet and dry soils Producer profitability, Supply reliability (subcomponent of broad adaptability) M Lowland varieties are naturally found in floodplains and upland varieties are found in more well drained

areas. (43) Screening studies found survival and growth in both wet and dry areas. (12, 13, 14, 15, 16, 17, 18)

Freeze tolerant Producer profitability, Supply reliability (subcomponent of broad adaptability) H Switchgrass has a range well into Canada and into Mexico, thus some varieties are more freeze tolerant

than others. (43)



### 26Efficient nutrient

use Producer profitability,

Environmental benefit (needs little fertilizer) M Fertilizer inputs in the range of 40 to 120 kg N ha -1
per year appear to be the most cost-effective levels depending on region of the country and rainfall

levels. (3, 43, 44, 45, 46, 47, 48) Nutrient loss is greater with 2 or more cuts per year; best nutrient use efficiency is 1 cut per year after senescence. (49, 50)

Efficient water use Producer profitability,

Environmental benefit (needs little or no irrigation) H The case for low water requirement derives primarily from the observation that switchgrass remains green when other forages turn brown from drought stress. Roots are deeper than many grasses. Recent studies on transpiration show differences among varieties. (11,

51, 48) Precipitation levels may be critical to

successful establishment (3) but yields are not strongly affected by precipitation after fully established. (3)
High yield potential Producer profitability,

Environmental benefit (efficient land use) H-M High yields in the 20 to 30 dry Mg ha -1 range have been demonstrated in a few locations, average yields following switchgrass selection and development tend to be in the range of 10-20 dry Mg ha -1

. (3)
Breeding studies have indicated a potential to improve yields at a rate of 5% or greater per breeding cycle. (40)

Alternate uses Producer profitability H A fa rmer’s co-op in Iowa is developing several markets for switchgrass including forages, mulch for landscaping, fiberboard and paper, plastics filler, stove pellets, fireplace logs, and animal bedding. (60)
Yield reliability Supply reliability H Yield reliability in many soil and climate conditions is higher than most annuals and better than many perennials based on screening trial results (12, 13, 14, 15,

16, 17, 18)

Pests and disease problems are

minimal Supply reliability,

Producer profitability,

Environmental benefit (low chemical use) H Pest and disease incidence has been very low thus far but some pests and diseases have been identified. (57)
Research in Virginia has shown an advantage to using a granular systemic insecticide in rows at time of planting reducing need for any further insecticide

use. (53)
Easily/reliable propagation Supply reliability, Producer profitability M Seed production is easy but controlled crossing is required. High demand for improved varieties is already increasing seed costs. Micro propagation of genotypes is possible but costly. (56)

Quick/reliable

stand

establishment Supply reliability, Producer profitability M to

L Many of the screening trials reported very slow establishment rates (3~4 years) while some later studies achieved full yield by the 2 nd year. Seeding failures may occur if seed dormancy is not broken (47,

48, 53, 54) , or if rainfall is not sufficiently frequent. (55)

Soil carbon sequestration rate potential is high Environmental benefit (soil improvement, low GHG emissions) H The deep rooting system of switchgrass allows crop to initially sequester carbon at a high rate (1 to 1.6 Mg C ha- 1 ) if production site is carbon depleted. (3, 12,

58, 59)

Soil loss is

minimal Environmental benefit (sustainable productivity) H Most perennials result in lower soil loss than annual crops even when planted into conventionally tilled soils, but no till establishment results in the least soil

loss. (12,17)



### 27Chemical inputs

minimal Environmental benefit (low GHG emissions), Producer profitability M Herbicides are generally required in first year for successful establishment, but rarely thereafter; mowing above the new seedlings is sometimes sufficient; there has been little need for pesticides. (46,

47, 53)
Chemical inputs

minimal Addresses an important

environmental

criteria H Herbicides are generally required in first year for successful establishment, but rarely thereafter; mowing above the new seedlings is sometimes sufficient; there has been little need for

insecticides. (46, 47, 53)
Energy input to

energy crop production is low Environmental benefit (low GHG emissions), Producer profitability H Energy input requirements are between 3 and 4% of the HHV of the pre-harvest production at yields ranging from 10 to 30 dry Mg ha -1 and optimized

fertilization levels. (39)
Energy input of

delivered

feedstock is low Environmental benefit (low GHG emissions), Producer profitability H Total energy input requirements for crop production, harvest and storage, and transport with both current and mature technologies are estimated to be 8.5% or below at current yields (10 Mg ha -1 ), reducing to 6.5% at 30 Mg ha -1 with mature technology. (39)
Invasive potential

is low Environmental benefit (low risk) H Switchgrass is a native species that is persistent once established, but not overly aggressive in spreading to

new areas. (43)

