Characterization of Miscanthus Cell Wall Polymers

Characterization of Miscanthus Cell Wall Polymers

Received: 26 April 2018 | Revised: 17 July 2018 | Accepted: 30 May 2018 DOI: 10.1111/gcbb.12538 ORIGINAL RESEARCH Characterization of Miscanthus cell wall polymers Judith Schäfer1 | Melinda Sattler1 | Yasir Iqbal2 | Iris Lewandowski2 | Mirko Bunzel1 1Department of Food Chemistry and Phytochemistry, Institute of Applied Abstract Biosciences, Karlsruhe Institute of Efficient utilization of lignocellulosic Miscanthus biomass for the production of Technology (KIT), Karlsruhe, Germany biochemicals, such as ethanol, is challenging due to its recalcitrance, which is influ- 2Biobased Products and Energy Crops enced by the individual plant cell wall polymers and their interactions. Lignocellu- (340b), Institute of Crop Science, University of Hohenheim, Stuttgart, losic biomass composition differs depending on several factors, such as plant age, Germany harvest date, organ type, and genotype. Here, four selected Miscanthus genotypes Correspondence (Miscanthus sinensis, Miscanthus sacchariflorus, Miscanthus × giganteus, Mis- Mirko Bunzel, Department of Food canthus sinensis × Miscanthus sacchariflorus hybrid) were grown and harvested, Chemistry and Phytochemistry, Institute of separated into stems and leaves, and characterized for their non‐starch polysaccha- Applied Biosciences, Karlsruhe Institute of Technology (KIT), Karlsruhe, Germany. ride composition and structures, lignin contents and structures, and hydroxycinna- Email: [email protected] mate profiles (monomers and ferulic acid dehydrodimers). Polysaccharides of all genotypes are mainly composed of cellulose and low‐substituted arabinoxylans. Funding information Biotechnology and Biological Sciences Ratios of hemicelluloses to cellulose were comparable, with the exception of Mis- Research Council, and Department for canthus sinensis that showed a higher hemicellulose/cellulose ratio. Lignin contents Environment, Food and Rural Affairs of Miscanthus stems were higher than those of Miscanthus leaves. Considering the (GIANT-LINK project LK0863); Deutsche Forschungsgemeinschaft; Karlsruhe same organs, the four genotypes did not differ in their Klason lignin contents, but Institute of Technology Miscanthus × giganteus showed the highest acetylbromide soluble lignin content. Lignin polymers isolated from stems varied in their S/G ratios and linkage type dis- tributions across genotypes. p‐Coumaric acid was the most abundant ester‐bound hydroxycinnamte monomer in all samples. Ferulic acid dehydrodimers were ana- lyzed as cell wall cross‐links, with 8‐5‐coupled diferulic acid being the main dimer, followed by 8‐O‐4‐, and 5‐5‐diferulic acid. Contents of p‐coumaric acid, ferulic acid, and ferulic acid dimers varied depending on genotype and organ type. The lar- gest amount of cell wall cross‐links was analyzed for Miscanthus sinensis. KEYWORDS biomass, cell wall polysaccharides, cross‐links, lignin, Miscanthus 1 | INTRODUCTION yield capacity, tolerance for temperate climates, and its There is an increasing interest in using biomass from fast ability to grow on marginal land. Currently, Miscant- growing non‐food perennial grasses as renewable resource. hus × giganteus is the only genotype that is commercially Miscanthus, a perennial C4 grass, is considered a leading available in Europe. Introducing new genotypes are candidate for bioenergy production due to its high biomass required in order to reduce biomass production costs, ---------------------------------------------------------------------------------------------------------------------------------------------------------------------- This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited. © 2018 The Authors GCB Bioenergy Published by John Wiley & Sons Ltd | GCB Bioenergy. 2019;11:191–205. wileyonlinelibrary.com/journal/gcbb 191 192 | SCHÄFER ET AL. improve stress tolerance, and adapt biomass characteristics and the biomass needs to be pretreated to remove lignin. to user requirements (Lewandowski et al., 2016; Lewan- Besides lignin contents, the structural composition of lignin dowski, Clifton‐Brown, Scurlock, & Huisman, 2000). polymers may influence pretreatment processes, e.g. high Lignocellulosic biomass is made up of plant cell wall portions of β‐O‐4‐ethers can be easily cleaved during pre- polymers. Their composition is complex and often determi- treatment processes. Therefore, it is important to character- nes biomass recalcitrance. Cell walls of grasses are mainly ize all cell wall polymers of different Miscanthus composed of cellulose, hemicelluloses (arabinoxylans and genotypes in detail instead of limiting the analytical work mixed‐linked β‐glucans in particular grasses), and lignin to specific polymers to