The Catabolism of Complex Carbohydrates in Four Representative Examples of the Geobacillus Genus Submitted by George Mackford Taylor, to the University of Exeter as a thesis for the degree of Masters of Science by Research in Biosciences, August 2014. This thesis is available for Library use on the understanding that it is copyright material and that no quotation from the thesis may be published without proper acknowledgement. I certify that all material in this thesis which is not my own work has been identified and that no material has previously been submitted and approved for the award of a degree by this or any other University. Signature…………………………………………………………................................ ACKNOWLEDGEMENTS ACKNOWLEDGEMENTS I would like to acknowledge my supervisor Prof. John Love and colleague Dr. Tom Howard for their valuable insights and guidance, which have been vital to this project. I would also like to thank Dr. Thomas Lux for his bioinformatic analysis of the Geobacillus genome, which was essential in starting this research and offer my thanks to Shell Research Ltd. who financially supported this project. 2 ABSTRACT ABSTRACT The ever-increasing demand for transportation fuels, the decrease in global petroleum reserves, and the negative impact of greenhouse gases make renewable and sustainable biofuels an imperative for the future. First-generation biofuels produced from food crops are limited by cost and competition with food supply. Despite considerable effort to produce fuels from lignocellulosic biomass, chemical and enzymatic pretreatment to solubilise the biomass prior to microbial bioconversion remains a major economic barrier to the development of an industrial process. Here we report the complete genomic surveys of complex carbohydrate catabolism in four representative examples of the Geobacillus genus: G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus and G. kaustophilus. In concordance with the genomic survey the empirical confirmation of mono-, di- and poly- saccharide degradation in each species was investigated. The data collected indicates that all four species were able to utilise a wide range of C5 and C6 monosaccharides and the disaccharide cellobiose, which are all catabolic products of lignocellulosic biomass. G. thermodenitrificans was also able to catabolise one of the major carbohydrates of lignocellulose, xylan. G. thermoglucosidans, G. stearothermophilus and G. kaustophilus however were unable to utilise xylan for growth. Comparison of the G. thermodenitrificans and G. thermoglucosidans xylan degradation genes highlighted a xylan 1,4-β-xylosidase predicted in G. thermodenitrificans but not predicted in G. thermoglucosidans, which suggested an incomplete pathway. We created several constructs with Gtn xynB to test sub-cellular localisation of this enzyme and whether introduction allows xylan utilisation in G. thermoglucosidans. 3 LIST OF CONTENTS LIST OF CONTENTS LIST OF FIGURES 6 LIST OF TABLES 8 1. INTRODUCTION 9 1.1 Cellulose 11 1.2 Hemicellulose 11 1.3 Lignin 13 1.4 Synthetic catabolism of lignocellulose 15 2. MATERIALS AND METHODS 19 2.1 Bacteria 19 2.2 Media 19 2.3 Plasmids 19 2.4 Transformations 19 2.5 Genome analysis 21 2.6 Data analysis 22 3. RESULTS 23 3.1 In silico analysis of carbohydrate catabolic potential in Geobacillus 23 3.1.1 Phylogeny of the Geobacillus genus and selection of representative species 23 3.1.2 Identification and mapping of carbohydrate catabolic enzymes 3.2 Formulation of minimal growth media for Geobacillus 3.2.1 Geobacillus growth is sustained by tryptone and peptone 23 27 27 3.2.2 Geobacillus growth in ASM medium and formulation of a new minimal medium 31 3.3 In vivo analysis of carbohydrate metabolism in representative Geobacillus 37 3.3.1 Controls: Geobacillus growth without carbohydrate addition or in glycerol 37 3.3.2. Geobacillus growth with C6 saccharides 41 3.3.3. Geobacillus growth with C5 saccharides 41 3.3.4. Geobacillus growth in hydrotreated lignocellulose (RAPT) 46 3.4 Engineering xylan catabolism in Geobacillus thermoglucosidans 46 3.4.1 Plasmid constructs and transformation 48 4 LIST OF CONTENTS 3.4.2 Growth of Geobacillus thermoglucosidans engineered with xylanase 51 3.4.3 Gtn xynB contains an active extracellular export signal 51 4. DISCUSSION 55 4.1.1 Catabolism of carbohydrates in the Geobacillus genus 55 4.2.1 Transgene expression 56 4.3.1 Wider aspect 57 5. CONCLUSION 60 6. BIBLIOGRAPHY 61 5 LIST OF FIGURES LIST OF FIGURES Figure 1-1. Bioconversion strategies for converting lignocellulose into biofuels 10 Figure 1-2. Catabolic pathway for the degradation of cellulose to glucose 12 Figure 1-3. Catabolic pathway for the degradation of xylan to xylose 14 Figure 2-1. Plasmid map of pS797 20 Figure 3-1. Phylogenetic tree based on the predicted pangenome of all selected Geobacilli 24 Figure 3-2. Glycolysis pathway map 25 Figure 3-3. Growth of G. thermodenitrificans in TGP media 32 Figure 3-4. Growth of G. thermodenitrificans in variations of TGP media 33 Figure 3-5. Growth of G. thermodenitrificans in a range of tryptone and peptone concentrations Figure 3-6. 34 G. thermodenitrificans growth in a minimal tryptone or peptone concentration supplemented with glucose or glycerol 35 Figure 3-7. Growth of G. thermodenitrificans in TGP and ASM media 36 Figure 3-8. Growth of G. thermodenitrificans in ASM buffered with a range of MOPS concentrations 38 Figure 3-9. pH and bacterial growth of G. thermodenitrificans in buffered ASM 39 Figure 3-10. Growth of four representative Geobacillus species in MASM without carbohydrate or in the presence of glycerol 40 Figure 3-11. Growth of four representative Geobacillus species investigated in the presence of C6 saccharides 42 Figure 3-12. Growth of Geobacillus in MASM supplemented with microcrystalline cellulose (avicel) 44 Figure 3-13. Growth of Geobacillus in the presence of C5 saccharides 45 Figure 3-14. Growth of G. thermodenitrificans in the presence of hydrotreated lignocellulose “RAPT” 47 Figure 3-15. Plasmid constructs for G. thermoglucosidans xylan catabolism 49 Figure 3-16. Plasmid construct for Gtn xynB cellular localization 50 LIST OF FIGURES Figure 3-17. Growth of G. thermoglucosidans engineered with pXYNB 52 Figure 3-18. Growth of G. thermoglucosidans engineered with pPldhA::XYNB 53 Figure 3-19. Expression of sGFP in G. thermoglucosidans engineered with pXYNB70::sGFP 54 7 LIST OF TABLES LIST OF TABLES Table 1-1. Literature review of Geobacillus species carbohydrate utilisation 17 Table 3-1. Enzymes involved in the catabolism of glycerol to glyceraldehyde-3phosphate in Geobacillus 26 Table 3-2. Enzymes involved in the catabolism of cellulose to glucose in Geobacillus 28 Table 3-3. Enzymes involved in the catabolism of xylan to glyeraldehyde-3phosphate in Geobacillus 29 Table 3-4. Enzymes involved in the catabolism of arabinose to glyeraldehyde-3phosphate in Geobacillus Table 3-5. 