Sterility is natural

or can be created Environmental benefit (low risk) M-L Switchgrass is an out crossing species, thus large populations of naturally selected “improved” varieties planted near remnant native populations, might result in changing some traits in the native populations; this area needs more research to determine risk levels, distance of effects, and potential for creating sterile varieties. Rapid commercial scale-up possible Supply logistics (enabler of near-term commercial success) M Scaling up of stands of select varieties to propagate enough seed for several large projects simultaneously would be a problem, probably taking 3-5 years at a minimum. However, farmers are interested if markets emerge. (60)
Multiple harvest options Supply logistics (allows greater adaptability of the production system) H The thin stemmed switchgrass at current yield levels is amenable to conventional mowing and conditioning, and can be field chopped and ensiled, or swathed and baled in either round bales, small or large square bales or “loafs” for dry storage or further handling (e.g. pelletizing). Higher yield levels will likely require modifications to equipment and/or development of more innovative designs. (39)

Harvest window is

broad Supply logistics (increases probability that majority of crop can be harvested) M While switchgrass can theoretically be harvested 2 or more times during the growing season, in fall and even in the following spring – the most sustainable system for most regions is one harvest per year in fall after senescence. Spring harvests risk a 30 to 40% yield reduction compared to fall harvest. (58, 61)
Storage time is

minimal Supply logistics (reduces cost, minimizes loss, reduces changes in composition) L The downside of one harvest per year is that the biomass must be stored for longer periods. Development of storage methods that minimize losses are a major research effort. (39)

Composition Conversion M Optimal composition for ethanol made with the SSF



### 28(must be specified based on planned

conversion process) efficiency (final product cost) process includes high cellulose, low ash, low nitrogen and just enough lignin to reduce facility power costs. Other biofuel processes may prefer more nitrogen (proteins) or more lignin to produce a greater variety of co-products. Switchgrass has higher cellulose levels and lower ash levels compared to many other herbaceous crops

screened (13,18) , but higher ash and nitrogen levels than fast growing trees.



### 29

### 30 6. CONCLUSION

The screening trials funded by the U.S. Departme nt of Energy in the late 1980s to early 1990s assessed a wide range of about 34 species with trials being conducted on a wide range of soil types in 31 different sites spread over seven states in crop producing regions of the U.S. Several species were identified as having merit for further development. Six of the seven institutions included switchgrass among the species recommended as having high potential in their region and/or deserving of further study. Most projects had some to serious problems with switchgrass establishment during drought years, but later crop development research iden tified methods to improve establishment success under most conditions. The two southeast projects, in Virginia and Alabama, had the most success with switchgrass and produced some of the most persuasi ve information showing the merits of switchgrass – especially the potential for high yields, its deep rooting characteristics, and its potential value in carbon sequestration. All of the Midwest projects (in Indiana, Iowa, and North Dakota) came to the conclusion that switchgrass merited further cons ideration primarily after conducting economic analysis, since visual results of crop yields most often led toward favoring sorghum systems. In some cases, additional characteristics such as more favorab le conversion characteristics or lower erosion potential increased the interest in switchgrass. Economic and environmental assessments by Oak Ridge National Laboratory’s Biofuels Feedstock Development Program staff together with the screening project results, and funding limitations lead to making the decision to further develop only switchgrass as a “model” or “prototype” species in 1991.

Selection of switchgrass as a model species in 1991 lead to a switchgrass specific solicitation and then to 10 years of switchgrass development at ten institutions under the management of Sandy McLaughlin and others at ORNL. (3) 

### More recently switchgrass has been the focus of investigations at several additional universities and private institutions. New varieties have been developed and released, management techniques have been impr oved, and much more is now known about how switchgrass can be harvested, handled, stored and c onverted to ethanol or used to produce power. Now, in 2007, it is very apparent that while sw itchgrass may not be a perfect energy crop (and there may not be a perfect crop), it has many valuable char acteristics that will result in its continuing to be not only a “model or prototype” for crop development, but also one of the more sustainable feedstocks for the production of renewable alternative fuels in the U.S.