better evaluate the genotypes for (Vogel, 2008). In addition, hydroxycinnamates, such as fer- biomass utilization. For this reason, we analyzed four Mis- ulic and p‐coumaric acids are bound to polysaccharides canthus genotypes for their cell wall composition, and all and lignin. Ferulic acid is usually attached to arabinoxylans relevant polymers were characterized in detail. and is responsible for the formation of cross‐links between polysaccharides, and polysaccharides and lignin, whereas 2 | MATERIALS AND METHODS p‐coumaric acid is usually bound to lignin (Bunzel, 2010; ‐ Ralph, 2010) with only minor amounts of p coumaric acid 2.1 | Chemicals being attached to arabinoxylans (Allerdings, Ralph, Stein- hart, & Bunzel, 2006). In order to obtain biochemicals and Heat‐stable α‐amylase Termamyl 120 L (from Bacillus biofuels from lignocellulosic biomass, efficient pretreatment licheniformis, 120 KNU/g), the protease Alcalase 2.5 L procedures, followed by enzymatic hydrolysis, and micro- (from Bacillus licheniformis, 2.5 AU/g), and the amyloglu- bial fermentation processes are required (Rastogi & Shri- cosidase AMG 300 L (from Aspergillus niger, 300 AGU/g) vastava, 2017). Biomass pretreatment removes or alters were kindly donated by Novozymes (Bagsvaerd, Den- lignin, a key factor of biomass recalcitrance, and loosens mark); the complex carbohydrase mixture Driselase (from the cell wall polymer network. Enzymatic hydrolysis con- Basidiomycetes sp.) was from Sigma‐Aldrich (St. Louis, verts cellulose and hemicelluloses into monomers, which MO). Chemicals used, including deuterated NMR solvents, are fermented using various microorganisms. The efficiency were either from Sigma‐Aldrich, Roth (Karlsruhe, Ger- of these processes varies considerably depending on bio- many), VWR (Radnor, PA, USA), or Alfa Aesar (Ward mass composition. Thus, cell wall composition data of vari- Hill, MA, USA). ous Miscanthus genotypes is crucial to select suitable genotypes for potential biochemical and biofuel production. 2.2 | Field trial description The gross composition of Miscanthus biomass, i.e., cel- lulose, hemicellulose, and lignin contents, has been Miscanthus material was harvested from a field trial estab- described earlier (Arnoult & Brancourt‐Hulmel, 2015; da lished as a part of the European project OPTIMISC to Costa et al., 2017; Hodgson et al., 2011; Lygin et al., compare 15 Miscanthus genotypes at six sites across Eur- 2011; Zhao et al., 2014). A few authors also report some ope. A detailed description of the field trials and genetic structural details such as lignin monomer composition and/ material is provided in Kalinina et al. (2017). For this or lignin linkage type profiles (Cheng, Sorek, Zimmer- study four Miscanthus genotypes were selected from the mann, Wemmer, & Pauly, 2013; Le Ngoc Huyen, Rémond, location Stuttgart (lat. 48°74′N; long. 8°93′E). The field Dheilly, & Chabbert, 2010; Villaverde, Li, Ek, Ligero, & trial was planted from in‐vitro propagated plants on 22nd Vega, 2009), and acetylation degree of polysaccharides May 2012 on former arable land. Before planting out the (Van der Weijde et al., 2017). However, these data are plugs, the ground was prepared as follows: Weeds were mostly limited to Miscanthus × giganteus. Studies on removed with glyphosate, inversion ploughed and harrowed structural details of cell wall polymers such as lignin link- to produce a fine tilth. After planting, the plugs were age type profiles and ferulic acid dehydrodimer contents watered to provide a good hydraulic contact between the specific to other Miscanthus genotypes are rarely available. soil and plug. The genotypes were established in random- In addition, published studies often describe the relation- ized complete block design with three replications and each ship between individual constituents and fermentation plot comprised of 5 × 5 m with 49 plants (plugs) per plot yields without analyzing the whole cell wall composition (resulting in a density close to 2 plants per m2). in detail. In general, polysaccharide contents mainly deter- Post‐planting herbicide was not applied in the first year, mine the fermentation yield. However, efficient biomass and weeds were controlled mechanically. In the first year utilization is determined by the whole cell wall composi- (2012), fertilizer was applied at all the sites at rates of 44 tion because structural features of cell wall polymers and and 110 kg/ha phosphorus (P) and potassium (K), respec- polymer interactions also affect biomass recalcitrance. Lig- tively. No nitrogen (N) fertilizer was applied that year to nin is a key factor in determining biomass recalcitrance, avoid stimulating weed growth. From the second year SCHÄFER ET AL. | 193

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