30 Maximal specific growth rates of the four Geobacillus species investigated on a range of carbon sources 43 INTRODUCTION 1. INTRODUCTION The increasing demand for fuels, limited secure accessible global petroleum reserves, and the impact of greenhouse gases on climate change have increased the need for renewable and sustainable biofuels (1, 2, 3, 4). First generation biofuels have been derived from food crops such as sugar cane, corn, wheat, and sugar beets (5, 6, 7). However, producing a high volume of first generation biofuels from food crops creates direct competition with the food supply driving higher food prices (5). For next generation biofuels to be economically and environmentally sustainable, they must be produced from renewable resources that do not compete with food supply and have mitigation potential for greenhouse gas emissions. Biofuels produced from more abundant and underused resources such as plant biomass (second generation), algal biomass (third generation) and greenhouse gases such as carbon monoxide and carbon dioxide (fourth generation) (5) could overcome and prevent the link between food and fuel price. Plant biomass (lignocellulose) is the most abundant biomass on Earth and consists of about 70% sugars (5, 8) and for this reason it is a leading candidate for a renewable substrate. Plant biomass presents a major challenge for downstream processing as the majority of carbon is derived from the plant cell wall in the form of recalcitrant structural biopolymers rather than residing in the more easily accessible sugars, starch, and oil fractions (9, 10). The composition of cell walls varies widely among plant species (11), but is primarily composed of five components: cellulose (~35-60%), hemicellulose (~20-35%), lignin (~10-25%), pectin, and minerals that are collectively referred to as lignocellulose (12). Lignocellulose has drawn intense interest as a potentially sustainable carbon source because degradation of cellulose and hemicellulose directly yields fermentable hexose (C6) and pentose (C5) sugars. Consolidated bioprocessing (CBP) is an approach for second-generation biofuel (bioethanol) production from lignocellulosic feedstocks. The process has generated much interest because it utilizes microorganisms to perform the direct hydrolysis and the fermentation of biomass to biofuel a single process without the need for added enzymes. Current strategies for second-generation biofuel production require three major operational steps: physiochemical pretreatment, enzymatic saccharification and fermentation (Fig 1-1) (5, 13). Pretreament and enzymatic hydrolysis represent substantial cost. It is predicted that the use of cellulolytic microbes for consolidated bioprocessing and eliminating pretreatment would reduce bioprocessing costs by 40% (2). However, few industrially tractable microbes possess the inherent ability to catabolise these complex sugars. 9 INTRODUCTION A B Conven onal Strategy 1st genera on CBP (current strategy) Plant Biomass Plant Biomass C 2nd genera on CBP Plant Biomass Physiochemical pretreatment (High temperature, acid or alkali treatment) Pretreated Biomass Pretreated Biomass Enzyma c hydrolysis Fermentable Sugars CBP; hydrolysis and fermenta on by a single organism Single Step BioProcessing: hydrolysis and fermenta on by a single organism without Pretreatment Fermenta on Biofuel Recovery Biofuel Recovery Biofuel Recovery Figure 1-1. Bioconversion strategies for converting lignocellulose into biofuels. (A) typical current bioprocess, (B) consolidated bioprocessing (CBP) of pretreated plant biomass involving saccharolytic fermentative thermophile, and (C) CBP of untreated plant biomass involving saccharolytic fermentative thermophile. Shaded boxes highlight stages performed by microbes. 10 INTRODUCTION 1.1 Cellulose Cellulose is the major load-bearing component of plant cell walls and is thought to be the most abundant biopolymer on Earth (14). Cellulose microfibrils are insoluble, cable-like structures composed of approximately 24 hydrogen-bonded chains containing β(1,4)-linked glucose molecules (15, 16). The glucan chains are parallel, and successive glucose residues are rotated 180 degrees to form a repeating disaccharide unit called cellobiose. This allows glucan chains to form a flat, relatively inflexible, ribbon-like crystalline structure held together by hydrogen bonds and Van der Waals forces to form microfibrils (17). Cellulases break down cellulose. Both bacterial and fungal species have been reported to produce thermostable cellulases. Thermophilic and mesophilic fungal genera such as Aspergillus, Rhizopus, Trichoderma, Sclerotium, Sporotrichum thermophile, Thermoascus thermophile var. coprophile, Chaetomium thermophile and Coniochaeta ligniara belonging to the (18, 19) produced cellulases. genera Bacillus, Geobacillus, Several thermophilic bacteria, Caldibacillus, Acidothermus, Caldocellum, and Clostridium also produce thermostable cellulase (20, 21, 22, 23, 24, 25, 26, 27, 28, 29, 30, 31). The depolymerisation of cellulose is catalysed by cellulases (Fig. 1-2). Three cellulases have been reported, endoglucanase (1,4- β-D-glucan glucohydrolase [EC 3.2.1.4]), exoglucanase (1,4-β-D-glucan cellobiohydrolase [EC 3.2.1.91]), and βglucosidase (β-D-glucoside glucohydrolase [EC 3.2.1.21]) work synergistically to hydrolyze cellulose (32, 33). Endoglucanase hydrolyses the (1→4)-β-D-glucosidic linkages in cellulose randomly, producing oligosaccharides, cellobiose and glucose. Exoglucanase hydrolyses (1→4)-β-D-glucosidic linkages in cellulose, releasing cellobiose from either the non-reducing or reducing termini and β-glucosidase hydrolyses cellobiose to glucose (34). Alternatively, cellulose can undergo hydrolysis of the non-reducing terminal releasing α-D-glucose, which is catalysed by αglucosidase ([EC 3.2.1.20]). 