There are many herbaceous crops that are still of in terest to biomass energy crop developers. A DOE sponsored workshop held in 2006 (34) 

### provided a group of crop experts from the southeast an opportunity to discuss the advantages and issues associated with potential biomass energy crop candidates. Crops that made the list included sev eral annuals and perenni als. Annuals included sorghum-sudan grass, sweet sorghum, johnsongrass, pear l millet, and industrial hemp. Perennials included giant reed, energy cane, switchgrass, giant Miscanthus, bermudagrass, napiergrass, bahiagrass, tall fescue, and sericea lespedeza. Re gional and local considerations may well favor use of an herbaceous energy crop other than switchgrass. It is important, however, that any crop used for bioenergy be capable of being produced in a way th at is not only economically sustainable but that also meets high standards of environmental sustainability.

### 31 7. REFERENCES

1. L.L. Wright, J.H. Cushman, A.R. Ehrenshaft, S.B. McLaughlin, S.A. Martin, W.A. McNabb, J.W. Ranney, G.A. Tuskan, A.F. Turhollow, Biofuels Feedstock Development Program Annual Progress Report for 1992 . ORNL-6781. Oak Ridge National Laboratory, Oak Ridge, TN 37831,1993. 2. S.E. Sladen, D.I. Bransby, and G.E. Aiken, Biomass, Yields, Composition, and Production Costs for Eight Switchgrass Varieties in Alabama, Biomass and Bioenergy Vol 1(2): 119-122, 1991. 3. S.B. McLaughlin, and L.A. Kszos. Development of switchgrass (Panicum virgatum) as a bioenergy feedstock in the United States. Biomass and Bioenergy 28 (2005):515-535, 2005. 4. S.B. McLaughlin, New Switchgrass Biofuels Research Program for the Southeast, pp.111-115, In: Proceedings of the Annual Automotive Technol ogy Development Contractors’ Coordination Meeting. SAE International, Warrendale Pennsylvania, 1992. 5. J. H. Cushman and A.F. Turhollow, “Selecting Herbaceou Energy Crops for the Southeast and

Midwest/Lake States” pp. 465-480 In: Energy from Biomass and Wastes XIV, D.L. Klass (ed), Institute of Gas Technology, Chicago, Illinois, 1991.

6. SERI. The Production of Herbaceous Feedstocks for Renewable Energy . SERI/SP-273-2302, DE85012136 Solar Energy Research Institute, Golden, Colorado 80401-3393, 1986. 7. Oak Ridge National Laboratory (ORNL). Request for Proposal No. 19-6233 Entitled “Selection of Herbaceous Species for Energy Crops” . Released by Oak Ridge National Laboratory’s Bioenergy Feedstock Development program approximately March 1984 with proposals due July 17, 1984.

8. OTA. Energy from biological processes . Congress of the United States Office of Technology Assessment. U.S. Government printing Office 0-65-498. Washington, D.C., 1980. 9. J.B. Berger, and J.H. Cushman, Herbaceous Energy Crops – Planning for a renewed Commitment

, Environmental Sciences Division Publication No . 2385. Oak Ridge National Laboratory Biomass/ Feedstock Development Program, Oak Ridge, TN, 1984. 10. J.H. Cushman, A.F. Turhollow, and J.W. Johnston. Herbaceous Energy Crops Program: Annual Progress Report for FY 1985 . ORNL – 6263. Oak Ridge National Laboratory, Oak Ridge, TN,

19896. 11. D.J. Parrish, D.D. Wolf, W.L. Daniels, D.H. Vaughan, and J.S. Cundiff. Perennial Species for Optimum Production of Herbaceous Bioma ss in the Piedmont, Final Report 1985-1989

. ORNL/Sub/85-27413/5, submitted to the Biomass Feedstock Development Program, Oak Ridge National Laboratory, Oak Ridge, Tennessee, 1990. 12. D.J. Parrish, D.D. Wolf, and W.L. Daniels. Perennial Species for Optimum Production of

Herbaceous Biomass in the Piedmont (Management Study, 1987 – 1991): Final Report

. ORNL/Sub/85-27413/7, submitted to the Biomass Feedstock Development Program, Oak Ridge National Laboratory, Oak Ridge, Tennessee, 1993. 13. D.I. Bransby, S.E. Sladden, and D.D. Kee, Selection and Improvement of Herbaceous Energy Crops for the Southeastern USA, Final Report in a Field and Laboratory Research Program for the period March 15, 1985 to March 19, 1990, ORNL/Sub//85-27409/5, Oak Ridge National Laboratory Biomass/ Feedstock Development Program, Oak Ridge, TN, 1990. 14. N. Wright, S creening of Herbaceous Species for En ergy Crop Production: Final Report 1985-1990

