Plant species composition and biofuel yields of conservation grasslands.

Marginal croplands, such as those in the Conservation Reserve Program (CRP), have been suggested as a source of biomass for biofuel production. However, little is known about the composition of plant species on these conservation grasslands or their potential for ethanol production. Our objective was to assess the potential of CRP and other conservation grasslands for biofuel production, describing the relationships of plant species richness and tall native C4 prairie grass abundance with plant chemical composition and the resulting potential ethanol yield. We determined plant species composition and diversity at multiple scales with the modified Whittaker plot technique, aboveground biomass, plant chemical composition, and potential ethanol yield at 34 sites across the major ecological regions of the northeastern USA. Conservation grasslands with higher numbers of plant species had lower biomass yields and a lower ethanol yield per unit biomass compared with sites with fewer species. Thus, biofuel yield per unit land area decreased by 77% as plant species richness increased from 3 to 12.8 species per m2. We found that, as tall native C4 prairie grass abundance increased from 1.7% to 81.6%, the number of plant species decreased and aboveground biomass per unit land area and ethanol yield per unit biomass increased resulting in a 500% increased biofuel yield per unit land area. Plant species richness and composition are key determinants of biomass and ethanol yields from conservation grasslands and have implications for low-input high-diversity systems. Designing systems to include a large proportion of species with undesirable fermentation characteristics could reduce ethanol yields.

[1]  D. Ugarte The Economic Impacts of Bioenergy Crop Production on U.S. Agriculture , 2000 .

[2]  Martin Zobel,et al.  Contrasting plant productivity-diversity relationships across latitude: the role of evolutionary history. , 2007, Ecology.

[3]  I. S. Pretorius,et al.  Microbial Cellulose Utilization: Fundamentals and Biotechnology , 2002, Microbiology and Molecular Biology Reviews.

[4]  B. Tracy,et al.  Pasture and cattle responses in rotationally stocked grazing systems sown with differing levels of species richness , 2006 .

[5]  David Tilman,et al.  Niche differences in phenology and rooting depth promote coexistence with a dominant C4 bunchgrass , 2005, Oecologia.

[6]  K. Vogel,et al.  In vitro gas production as a surrogate measure of the fermentability of cellulosic biomass to ethanol , 2005, Applied Microbiology and Biotechnology.

[7]  Robert B. Mitchell,et al.  Chemical composition and response to dilute-acid pretreatment and enzymatic saccharification of alfalfa, reed canarygrass, and switchgrass , 2006 .

[8]  W. Post,et al.  Conversion from agriculture to grassland builds soil organic matter on decadal timescales. , 2006, Ecological applications : a publication of the Ecological Society of America.

[9]  K. Gross,et al.  Fertilization effects on species density and primary productivity in herbaceous plant communities , 2000 .

[10]  Jeffrey F. Pedersen,et al.  Evaluation of a Filter Bag System for NDF, ADF, and IVDMD Forage Analysis , 1999 .

[12]  Les D. Murray,et al.  Potential effects on grassland birds of converting marginal cropland to switchgrass biomass production , 2003 .

[13]  J. Veech A Comparison of Landscapes Occupied by Increasing and Decreasing Populations of Grassland Birds , 2006, Conservation biology : the journal of the Society for Conservation Biology.

[14]  T. Stohlgren,et al.  Riparian zones as havens for exotic plant species in the central grasslands , 1998, Plant Ecology.

[15]  D. Tilman,et al.  Plant functional composition influences rates of soil carbon and nitrogen accumulation , 2008 .

[16]  J. Blair,et al.  Plant community responses to resource availability and heterogeneity during restoration , 2004, Oecologia.

[17]  A. Knapp,et al.  Dominant species maintain ecosystem function with non‐random species loss , 2003 .

[18]  M. Casler,et al.  Cultivar × Environment Interactions in Switchgrass , 2003 .

[19]  John Pierce,et al.  Bio-Based Industrial Products: Priorities for Research and Commercialization , 2000 .

[20]  John S. Shenk,et al.  Population Definition, Sample Selection, and Calibration Procedures for Near Infrared Reflectance Spectroscopy , 1991 .

[21]  Christopher L. Lant,et al.  Using GIS-Based Ecological-Economic Modeling to Evaluate Policies Affecting Agricultural Watersheds , 2005 .

[22]  J. Blair,et al.  Modulation of diversity by grazing and mowing in native tallgrass prairie , 1998, Science.

[23]  Alan K. Knapp,et al.  Effect of Fire and Drought on the Ecophysiology of Andropogon gerardii and Panicum virgatum in a Tallgrass Prairie , 1985 .

[24]  C. Lortie,et al.  Do biotic interactions shape both sides of the humped-back model of species richness in plant communities? , 2006, Ecology letters.

[25]  D. D. Wolf,et al.  Switchgrass Biomass Composition during Morphological Development in Diverse Environments , 1995 .

[26]  Akwasi A. Boateng,et al.  Biomass Yield and Biofuel Quality of Switchgrass Harvested in Fall or Spring , 2006 .

[27]  T. Fukami,et al.  Productivity–biodiversity relationships depend on the history of community assembly , 2003, Nature.

[28]  D. Tilman,et al.  Carbon-Negative Biofuels from Low-Input High-Diversity Grassland Biomass , 2006, Science.

[29]  J. Blair,et al.  CHANGES IN ECOSYSTEM STRUCTURE AND FUNCTION ALONG A CHRONOSEQUENCE OF RESTORED GRASSLANDS , 2002 .

[30]  T. Stohlgren,et al.  A Modified-Whittaker nested vegetation sampling method , 1995, Vegetatio.