1.2 Hemicellulose Hemicellulose is a general designation for a diverse class of linear and branched polysaccharides that differ widely in composition among plant development (12). Most hemicelluloses have a β(1,2)-linked glucan, xylan, galactan, mannan, or glucomannan backbone that is branched with single or longer glycosyl residues (35). Although hemicellulose represents a potentially large fermentable pool of sugar, it presents challenges to biofuel production. 11 INTRODUCTION Cellulose Catabolism Cellulose Endoglucanase (EC 3.2.1.4) Exoglucanase (EC 3.2.1.91) α-glucosidase (EC 3.2.1.20) Cellobiose β-glucosidase (EC 3.2.1.21) 2x Glucose Figure 1-2. Catabolic pathway for the degradation of cellulose to glucose. The degradation of cellulose requires the synergistic action of multiple enzymes to degrade the polysaccharide to glucose. The mechanism involves endoglucanase randomly hydrolysing cellulose into oligosaccharides, which in turn are subject to either exoglucanase, which catalyses the release of cellobiose, or α-glucosidase, which catalyses the successive release of glucose from the non-reducing terminal. Subsequently β-glucosidase hydrolyses cellobiose to generate 2 glucose units. 12 INTRODUCTION Xylan is the most abundant hemicellulose in grasses such as Panicum virgatum (switchgrass) and Miscanthus (rhizomatous grass) and angiosperm hardwoods, such as Eucalyptus globulus (eucalyptus), Salix (willow) and Populus (aspen) (36, 37). The backbone of xylan consists of a linear polymer of β-(1,4)-linked xylosyl units, which is most commonly decorated with arabinosyl, xylosyl, or glucuronic acid substituents (37, 38). However, the structure of xylan is highly variable among different species largely due to the differing pattern of substituents (12). Xylan degrading enzymes are produced by various organisms like fungi, bacteria, yeast, marine algae, protozoans, snails, crutaceans, insects, and seeds (39, 40). Bacteria and fungi are large producers of thermostable xylanases (40, 41). Thermostable xylanases are produced by fungi including Laetiporus sulphureus (42), Talaromyces thermophiles (43), Thermomyces lanuginosus (44), Nonomuraea flexuosa (45) and Thermoascus aurantiacus (45). Thermophilic bacteria such as Bacillus (46, 47, 48), Geobacillus (49, 50), Thermotoga (51, 52), Acidothermus (53), Paenibacillus (54, 55), Thermoanaerobacterium (56), Actinomadura (57), Alicyclobacillus (58), Anoxybacillus (59), Nesterenkonia (60), and Enterobacter (61) have been reported to produce thermostable xylanases. Complete enzymatic hydrolysis of hemicellulose requires the synergistic action of numerous enzymes including endo-β-1,4-xylanases ([EC 3.2.1.8]), xylan 1,4-βxylosidases ([EC 3.2.1.37]), α-L-arabinofuranosidase ([EC 3.2.1.55]), α-glucuronidases ([EC 3.2.1.139]), acetylxylan esterases ([EC 3.1.1.72]), feruloyl esterases ([EC 3.1.1.73]), mannan endo-1,4-β-mannanases ([EC 3.2.1.78]), β-1,4-mannosidases ([EC 3.2.1.25]), and arabinan endo 1,5-α-L-arabinosidases ([EC 3.2.1.99]) (34, 41, 62, 63). In the case of xylan, endo-1,4-β-xylanase and xylan 1,4-β-xylosidase hydrolyse the xylan backbone (Fig. 1-3). Endo-1,4-β-xylanase hydrolyses internal (1,4)-β-D- xylosidic linkages in xylan backbone resulting in varied length xylooligosaccharides (xylobiose, xylotriose, xylotetrose, etc.). Xylan 1,4-β-xylosidases catalyses the hydrolysis of xylooligosaccharides from the non-reducing termini into individual xylose units (64). 1.3 Lignin Lignin is a highly complex aromatic heteropolymer whose biological role in plants is to increase cell wall integrity and resistance to attack by pathogens (65). It is mainly composed of the monolignols ρ-courmaryl, coniferyl, and sinapyl alcohols, which give rise to the ρ-hydroxyphenyl (H), guaiacyl (G) and syringyl (S) lignin units (66). This rigid structure can comprise up to 30% plant biomass and encloses both cellulosic and 13 INTRODUCTION Xylan Catabolism Xylan α-L-Arabinofuranosidase (EC 3.2.1.55), α-Glucuronidases (EC 3.2.1.139), Acetylxylan esterases (EC 3.1.1.72), Feruloyl esterases (EC 3.1.1.73) Xylan Arabinose Endo-β-1,4-xylanase (EC 3.2.1.8) Xylan 1,4-βxylosidase (EC 3.2.1.8) Xylose Figure 1-3. Catabolic pathway for the degradation of xylan to xylose. The degradation of xylan requires the synergistic action of multiple enzymes to debranch the hemicellulose and to depolyermise the backbone. Initially debranching is catalysed by α-L-arabinofuranosidase, α-glucuronidase, acetylxylan esterase and feruloyl esterase. The subsequent backbone is depolymerised by endo-1,4-β-xylanase, which catalyses the random hydrolysis generating xylooligosaccharides, which in turn are subject to xylan 1,4-β-xylosidase that catalyses the release of xylose units from the non-reducing terminal. 14 INTRODUCTION hemicellulosic fractions making their microbial degradation impossible without the depolymerisation of lignin (7, 67, 68, 69). Despite the naturally evolved recalcitrance of lignin, some microbes have evolved enzymatic approaches to lignin degradation. The most active lignin degraders identified to date are fungi, such as those belonging to the white-rot or brown-rot families that decompose wood (70, 71, 72). The current model for microbial lignin degradation invokes the oxidative combustion of lignin mediated by a broad range of small molecule oxidants produced by metalloenzymes, such as vetratryl alcohol cation radical (73) and various Mn (III) coordination complexes (74, 75). These diffusible mediators, rather than the enzymes are thought to react direcly with lignin to generate radical sites with the substrates and initiate a cascade of bond scission reactions that ultimately leads to its decomposition to smaller aromatic compounds, CO2, and water (65). 