, ORNL/Sub/85-27411/5, 1990. 15. R.A. Pfeifer, G.W. Fick, D.J. Lathwell, and C. Maybee. Screening and Selection of Herbaceous Species for Biomass Production in the Midwest/Lake States: Final Report 1985-1989. ORNL/Sub/85-27410/5, submitted to the Biomass Feedstock Development Program, Oak Ridge National Laboratory, Oak Ridge, Tennessee, 1990. 16. J.H. Cherney, K.D. Johnson, J.J. Volenec, E.J. Kladivko, and D.K. Greene. 1990. Evaluation of Potential Herbaceous Biomass Crops on Marg inal Crop Land (1) Agronomic Potential. ORNL/Sub/85-27412/5&P1, submitted to the Biomass Feedstock Development Program, Oak Ridge National Laboratory, Oak Ridge, Tennessee, 1990. 17. I.C. Anderson, D.R. Buxton, and J.A. Hallam,, Selection of Herbaceous Energy Crops for the Western Corn Belt. Final Report Part I: Agronomic Aspects. ORNL/Sub/88-SC264/P1, Oak Ridge National Laboratory Biomass/ Feedstock Development Program, Oak Ridge, Tennessee, 1994.

Available at http://bioenergy.ornl.gov/main.aspx (use search function).

### 32 18. D.W. Meyer, W.E. Norby, D.O. Drickson, and R.G. Johnson. Evaluation of Herbaceous Biomass Crops in the Northern Great Plains . ORNL/Sub/88-SB844/2. Oak Ridge National Laboratory. Oak Ridge, TN 37880, 1994. Available at http://bioenergy.ornl.gov/main.aspx (use search function). 19. G.W. Fick, R.A. Pfeifer, and D.J. Lathwell. Production Patterns of Perennial Herbaceous Biomass Crops in the Great Lakes Region. Energy Sources 16:333-348, 1994. 20. C.L. Dobbins, P. Preckel, A. Mdafri, J. Lowenberg-DeBoer, and D. Stucky. Evaluation of Potential Herbaceous Biomass Crops on Marginal Crop Lands: (2) Economic Potential Final Report 1985-

1989 . ORNL/Sub/85-27412/5&P2. Oak Ridge Nati onal Laboratory, Oak Ridge, TN. 37880, 1990. 21. I.C. Anderson, D.R. Buxton, and J.A. Hallam, Selection of Herbaceous Energy Crops for the Western Corn Belt. Final Report Part II: Economic Potentials , ORNL/Sub/88-SC264/P2, Oak Ridge National Laboratory Biomass/ Feedstock De velopment Program, Oak Ridge, TN, 1994. 22. D.W. Meyer, D.E. Lippert, D.O. Erickson, and R.G. Johnson, Evaluation of Herbaceous Biomass Crops in the Northern Great Plains: 1990 Annual Report, ORNL/Sub/19X-SB844C/3. Oak Ridge National Laboratory, Oak Ridge TN37880, 1991. 23. R.G. Johnson, R.S. Sell, and D.W. Meyer. Economic Evaluation of Her baceous Biomass Crops in the Northern Great Plains-Economic Analysis . Report on Subcontract No. 19x-SB844c. Oak Ridge National Laboratory, Oak Ridge, TN. 37880, 1993b. 24. J.W. Johnston, Jr. Evaluation of the Potential for Using Old-Field Vegetation as an Energy Feedstock: Biomass Yield, Chemical Com position, Environmental Concerns, and Economics

. ORNL/TM-11615 Oak Ridge National Laboratory, Oak Ridge, TN 37880, 1990. Available at http://www.osti.gov/bridge/servlets/purl/6467844-Qfkbnw 25. J.H. Cushman, A.F. Turhollow, and J.W. Johnston. Herbaceous Energy Crops Program Annual Progress Report for FY 1987 . ORNL-6514. Oak Ridge Nationa l Laboratory, Oak Ridge, TN, 1989. 26. U.S. Department of Agriculture Soil Conservation Service, Basic Statistics 1982 National Resources Inventory, Statistical Bulletin No. 756, Iowa State University Statistical laboratory. September 1987. 27. A.F. Turhollow, J.H. Cushman, and J.W. Johnston. Herbaceous Energy Crops Program: Annual Progress Report for FY 1988 . ORNL-6639. Oak Ridge Nationa l Laboratory, Oak Ridge, TN, 1990. 28. E. Heaton, T. Voight, and S.P. Long. A quantitative review comparing the yields of two candidate C4 perennial biomass crops in relation to nitrogen, temperature, and water . Biomass and Bioenergy 27 (2004): 21-30, 2004a. 29. E.A. Heaton, J. Clifton-Brown, T.B. Voight, M.B. Jones, and S.P. Long. Miscanthus for Renewable Energy Generation: European Union Experience and Projections for Illinois . Mitigation and Adaptation Strategies for Global Change 9: 433-451, 2004b. 30. J. McLaren, Sorghum BioConversion Research: Sorghum – The Next Most Important Crop for Ethanol, Presented at the 2007 World Congress on Industrial Biotechnology and Bioprocessing, Orlando, Florida, Mar 21-24, 2007. more information on project can be found at http://www.strathkirn.com/Presentations/ASTAsorghum02.htm 31. G. Thomas, The Role of the Genus Sorghum as a Cellulosic Bio-feedstock, Presented at the 2007 World Congress on Industrial Biotechnology and Biopr ocessing, Orlando, Florida, Mar 21-24, 2007. 32. D. Tillman, J. Hill, and C. Lehman. Carbon-Negative Biofuels from Low-Input High-Diversity

