Seasonal changes in chemical composition and leaf proportion of elephantgrass and energycane biomass
Introduction
Dependence on imported fossil fuels has created political and economic challenges for many countries, and combustion of fossil fuels is associated with climate change (Kim and Day, 2011, Parrish and Fike, 2005). Lignocellulose represents an alternative energy production system; a potential cellulose-to-liquid fuel bioenergy (Anderson and Akin, 2008, Carroll and Somerville, 2009). Perennial C4 grasses are a promising source of lignocellulose for conversion to biofuel in the Southeast USA (Knoll et al., 2012, Na et al., 2015a). Elephantgrass [or napiergrass; Pennisetum purpureum Schum.; synonym Cenchrus purpureus (Schumach.) Morrone], and energycane (Saccharum spp. hybrid) have documented high biomass production (Morais et al., 2012, Na et al., 2015b, Woodard and Prine, 1993) and are considered two of the most promising dedicated energy crops in tropical and subtropical environments (Fedenko et al., 2013).
While high levels of lignocellulose are desirable for biofuel production, high N and/or ash concentrations in biomass may reduce the efficiency of thermochemical conversion to fuel (Shahandeh et al., 2011). Thus, characterizing the chemical properties of biomass is important. The detergent fiber analyses, which were originally proposed for forages (Van Soest et al., 1991), provide estimates of cell wall constituents including cellulose, hemicellulose, and lignin. They can be useful indicators of cellulosic biomass quality because the plant cell wall is the primary energy source for ruminant microorganisms (Guretzky et al., 2011, Jung and Lamb, 2004), and in the ruminant animal these microbes face barriers limiting access to structural carbohydrates that are similar to those that occur in bioconversion to ethanol (Lorenz et al., 2009a). Further, it has been shown that cellulose and hemicellulose concentrations, estimated from detergent fiber analysis, are correlated with theoretical ethanol yield potential (r = 0.91 and 0.51, respectively; Lorenz et al., 2009b).
For a relatively low value crop such as perennial grasses for biofuel, it is essential to minimize N input and increase efficiency of N cycling (Erickson et al., 2012, Erisman et al., 2010). Previous research has shown that concentrations of N, P, and K in harvested plant material are dependent on harvest date (Adler et al., 2006, Heaton et al., 2009, Kering et al., 2012), and nutrient removal in harvested biomass is strongly affected by harvest date and frequency (Na et al., 2014). Changes in plant-part proportion as the season progresses, specifically decreasing amount of leaf (Woodard et al., 1993), affect biomass nutrient concentration and inform harvest timing decisions.
Most biomass plant-part and nutrient composition data for perennial grasses are from experiments harvested once at the end of the growing season (Adler et al., 2006, Fedenko et al., 2013, Guretzky et al., 2011). Thus, there are limited data available that describe compositional changes of perennial grasses throughout the growing season. This information, along with seasonal patterns of biomass accumulation (Na et al., 2015a), is valuable for identifying optimum harvest dates and frequencies. The objectives of this experiment were to quantify seasonal changes in i) fiber and nutrient composition of elephantgrass and energycane biomass and ii) leaf proportion and the effect of inclusion of leaf on composition of harvested biomass.
Section snippets
Experimental site, treatments, and design
A field experiment was conducted during 2010 and 2011 at the University of Florida Plant Science Research and Education Unit at Citra, Florida (29°24′20″N, 82°08′41″W and 22 m altitude). The soil series was a well-drained Candler sand (hyperthermic, uncoated Lamellic Quartzipsamments) (Soil Survey Staff, 2013). Initial soil characterization of topsoil (0–20 cm) showed an average soil pH of 7.0, and Mehlich-1 extractable P, K, and Mg of 54, 20, and 123 mg kg−1, respectively. These concentrations are
Leaf proportion in total biomass
Leaf proportion in total biomass was affected by entry and sampling date main effects in 2010 (P < 0.001) and the interaction of entry and sampling date in 2011 (P < 0.001, Fig. 3). In 2010, leaf percentage averaged across the two elephantgrasses (Merkeron and UF1) and one energycane (L79-1002) decreased from 56% in June to 19% in December. Average leaf percentage over the season was greatest for L79-1002 and Merkeron (34 and 33%, respectively) and least (26%) for UF1 (Fig. 3). In 2011, L79-1002
Discussion
Second year (2011) tillers came from established rhizomes from the first year of growth, whereas first year (2010) tillers came from stems planted during the preceding winter season. In addition, the last freeze event in spring 2010 was 7 March compared with 14 February in 2011. Thus, initial growth in the spring of 2010 began considerably later than in 2011, and as a result the effective maturity of plants at a given sampling date was less in Year 1 than Year 2. Changes in plant biomass
Conclusion
There were important seasonal changes and differences in chemical composition among grasses. In general, elephantgrass cell wall constituents increased from early in the growing season until late summer and either remained relatively constant (UF1) or slightly increased (Merkeron) during the remainder of the growing season. Unlike elephantgrass, once energycane cell wall constituents peaked in late summer, concentrations tended to decrease thereafter. The concentrations of N and ash in biomass
Acknowledgements
We gratefully acknowledge the assistance of Dwight Thomas, Miguel Castillo, Kim Mullenix, Nick Krueger, and Marcelo Wallau with data collection and field management.
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