1.4 Synthetic catabolism of lignocellulose Considerable effort has been made to develop a single microbe capable of both saccharification (hydrolysis of polysaccharides) and fermentation to avoid the substantial expense of using saccharolytic enzyme mixtures (76). The heterologous expression of saccharolytic enzymes has been demonstrated in a number of organisms, including Saccharomyces cerevisiae, Zymomonas mobilis, and Escherichia coli (76, 77, 78). Xylanases were engineered into E. coli to make fatty-acid-derived fuels (FA-fuels) directly from hemicellulose; fatty acid ethyl esters (FAEEs) were produced at 11.6 mg l-1 from a glucose and hemicellulose mix (79). Cellulases are complex enzymes and difficult to express heterologously (80). However, E. coli strains have also been engineered to grow on either cellulose or hemicellulose and, separately, produce pinene, butanol or FAEEs. Co-cultures of two such strains -1 produced 71 mg l FAEEs from pretreated switchgrass (77). E. coli expressing a betaglucosidase was able to produce isopropanol from cellobiose at titers up to 4 g l-1 (81). B. subtilis has been engineered to overexpress an endoglucanase and express minicellulosomes on its surface (82, 83). Although these approaches have resulted in progress in cellulose and hemicellulose utilisation, the overall enzyme activity is still very low compared with that of naturally cellulolytic organisms and the rates of hydrolysis are not sufficient for an industrial process that produces a low value product such as automobile fuel (76). Thermophilic microorganisms have a number of potential advantages over mesophiles as a microbial chassis for the conversion of lignocellulosic biomass to liquid transport fuels. Growing at temperatures of 50-80 ˚C thermophiles are sources of highly active and thermostable enzymes (18, 20, 21, 84, 85, 86, 87, 88). These 15 INTRODUCTION thermostable enzymes offer several potential advantages in the hydrolysis of lignocellulosic materials such as the increased solubility of reactants and products, resulting in higher reaction velocities thus decreasing the amount of enzyme needed (87, 89); shorter hydrolysis times; decreased risk of contamination, and thus, increased productivity; facilitated recovery of volatile products e.g. ethanol (90); and decreased cost of energy for cooling after thermal pretreatment. Moreover thermophiles have been widely accepted as the most efficient microbial group as producers of thermostable cellulases and xylanases for the degradation of lignocellulosic biomass (47, 85, 91). For example, thermophile Thermoanaerobacterium species were engineered with a thermostable mannanase and three cellulolytic enzymes in aim of improving the bacteria as a model system for lignocellulosic degradation (92). The Geobacillus genus is one promising candidate for lignocellulose to biofuel conversion; its thermophilic nature is desirable for biomass breakdown and fuel isolation (93). Members of the genus are capable of aerobic and facultatively anaerobic growth at temperatures between 40 and 70 ˚C (94). Geobacillus can ferment both hexose and pentose sugars (95) and, moreover, extracellular endo/ exoglucanase activity has been demonstrated in Geobacillus species, such as Geobacillus sp. R7 (84) and Geobacillus sp. T1 (17). Geobacillus sp. R7 and sp. T1 have not demonstrated growth on cellulose, only to produce cellulase in its presence (17, 84). In addition, literature concerning cellulase activity in Geobacillus reports levels with an activity too low to support growth. For example, under optimal conditions Geobacillus spp. have produced endoglucanase activities of 0.0113 U ml-1 (30), 0.058 U ml-1 (21) and 0.064 U ml-1 (96). Moreover, literature shows fermentation of all C5 and C6 sugars to be in the presence of an alternative carbon source (Table 1-1), such as tryptone or yeast extract that could be a potential substrate for growth. Therefore this project investigates the input pathway of Geobacillus by analysing their growth on a variety of carbon sources that compose lignocellulose. We report here the presence of catabolic pathways for mono-, oligo- and polysaccharides, demonstrating the ability of four representative species from Geobacillus genus to ferment specific carbohydrates. This thesis presents a genomic survey of the catabolic pathways of specific sugars in G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus and G. kaustophilus. Subsequently, the growth of G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus and G. kaustophilus was monitored on these carbohydrates to confirm the catabolic pathways indicated by genomic mapping. Having established sugars that cannot be natively fermented by the four Geobacillus species a synthetic pathway was designed and engineered for xylan 16 INTRODUCTION Carbon Source L-Arabinose L-Arabinose Geobacillus Species G.kaustophilus G. thermoglucosidans Tryptone/ Yeast Extract 10 g/l Tryp Tryp Reference (97) (98) Cellobiose G. thermoglucosidans 10g/l Tryp (99) Cellobiose G. thermoglucosidans 1% YE (95) Cellobiose G.kaustophilus 10 g/l Tryp (97) Cellobiose G. Strain C5 0.5g/l YE (100) Glucose G. thermoglucosidans Tryp (98) Glucose G. thermoglucosidans 10g/l Tryp (99) Glucose G. Strain C5 0.5g/l YE (100) Glucose G. caldoproteolyticus 0.5g/l YE (101) Glycerol G. Strain C5 0.5g/l YE (100) Glycerol G. thermoglucosidans 1% YE (95) Glycerol G. caldoproteolyticus 0.5g/l YE (101) Maltose G.kaustophilus 10 g/l Tryp (97) Soluble Starch Starch Sucrose G.kaustophilus G. caldoproteolyticus G. thermoglucosidans 10 g/l Tryp 0.5g/l YE Tryp (97) (101) (98) Sucrose G.kaustophilus 10 g/l Tryp (97) Sucrose Sucrose Trehalose G. Strain C5 G. caldoproteolyticus G. Strain C5 0.5g/l YE 0.5g/l YE 0.5g/l YE (100) (101) (100) Xylan G. thermodenitrificans 3g/l YE (102) D-Xylose G. thermoglucosidans 10g/l Tryp (99) D-Xylose G.kaustophilus 10 g/l Tryp (97) D-Xylose G. thermoglucosidans 1% YE (95) D-Xylose G. thermoglucosidans Tryp (98) D-Xylose G. Strain C5 0.5g/l YE (100) Xylooligosaccharide G.kaustophilus 10 g/l Tryp (97) Table 1-1. Literature review of Geobacillus species carbohydrate utilisation. Geobacillus is capable of growing on a wide range of carbohydrates, however, reported media contained carbon in the form of tryptone or yeast extract. 17 INTRODUCTION catabolism in G. thermoglucosidans. Several constructs were designed to test subcellular localisation of the engineered enzyme and whether its introduction allows xylan utilisation in G. thermoglucosidans. 18 MATERIALS AND METHODS 2. MATERIALS AND METHODS 2.1 Bacteria Bacteria species were Geobacillus thermodenitrificans K1041, G. thermoglucosidans DSM 2542 (formerly G. thermoglucosidasius DSM 2542), G. stearothermophilus DSM 22, G. kaustophilus DSM 7263 and Escherichia coli S17-1. G. thermodenitrificans and E. coli strains were gifts from Biosyntha, Welwyn Garden City, Hertfordshire, UK. G. thermoglucosidans, G. stearothermophilus and G. kaustophilus were purchased from the DSMZ culture collection. 