Grassland Biomass . Science 8 December 2006:314:1598-1600. DOI: 10.1126/science.1133306.

33. David Tillman, Peter B. Reich, Johannes Knops, Da vid Wedin, Troy Mielke, and Clarence Lehman. Diversity and Productivity in a Long-Term Grassland Experim ent. Science 26 October 2001: Vol. 294. no. 5543, pp. 843 – 845, DOI: 10.1126/science.1060391. 34. Department of Energy, Office of Biomass Program. 30 x 30 Workshop. 2006

. Notes available at www.30x30workshop.govtools.us 35. Turhollow, A.F., J.W. Johnston, and J.H. Cushman. Linking Energy Crop Production to Conversion: The Case of Herbaceous Lignocellulosic Crops to Ethanol . RERIC International Energy Journal: Vol. 10, No. 2 (41-49), December 1988. 36. R.S. Butner, D.C. Elliot, L.J. Sealock, Jr., and J.W. Pyne, Effect of Biomass Feedstock Chemical and Physical Properties on Energy Conversion Processes , PNL6575 Vols. 1 and 2. Pacific Northwest Laboratory, Richland, WA 1988. 

### 37. K.P. Vogel and G.J. Hans-Joachim, Genetic Modification of Herbaceous Plants for Feed and Fuel, Critical Reviews in Plant Sciences 20(1): 15-49, 2001.

### 33 38. A.A. Snow, Transgenic crops-Why Gene Flow Matters , Nature Biotechnology 20:542, June

2002. 39. S. Sokhansanj, S. Mani, A.Turhollow, A. Kumar, D. Bransby, L. Lynd, M. Laser, Large Scale Production, Harvest and Transport of a Switchgrass ( Panicum virgatum L.) Current Technology and Visioning a Mature Technology. Manuscript submitted for publication to Biomass and Bioenergy in

June 2007. 40. C. M. Taliaferro, K.P. Vogel, J.H. Bouton, S.B. McLaughlin, and G.A. Tuskan, Reproductive Characteristics and Breeding Improvement Potential of Switchgrass. In: “Proceedings of the 4 th


### biomass Conference of the Americas – Biomass, A Growth Opportunity in Green Energy and ValueAdded Products” (R. Overend and E. Chornet, Eds.) pp. 147-153. Elsivier Sciences, Oxford, United Kingdom, 1999. 41. C.M. Taliaferro, Breeding and Selection of New Switchgrass Varieties for Increased Biomass

Production. ORNL/SUB-02-19XSY162C/01. Oak Ri dge National Laboratory, Oak Ridge,

Tennessee. 2002. 

### Available at: http://bioenergy.ornl.gov/main.aspx (search by author). 42. K.P. Vogel, Genetic Improvement of Switchgrass and Oth er Herbaceous Plants for Use as Biomass Fuel Feedstock: Final Report, ORNL/SUB/90-90OR21954/1, Oak Ri dge National Laboratory, Oak Ridge, TN. 

### Available at: http://bioenergy.ornl.gov/main.aspx (search by author). 43. L.E. Moser and K.P. Vogel, Switchgrass, Big Bluestem, and Indiangrass, pp. 409-420 In: Forages Volume 1: An Introduction to Grassland Agriculture (eds R.F. Barnes, D.A. Miller, C.J. Nelson), Iowa State University Press, Ames Iowa 50014, 1995. 44. K.P. Vogel, J.J. Brejda, D.T. Walters, D. R. Buxton, Switchgrass Biomass Production in the Midwest USA: Harvest and Nitrogen Management. Agronomy Journal 2002; 94:413-420. 45. A. Teel, S. Barnhard, G. Miller, Management Guide for the Production of Switchgrass for biomass Fuel Production in Southern Iowa, PM 1710, Iowa State University Extension, Revised May 2003.

Available at: http://www.extension.iastate.edu/Publications/PM1710.pdf

. 46. J. Lawrence, J. Cherney, P. Barney, Q. Ketterings, Establishment and Management of Switchgrass, Fact Sheet 20, Agronomy Fact Sheets, Cornell Univ ersity Cooperative Extension, 2006. Available at: http://nmsp.css.cornell.edu/publications/factsheets/factsheet20.pdf 

### 47. L. Rinehart, Switchgrass as a Bioenergy Crop, A Web Publication of ATTRA – National Sustainability Agriculture Information Service ( www.attra.ncat.org ), 2006. Available at www.attra.ncat.org/attra-pub/pdf/switchgrass.pdf

. 48. D.J. Parrish, D.D. Wolf, J.H. Fike, W.L. Daniels, Switchgrass as a Biofuels Crop for the Upper Southeast: Variety Trials and Cultural Improvements – Final Report for 1997 to

2001 , ORNL/SUB-03-19XSY163/01, Oak Ridge National Laboratory, Oak Ridge, Tennessee, 2003. Available at: http://bioenergy.ornl.gov/main.aspx

. 49. J. H. Reynolds, C.E. Sams, H.A. Fribourg, Photosynthesis and Forage Quality of Tall Fescue and Switchgrass, TEN00105 University of Tennessee, Department of Plant Sciences – Recent Findings on

website. 2000. Available at 

### http://plantsciences.utk.edu/sams_ad421_2000.htm

. 50. W.E. Thomason, W.R. Raun, G.V. Johnson, C.M. Taliaferro, K.W. Freeman, K.J. Wynnm, R.W.

Mullen. Switchgrass Response to Harvest Frequency and Time and Rate of Applied Nitrogen. Journal of Plant Nutrition 2004; 27:1199-1226. 

### 51. G.T. Byrd and P.A. May, II, Physiological Comparisons of Switchgrass Cultivars Differing in Transpiration Efficiency, Crop Science 40: 1271-1277, 2000. 52. D.G. De La Torre Ugarte, M.E. Walsh, H. Shapouri, S.P. Slinsky The Economic Impacts of Bioenergy Crop Production on U.S. Agriculture, U.S. Department of Agriculture, Office of Chief Economist, Office of Energy Policy and New U ses, Agricultural Economic Report Number 816, February 2003. Available at http://www.usda.gov/oce/reports/energy/index.htm

.

53. D.D. Wolf and D.A. Fiske, Planting and Managing Switchgra ss for Forage, Wildlife, and
Conservation, Publication 418-013, Virginia Coopera tive Extension, 1995. Available at: http://www.ext.vt.edu/pubs/forage/418-013/418-013.html

.

### 34 54. A. Teel, S. Barnhard, Switchgrass Seeding Recommendations for the Production of biomass Fuel in Southern Iowa, PM 1773, Iowa State University Extension, Revised May 2003. Available at: http://www.extension.iastate.edu/Publications/PM1773.pdf

. 

### 55. W. Ocumpaugh, M. Hussy, J. Read, J. Muir, F. Horns, G. Evers, K. Cassida, B. Venuto, J. Grichar, C. Tishchler, Evaluation of Switchgrass Cultivars and Cultural Methods for Biomass Production in the South Central U.S.- Consolidated Report 2002, ORNL/SUB-03- 19XSY091C/01, Oak Ridge National Laborator y, Oak Ridge, Tennessee, 2003. Available

at: http://bioenergy.ornl.gov/main.aspx (search by author). 56. B.V. Conger, Development of In Vitro Systems for Switchgrass (Panicum virgatum): Final Report for 1992 to 2002 , ORNL/SUB-02-11XSY161/01, Oa k Ridge National Laboratory, Oak Ridge, Tennessee, 2002. Available at: http://bioenergy.ornl.gov/main.aspx

. 57. B. Nyoka, P. Jeranyama, V. Owens, A. Boe, M. Moechnig, Management Guide for Biomass Feedstock Production from Switchgrass in the Northern Great Plains, SGINC2-07, North Central Sun Grant Center, South Dakota State Unive5rsity , Brookings, SD 57007, June 2007. Available at: http://agbiopubs.sdstate.edu/ articles/SGINC2-07.pdf