2.2 Media To determine Geobacillus carbohydrate catabolism in vivo, bacteria were grown on a 90mm petri dish (Thermo Fisher Scientific, Waltham, MA, USA) containing TGPagar (tryptone 17 g l-1, peptone 3 g l-1, NaCl 5 g l-1, K2HPO4 2.5 g l-1, sodium pyruvate 4 g l-1, 0.4% (w/v) glycerol and 16 g l-1 agar). Single colonies were selected and grown overnight in 5 ml TGP-broth at 55 ˚C, with orbital shaking at 220 r.p.m. 1 ml of these cultures, which were grown at 55 ˚C, 220 r.p.m for 24-32 h, were used to inoculate 50 ml of MASM (8 mM citric acid, 5 mM MgSO4, 20 mM NaH2PO4, 10 mM K2SO4, 25 mM (NH4)2SO4, 80 μM CaCl2, 1.65 μM Na2MoO4, 1 g l-1 yeast extract, 5 ml-1 trace element solution and 160 mM MOPS). The trace element solution contained: 1.44 g l-1 ZnSO4.7H2O, 0.56 g l-1 CoSO4.6H2O, 0.25 g l-1 CuSO4.5H2O, 5.56 g l-1 FeSO4.6H2O, 0.89 g l-1 NiSO4.6H2O, 1.60 g l-1 MnSO4, 0.08 g l-1 N3BO3, 60 mM H2SO4. The OD600 was used as a surrogate for bacterial growth and was measured using a BioPhotometer (Eppendorf). For the conjugal transformation E. coli and Geobacillus were cultured in LB (tryptone 10 g l-1, yeast extract 5 g l-1 and NaCl, 5 g l-1) and mLB (tryptone 10 g l-1, yeast extract 5 g l-1 NaCl 5 g l-1, MgSO4.7H2O 0.145 g l-1, CaCl2.2H2O 0.134 g l-1, FeSO4. 7H2O 0.011 g l-1 and nitrilotriacetic acid trisodium salt 0.288 g l-1). 2.3 Plasmids For this study pS797 was used as the mobilised plasmid designed for conjugal transfer (Fig. 2-1). The plasmid was a gift from Biosyntha, Welwyn Garden City, Hertfordshire, UK. 2.4 Transformations 2.4.1 E. coli heat shock transformation E. coli S17-1 was engineered with plasmids for conjugal transfer with Geobacillus. E. coli transformation was performed using the heat shock method. 1 μl 19 MATERIALS AND METHODS Figure 2-1. Plasmid map of pS797. pS797 is a mobilisable plasmid designed for conjugal transfer, courtesy of Biosyntha Technology Ltd. The plasmid contains the Nic region and traJ gene for conjugal transfer. The plasmid also carries the repBST1 origin of replication (Geobacillus), the ColE origin of replication (E. coli), ampicillin resistance (E. coli), kanamycin resistance (Geobacillus) and the Biobrick MCS. 20 MATERIALS AND METHODS of plasmid DNA was added to the thawed E. coli competent cells. After 30 min of incubation on ice, the suspension was incubated for 30 s at 42 ˚C and returned to the ice for 2 min. 1 ml of LB was added and the culture incubated for 1 h at 37 ˚C at 220 r.p.m. 100 μl of the culture was spread on LB-agar plates containing ampicillin, 100 µg ml-1 and grown overnight at 37 ˚C. 2.4.2 Geobacillus conjugal transformation The E. coli donors were grown on LB plates containing ampicillin, 100 μg ml-1 at 37 ˚C overnight. 15 μg of a colony was collected, washed once with 1 ml of LB medium and resuspended in antibiotic-free LB. Concurrently, the recipient Geobacillus was grown in mLB-agar at 55 ˚C overnight. resuspended in the conjugal mix. 3 μg’s of Geobacillus colonies was The conjugal mix was dispensed onto LB-agar plates in 10 µl aliquots, which were allowed to dry before incubation at 37 ˚C for 6-7 h. Following incubation colonies were resuspended in 1 ml LB. 10-1 and 10-2 dilutions were made in LB and 200 µl aliquots of each were spread on mLB-agar plates containing kanamycin, 12µg ml-1. Plates were incubated at 55 ˚C for 48 h isolating kanamycin-resistant Geobacillus transformants. 2.5 Genome analysis The genome assemblies were performed by Thomas Lux, the bioinformatics specialist in the Love Laboratory. The genomes of the strains of G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus and G.kaustophilus used in this project were sequenced at the Exeter University Next Generation Sequencing Facility, using the Illumina HiSEQ or MiSEQ platforms and resulted in theoretical genome coverage over 500-fold for each genome. The ensuing sequences were assembled de novo and annotated with reference to the previously sequenced Geobacillus genomes present at that time in the NCBI Genbank database: G. thermodenitrificans NG80-2 (NC_009328), G. thermoglucosidasius C56 YS93 (NC_015660), G. kaustophilus HTA426 (NC_006510), G. thermoleovorans CCB US3 UF5 (NC_016593), Geobacillus C56 T3 (NC_014206), Geobacillus HH01 (NC_020210), Geobacillus JF8 (NC_022080), Geobacillus WCH70 (NC_012793), Geobacillus Y412MC52 (NC_014915), Geobacillus Y412MC61 (NC_013411), Geobacillus Y4 1MC1 (NC_014650). To construct the Geobacillus phylogenetic tree, the Geobacillus pangenome (i.e. all the genes in all of the genomes) was determined using the sequence clustering algorithms: OrthoMCL (OMCL), COGtriangles (COG), and the bidirectional best hit (BDBH). Phylogenetic alignments were performed using MUSCLE software. 21 MATERIALS AND METHODS Conserved positions were located with Gblocks software and PhyML software running an approximate likelihood-ratio test (aLRT) algorithm (103). 2.6 Data analysis Data was processed using Graphpad Prism v6.0 for mac (GraphPad Software, San Diego, USA). Nonlinear regression was used to generate bacterial growth curves using the sigmoidal model, namely a “one-site, specific binding with Hill slope” equation. This is the simplest model that most accurately fits the data. 22 RESULTS 3. RESULTS 3.1 In silico analysis of carbohydrate catabolic potential in Geobacillus 3.1.1 Phylogeny of the Geobacillus genus and selection of representative species A phylogenetic tree of the Geobacillus genus was constructed using the available genomes of all the fully sequenced Geobacillus retrieved from the National Center for Biotechnology Information (NCBI) database. The resulting tree (Fig. 3-1) shows the predominance of 3 clades containing between 3 and 5 different species, and 4 offshoots from the main branch, each containing only 1 species. We therefore selected, as representative examples of the genus, four Geobacillus species: G. kaustophilus (Gkt; representative of clade A), G. thermodenitrificans (Gtn; representative of clade B), G. thermoglucosidans (Gth; representative of clade C) and G. stereothermophilus (Gst; representative of a single offshoot). 