. 58. D.J. Parrish, J.H. Fike, The Biology and Agronomy of Switchgrass for Biofuels, Critical Reviews in Plant Sciences 2005; 24: 423-459. 59. S.B. McLaughlin, D.G. De La Torre Ugarle, C. T. Garten, Jr., L.R. Lynd, M.A. Sanderson, V.R. Tolbert, D.D. Wolf. High Value Renewable Energy from Prairie Grasses , Environmental Sciences and Technology 36:2122-2129, 2002. 60. P.C. Hipple and M.D. Duffy, Farmers’ motivations for Adoption of Switchgrass, In: Trends in new crops and new uses, J. Janick and A. Whipkey (eds), ASHS Press, Alexandria, VA. Also available at: http://www.hort.purdue.edu/newc rop/ncnu02/pdf/duffy-252.pdf

. 61. P.R. Adler, M.A. Sanderson, A.A. Boateng, P.J. Weimer, J.G. Hans-Joachim, Biomass Yield and Biofuel Quality of Switchgrass Harvested in Fall or Spring. Agronomy Journal 2006; 98:1518-1525.

### 35 Appendix A. AUBURN UNIVERSITY YIELD RESULTS

Dry matter yields of herbaceous species from 1985 to 1989 at four locations in Alabama analyzed separately for each location in each year (table scanned from Auburn final report (13)



### .

### 36

### 37 Appendix B. GEOPHYTA YIELD RESULTS

Mean dry matter yields for one harvest per seaso n at three locations in Ohio for four years (scanned from Geophyta final report (14)



### .

### 38

### 39 Appendix C. PURDUE UNIVERSITY YIELD RESULTS

Figure C1. Switchgrass yield response to nitrogen fertilization (0, 50, 150, and 2000 kg N ha -1



### . Means of four replicates and one location in 1988 and 1989 (figure scanned from Cornell final
report (15)



### .

Figure C2 Sweet sorghum yield response to nitrogen fertilization (0,50,100, and 150 kg N ha -1


### averaged over four replicates, four locations, a nd two tillage treatments (figure scanned from Cornell final report (15)



### .

### 40

### 41 Appendix D. IOWA STATE UNIVERSITY YIELD RESULTS

Yield results for energy crops tested at Ames, a good cropland site and Chariton, a marginal cropland site ( 17)

. Ames

YEAR MONOCROP DOUBLE CROP ROTATION INTERCROP

FERT

TRT ALF RCG SWG BBS SS SSH SWS/R SSH/R CORN SB SWS SWS/R ALF/

SS RCG/

SS kgN/ha ---------------------------------------------------------------Mg/ha/year-----------------------------------------------------------------