3.1.2 Identification and mapping of carbohydrate catabolic enzymes The NCBI and Kyoto Encyclopaedia of Genes and Genomes (KEGG) databases were screened for the enzymes for carbohydrate catabolism in the four selected Geobacillus (Gtn, Gth, Gst and Gkt) by comparing protein sequences. Sequences assigned putative and hypothetic functions were inspected manually through searches against PFAM and PROSITE databases. Putative metabolic pathways were analysed by Metacyc and KEGG databases. In the four selected Geobacillus, as in bacteria generally, carbohydrate catabolism feeds into the glycolytic pathway (Fig 3-2) that results in the production of pyruvate, which is ultimately catabolised to lactic acid, acetic acid, acetylaldehyde and ethanol, depending on the O2 status of the medium. Although glycerol is not a carbohydrate, it is the carbon source for Geobacillus growth that is most referred to in the literature and was therefore deemed an appropriate substrate with which to start this investigation. Glycerol catabolism followed the phosphorylation pathway, which involved glycerol phosphorylation by glycerol kinase (EC 2.7.1.30) to generate glycerol-3-phosphate, which in turn is dehydrogenated by glycerol-3-phosphate dehydrogenase (EC 1.1.1.8), yielding NADH and dihydroxyacetone phosphate, which is finally converted by triose phosphoisomerase (EC 5.3.1.1) to glyceraldehyde-3-phosphate and enters the glycolytic cycle (Table. 3-1). Genes encoding the enzymes for glycerol catabolism to glyceraldehyde-3-phosphate are predicted in the genomes of the four Geobacillus species investigated. 23 RESULTS Figure 3-1. Phylogenetic tree based on the predicted pangenome of all selected Geobacilli. The tree, courtesy of Dr. Thomas Lux, highlights three clades and 4 offshoots from the main branch. To provide a full sample of the Geobacillus genus four representative examples thermodenitrificans (clade were B), selected; G. G. kaustophilus thermoglucosidans (clade (clade C) A), G. and G. stearothermophilus (offshoot D). 24 RESULTS Figure 3-2. Glycolysis pathway map. Green rectangles: Enzymes of the glycolytic pathway that are predicted in the genome of the four Geobacillus species investigated; White rectangle: other proteins not predicted in Geobacillus genome. The carbohydrate catabolism of Geobacillus feeds into glycolysis generating lacate, acetate, acetaldehyde and ethanol. Illustration of complete molecular pathway was generated using the KEGG PATHWAY software and are used with permission (http://www.genome.jp/kegg/kegg1.html). 25 RESULTS Genbank Accession Number Enzyme EC Number Glycerol kinase 2.7.1.30 YP_001125333.1 YP_004588513.1 EZP78188.1 YP_147213.1 N Glycerol-3phosphate dehydrogenase 1.1.1.94 YP_001126250.1 YP_004587515.1 EZP75923.1 YP_148073.1 N Triose phosphoisomerase 5.3.1.1 YP_001127095.1 YP_004586562.1 EZP74972.1 YP_148909.1 N Gtn Gth Gst SignalP Gkt Table 3-1. Enzymes involved in the catabolism of glycerol to glyceraldehyde-3phosphate in Geobacillus. The enzymes predicted in the genomes of G. thermodenitrificans (Gtn), G. thermoglucosidans (Gth), G. stearothermophilus (Gst) and G. kaustophilus (Gkt), which are involved in the catabolism of glycerol to glyceraldehyde-3-phosphate. 26 RESULTS Lignocellulose is a composite material containing both the C6 and C5 polysaccharides cellulose and xylan (Fig. 1-2, Fig. 1-3). During saccharification, cellulose is degraded to the monosaccharide glucose via the disaccharide cellobiose, and xylan is degraded to the monosaccharides arabinose and xylose. Cellulose degradation can be catalysed via two pathways both of which require the synergy of multiple enzymes, (Fig. 1-2). Genes coding for the catabolism of cellulose to glucose are predicted in the genomes of all four Geobacillus species investigated (Table 3-2). Cellulose is catabolised by endoglucanase (EC 3.2.1.4) to randomly generate cellulose oligosaccharides, cellobiose and glucose. The cellulose oligosaccharides then undergo continuous hydrolysis catalysed by α-glucosidase (EC 3.2.1.20), which releases glucose units until the oligomer has been catabolised to cellobiose, which in turn is hydrolysed by β-glucosidase to 2 glucose units. Subsequently, glucose feeds into the glycolytic pathway. The genomes of all four Geobacillus species contain multiple genes coding for xylanase degrading enzymes capable of catabolising xylan to xylose (Table 3-3). Xylan is catabolised into varied length xylooligosaccharides by endo-1,4-β-xylanase (EC 3.2.1.8), which is consecutively degraded into xylose units by xylan 1,4-βxylosidase (EC 3.2.1.37). Xylose catabolism followed the isomerase pathway where xylose is converted by xylose isomerase (EC 5.3.1.5) to D-xylulose that is successively phosphorylated by xylose kinase (EC 2.7.1.17) to generate D-xylulose-5-phosphate. D-xylulose-5-phosphate, an intermediate of the pentose phosphate pathway, is then metabolised by transketolase (EC 2.2.1.1) yielding glyceraldehyde-3-phosphate, which can feed into glycolysis. The backbone of xylan is commonly decorated with arabinose substituents. Arabinose is catabolised via the isomerisation of L-arabinose to L-ribulose, which is catalysed by L-arabinose isomerase (EC 5.3.1.4). L-ribulose is then phosphorylated by ribulokinase (EC 2.7.1.16) generating L-ribulose-5-phosphate, which in turn is catabolised by L-ribulose-5-phosphate 4-epimerase (EC 5.1.3.4) producing D-xylulose5-phosphate, which is then metabolised by transketolase (EC 2.2.1.1) yielding glyceraldehyde-3-phosphate, which can feed into glycolysis. Genes encoding the enzymes for arabinose catabolism to glyceraldehyde-3-phosphate are predicted in the genomes of the four Geobacillus species investigated (Table 3-4). 3.2 Formulation of minimal growth media for Geobacillus. 3.2.1 Geobacillus growth is sustained by tryptone and peptone To investigate Geobacillus carbohydrate catabolism in vivo, we initially cultured G. thermodenitrificans in tryptone-peptone-pyruvate-glycerol (TGP) medium, as 27 RESULTS Genbank Accession Number Enzyme EC Number Endoglucanase 3.2.1.4 Gtn Gth Gst SignalP Gkt YP_001126727.1 YP_004587002.1 EZP76424.1 YP_148566.1 N α-glucosidase 3.2.1.20 YP_001124655.1 YP_004589171.1 EZP78655.1 YP_146468.1 N β-glucosidase 3.2.1.21 YP_001126360.1 YP_148190.1 N β-glucosidase 3.2.1.21 YP_001125856 YP_004588242 YP_147709.1 N β-glucosidase 3.2.1.21 YP_001127225 YP_004586372 EZP75177.1 YP_149067.1 N Table 3-2. Enzymes involved in the catabolism of cellulose to glucose in Geobacillus. The enzymes predicted in the genomes of G. thermodenitrificans (Gtn), G. thermoglucosidans (Gth), G. stearothermophilus (Gst) and G. kaustophilus (Gkt), which are involved in the catabolic pathway for the degrade cellulose to glucose. 