1988

0 5.97 8.1 6.8 15.1 14.4 9.1 9.6 7.7

70 6.1 5.2 7.7 5.7 15.3 13. 6 11.7 11.9 8.6

140 6.1 5.5 8.3 6.4 17.5 14. 6 12.0 14.0 11.3

280 5.2 7.9 5.5 16.7 14.7 12.3 16.4 11.9

1989

0 3.0 5.0 6.2 16.3 13.1 10.1 9.3 10.5

70 11.1 5.8 8.0 6.9 16.1 14.7 15. 8 15.0 15.1 13.1 19.38 16.9 7.5

140 12.9 7.9 8.3 6.4 15.3 16.3 19. 0 19.1 17.8 16.1 22.25 15.9 9.5

280 10.0 8.1 8.2 15.0 16.4 21.7 22.3 19.0

1990

0 5.8 7.2 10.7 11.4 10.8 11.6 9.1 11.1

70 10.2 7.2 11.6 10.7 15.3 11.4 15. 7 12.8 15.1 12.9 18.22 14.9 8.2

140 12.1 10.3 10.6 11.4 20.7 15.3 19. 6 15.1 16.6 16.8 22.53 15.5 10.4

280 11.6 13.3 11.9 19.6 16.9 18.2 21.9 18.7

1991

0 4.6 4.9 7.3 13.5 14.3 19.9 8.9 7.3

70 10.1 6.8 11.2 8.3 16.7 16.3 14. 2 12.0 10.2 12.5 18.69 15.4 10.9

140 10.3 7.9 10.3 7.7 16.5 16.7 20. 5 14.2 11.5 13.3 19.43 17.1 13.5

280 11.4 9.5 6.9 16.3 14.1 20.7 19.4 12.0

1992

0 2.9 7.2 8.4 8.6 11.5 8.5

70 9.3 4.5 13.8 11.1 17.7 15.1 7.2 17.0 11.1 7.3

140 8.2 6.8 15.3 12.4 17.4 15.6 11.7 18.4 11.9 9.5

280 12.3 15.9 14.3 16.4 16.7 12.2

Chariton

1988

0 17.8 12.8 10.3 10.2 7.7

70 16.8 14.1 9.9 11.1 8.6

140 17.9 13.9 9.6 11.4 11.3

280 19.3 14.0 11.4 12.5 11.9

1989

0 3.1 16.1 15.1 11.8 10.9 10.5

70 6.8 3.1 15.8 14.2 11.8 13.7 15.1 10.4 13.81 2.3

- 140 7.6 2.9 15.6 13.5 11.9 14.0 17.8 12.1 15.53 2.5

- 280 3.0 16.4 15.7 12.8 14.2 19.0

1990

0 7.1 5.8 7.3 16.4 15.2 12.4 0.95 11.1

70 9.9 11.3 6.6 29.7 20.7 20.4 14. 9 15.0 15.1 13.7 20.95 3.8

- 140 11.0 11.8 8.3 9.4 22.9 21.8 21. 1 19.7 16.6 19.5 26.72 3.9

- 280 13.1 8.3 9.4 19.1 22.7 26.6 24.1 18.7

1991

0 4.8 7.8 5.5 13.5 14.1 11.7 10.6 7.3

70 7.4 7.9 8.9 5.5 17.7 16.5 18.8 15.8 10.2 17.2 24.41

- - 140 9.1 9.9 10.7 6.4 16.8 16.4 21.3 18.8 11.5 20.2 25.29

- - 280 10.5 10.9 5.5 17.2 16.9 23.6 21.5 12.0

1992

0 6.3 9.7 5.8 8.7 8.7 8.5

70 8.9 7.9 12.4 9.2 16.1 12. 9 7.2 14.2

140 6.7 10.9 15.8 10.5 16.7 12. 6 11.7 15.9

280 12.8 17.4 12.8 16.5 17.0 12.2
Notes: ALF = alfalfa, RCG = reed canarygrass, SWG=switchgr ass, BBS=big bluestem. SS=sweet sorghum, SSH=sorghum x sudangrass, SWS/R=sweet sorghum doublecropped with winter rye, SSH/R=sorghum x sudangrass double cropped with wi nter rye, CORN=corn total p lant yield in a corn-soybean-sorghum three year rotation, in the corn -soybean-sorghum rotation, ALF/SS is intercrop of alfalfa with sweet sorghum, the sum of 3 harvests. RCG/SS involved the planting of sweet sorghum into a reed canarygrass stand, the sum of 3 harvests.

### 42

### 43 Appendix E. NORTH DAKOTA STATE UNIVERSITY YIELD RESULTS

Mean biomass yields of several perennials at si x North Dakota sites, averaged across years and Nitrogen levels, (scanned from North Dakota State University final report (18) 

### ).

### 44

### 45 ORNL/TM-2007/109

INTERNAL DISTRIBUTION

1. V.H. Dale 19. S. Sokhansanj 2-13. M.E. Downing 20. A.F. Turhollow

14. R.L. Graham 21. T.O. West

15. G.K. Jacobs 22. E.G. Wilkerson 16. J.R. Mielenz 23-24. L.L. Wright

17. R.D. Perlack 25. ORNL Central Research Library

18. M.J. Sale 26. ORNL Laboratory Records - RC

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6021 37. K.D. Kephart, South Dakota State University, ADM 130, Box 2201, Brookings, SD

57007 38. L. Neal, 8920 Stephens Road, Laurel, MD 20723 39. T. Nipp, 444 North Capitol Street, NW, Suite 715, Washington, DC 20001 40. G.R. Petersen, Department of Energy, Golden Field Office, MS 1511, 1617 Cole Blvd., Golden, CO 80401 41. T.G. Rials, The University of Tennessee, 2506 Jacob Drive, Knoxville, TN 37996-4570 42. L.J. Russo, U.S. Department of Energy, EE-2E, 1000 Independence Ave., SW, Washington, DC 20585 43. C.J. Rutzke, 120 Riley Robb Hall, Cornell University, Ithaca, NY 14853 44. S.G. Tagore, U.S. Department of Energy, EE-2E, 1000 Independence Ave., SW, Washington, DC 20585 45. L.P. Walker, 232 Riley-Robb Hall, Cornell University, Ithaca, NY 14853-5701