28 RESULTS Enzyme EC Number Endo-1,4-βxylanase 3.2.1.8 Endo-1,4-βxylanase Genbank Accession Number Gtn Gth SignalP Gst Gkt YP_001125870.2 YP_004588260.1 ABI49951.1 WP_020279794 Y 3.2.1.8 YP_001125883.1 YP_004588273.1 2Q8X_A WP_020279011 N Xylan 1,4-βxylosidase 3.2.1.37 YP_001125867.1 ABI49959.1 WP_020279302 N Xylan 1,4-βxylosidase 3.2.1.37 YP_001125878.1 YP_004588268.1 ABI49941.1 WP_020279006 N Xylan 1,4-βxylosidase 3.2.1.37 YP_001125884.1 YP_004588274.1 ABI49956.1 WP_020279012 N Acetylxylan esterase 3.2.1.72 YP_001125885.1 YP_004588275.1 ABI49936.1 GAD13923 N Xylan α-1,23.2.1.131 glucuronosidase Q09LY5 N Xylose isomerase Xylose kinase 5.3.1.5 YP_001125866.1 YP_004588257.1 ABI49955.1 YP_147728.1 N 2.7.1.17 YP_001125865.1 YP_004588256.1 ABI49954.1 YP_147727.1 N Transketolase 2.2.1.1 YP_001125304.1 YP_004588539.1 EZP78159.1/ YP_147185.1 N Table 3-3. Enzymes involved in the catabolism of xylan to glyeraldehyde-3phosphate in Geobacillus. The enzymes predicted in the genomes of G. thermodenitrificans (Gtn), G. thermoglucosidans (Gth), G. stearothermophilus (Gst) and G. kaustophilus (Gkt) that function to degrade xylan to glyceroaldehyde-3phophate. 29 RESULTS Enzyme EC Number Genbank Accession Number SignalP Gtn Gth Gst Gkt YP_001125900.1 GAJ44956.1 Q9S467.2 YP_147757.1 N Ribulokinase 2.7.1.16 YP_001125901.1 GAJ44957.1 Q9S468.1 YP_147758.1 L-ribulose-5phosphate 4- 5.1.3.4. YP_001125902.1 GAJ44958.1 Q9S469.1 YP_147759.1 epimerase Transketolase 2.2.1.1 YP_001125304.1 YP_004588539.1 EZP78159.1 YP_147185.1 N L-arabinose isomerase 5.3.1.4 Table 3-4. Enzymes involved in the catabolism of arabinose to glyeraldehyde-3phosphate in Geobacillus. The enzymes predicted in the genomes of G. thermodenitrificans (Gtn), G. thermoglucosidans (Gth), G. stearothermophilus (Gst) and G. kaustophilus (Gkt), which have the potential to degrade arabinose to glyceroaldehyde-3-phophate. 30 N N RESULTS recommended by our industrial partner Biosyntha. Growth was monitored by optical density at 600 nm (OD600). Following inoculation and a lag phase of approximately 2 h, G. thermodenitrificans grew exponentially for 6 h to an OD600 of 2.5, when a drastic reduction in OD600 was observed. In the absence of glycerol, the bacteria grew as observed previously with glycerol for 6 h, but no decrease in OD600 was observed, and the culture attained a final OD600 of 5 after 24 h (Fig 3-3). To determine which of the remaining medium constituents was able to sustain microbial growth, a series of growth experiments in media containing all combinations of tryptone, peptone or pyruvate was performed (Fig. 3-4). G. thermodenitrificans did not grow at all in media containing only 4 g l-1 of sodium pyruvate. G. thermodenitrificans grew poorly (Maximal OD600 ≈ 0.5) in media containing peptone and pyruvate, but well in media containing tryptone and pyruvate (Maximal OD600 ≈ 5). It therefore appeared that pyruvate does not sustain Geobacillus growth, but that tryptone, and to a lesser extent, peptone do. However, these experiments were performed according to the original TGP formulation that contains 17 g l-1 of tryptone compared to only 3 g l-1 of peptone. When equal concentrations of tryptone or peptone were used in the medium, G. thermodenitrificans grew equally well (Fig. 3-5). As the concentration of tryptone or peptone was reduced, bacterial growth decreased. At 0.75 g l-1 tryptone or peptone, the maximum OD600 was approximately 0.5. Using the OD600 0.5 as a basal level of growth, G. thermodenitrficans was grown in 0.75 g l-1 of tryptone and/ or peptone supplemented with either 4 g l-1 of glycerol or glucose (Fig 3-6). In each case the addition of glycerol or glucose to tryptone, peptone or tryptone and peptone did not allow G. thermodenitrificans to grow to an OD600 greater than basal level of the no carbon control (≈ 0.5), therefore preventing analysis of the bacterial growth on these carbon sources. While these experiments were being performed, Biosyntha contacted us with a new “minimal medium” formulation, labelled ASM. As we were interested in carbohydrate metabolism, not in formulating a new minimal medium for Geobacillus, we transferred to ASM. 3.2.2 Geobacillus growth in ASM medium and formulation of a new minimal medium ASM medium contains (8 mM citric acid, 5 mM MgSO4, 20 mM NaH2PO4, 10 mM K2SO4, 25 mM (NH4)2SO4, 80 μM CaCl2, 1.65 μM Na2MoO4, 1 g l-1 yeast extract, 5 ml-1 trace element solution. The Trace element solution contained: 1.44 g l-1 ZnSO4.7H2O, 0.56 g l-1 CoSO4.6H2O, 0.25 g l-1 CuSO4.5H2O, 5.56 g l-1 FeSO4.6H2O, 0.89 g l-1 NiSO4.6H2O, 1.60 g l-1 MnSO4, 0.08 g l-1 N3BO3, and 60 mM H2SO4). To compare base line growth of G. thermodenitrificans in TGP and ASM the OD600 was monitored over 24 h without supplementation of any additional carbon substrate (Fig. 3-7). Following 31 RESULTS Figure 3-3. Growth of G. thermodenitrificans in TGP media. G. thermodenitrificans was grown in TGP (black circles), which contained the full complement of components, and TGP (No C.S) (white circles), which did not contain the added carbon source glycerol, therefore considered a no carbon source control. G. thermodenitrificans grown in the presence of glycerol showed lower levels of growth compared to cultures grown in the absence of glycerol. Data from the growth of G. thermodenitrificans in TGP media was fitted using the one site – specific binding with Hill slope equation (solid line), while the data collected from point of aggregation was fitted using a connecting line (dashed line). The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 32 Bacterial Growth (OD600) RESULTS 7 TPPy* T*Py* *PPy* T*** *P** **Py* 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 Time (h) Figure 3-4. Growth of G. thermodenitrificans in variations of TGP media. G. thermodenitrificans was grown in media containing variations of tryptone, peptone and sodium pyruvate; TPPy* (tryptone, peptone and sodium pyruvate), T*Py* (tryptone and sodium pyruvate), *PPy* (peptone and sodium pyruvate), T*** (tryptone), *P** (peptone) and **Py* (sodium pyruvate); to determine which of the constituents was able to support growth. The data demonstrated sodium pyruvate was not able to sustain G. thermodenitrificans growth, however, the inclusion of tryptone was sufficient for growth, and to a lesser extent peptone too. Data from the growth of G. thermodenitrificans was fitted using the one site – specific binding with Hill slope equation. The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 33 RESULTS Bacterial Growth (OD600) A 7 17 gl-1 13.4 gl-1 10.2 gl-1 6.8 gl-1 3.4 gl-1 1.7 gl-1 0.75 gl-1 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 20 24 28 Time (h) Bacterial Growth (OD600) B 7 6 5 4 3 2 1 0 0 4 8 12 16 Time (h) Figure 3-5. Growth of G. thermodenitrificans in a range of tryptone and peptone concentrations. G. thermodenitrificans was grown in 17, 13.4, 10.2, 6.8, 3.4, 1.7 and 0.75 gl-1 of tryptone (A) and peptone (B). G. thermodenitrificans grew equally well in both tryptone (A) and peptone (B) with the final OD600 being directly related to their concentration. Data from the growth of G. thermodenitrificans was fitted to the one site – specific binding with Hill slope equation. The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 34 RESULTS Figure. 3-6. G. thermodenitrificans growth in a minimal tryptone or peptone concentration supplemented with glucose or glycerol. -1 G. thermodenitrificans -1 grown in (A) 0.75 g l tryptone supplemented with 4 g l glucose or glycerol grew to a similar OD600 as the no carbon source base line ~ 0.5, where no carbon source is taken as no added glucose or glycerol to the minimal tryptone concentration. When cultured in (B) 0. 75 g l-1 peptone supplemented with 4 g l-1 glucose or glycerol G. thermodenitrificans grew to a similar final OD600 as the no carbon basal level of growth, where no carbon source is taken as no added glucose or glycerol to the minimal peptone concentration. Culturing G. thermodenitrificans in (C) 0.75 g l-1 both tryptone and peptone supplemented with 4 g l-1 glucose or glycerol bacterial growth entered stationary phase at a lower OD600 than the no carbon control, where no carbon source is taken as no added glucose or glycerol to the minimal tryptone and peptone. Data from the growth of G. thermodenitrificans was fitted to the one site – specific binding with Hill slope equation. The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 35 RESULTS A Bacterial Growth (OD600) 7 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 Time (h) Bacterial Growth (OD600) B 8 7 6 7 5 4 6 pH 3 2 5 1 0 0 4 8 12 16 20 24 28 4 Time (h) Figure 3-7. Growth of G. thermodenitrificans in TGP and ASM media. (A) G. thermodenitrificans grew to a higher OD600 (≈ 5) in TGP (black circles) compared to ASM (white circles) (≈ 1) in the absence of any additional carbon source. (B) G. thermodenitrificans grown in ASM supplemented with glucose (black circles, grey line) demonstrated an initial fast growth rate, but a final OD600 similar to the baseline of the bacterial growth in the absence of glucose (white circles, grey line). The pH (diamond) of G. thermodenitrificians grown in the presence of glucose (black solid line) shows a rapid drop that coincides with the drop in OD600. The pH of G. thermodenitrificans grown in the absence of glucose (black dotted line) is sustained at ≈ 7 over 24 h. Data from the growth of G. thermodenitrificans was fitted using the one site – specific binding with Hill slope equation (grey solid line), while the data collected from point of aggregation was fitted using a connecting line (grey dashed line). The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 36 RESULTS inoculation and a lag phase of 2 h G. thermodenitrificans grew in both media. In TGP, G. thermodenitrificans grew exponentially for 14 h reaching a maximal OD600 ≈ 5 whereas in ASM the exponential phase lasted 4 h and the culture reached a maximal OD600 ≈ 1, therefore providing a suitably low baseline from which to monitor growth in subsequent experiments. Biosyntha routinely added 10 g l-1 of glucose to the ASM-base formulation. When G. thermodenitrificans was cultured in this richer medium, a rapid exponential growth was observed (to an OD600 ≈ 2 in 4 h), followed by a reduction in OD600 to approximately 1 after a further 2 h. This reduction in OD600 coincided with a decrease in medium pH, from 7 to 5.4; this acidification was not observed in the absence of glucose (Fig 3-7). To mitigate the acidification of the media, G. thermodenitrificans was grown in buffered ASM with 1% glucose, (Fig 3-8). The results indicate that increasing the buffering alleviate pH changes in the media (Fig. 3-9). In addition buffering slows the growth of G. thermodenitrificans and delays aggregation of the culture. The buffering of ASM-1%Gluc results in a higher cell density. However, in all instances aggregation still occurred by 12 h. Consequently to determine carbon utilisation we used a re-formulated ASM. This medium, termed MASM, was ASM containing 160 mM MOPS added as a buffering system. 3.3 In vivo analysis of carbohydrate metabolism in representative Geobacillus The carbohydrate catabolism of G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus and G. kaustophilus was investigated by monitoring growth in MASM supplemented with glycerol (C3H8O3), glucose (C6H12O6), cellobiose (C6H12O11), cellulose ([C6H12O6]n), xylose (C5H10O5), arabinose (C5H10O5) and xylan ([C5H8O4R]n). Glycerol was chosen because it is the main carbon source for Geobacillus growth in the literature. Moreover, glycerol is the principal by-product of triacylglyceride hydrolysis (i.e. the production biodiesel) and therefore plentiful in the waste stream of the first generation biodiesel industry. The other compounds were selected because they represent the main products of lignocellulose acid hydrolysis. 3.3.1 Controls: Geobacillus growth without carbohydrate addition or in glycerol. All four Geobacillus species grew very little when incubated in MASM without any addition of the carbohydrate glycerol, thereby providing a low baseline (maximal OD600 ≈ 1) from which to monitor growth in subsequent experiments (Fig 3-10). When MASM was supplemented with 10 g l-1 of glycerol, G. thermodenitrificans, G. thermoglucosidans and G. stearothermophilus grew to a final OD600 of approximately 4.5, 3.5, and 3.5, respectively. The growth kinetic between these three species was 37 Bacterial Growth (OD600) RESULTS 7 320 mM 240 mM 160 mM 80 mM 60 mM 40 mM 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 Time (h) Figure 3-8. Growth of G. thermodenitrificans in ASM buffered with a range of MOPS concentrations. Increasing the concentration of MOPS slows the growth rate of G. thermodenitrificans, delays aggregation and allows growth to a higher OD600. Data from the growth of G. thermodenitrificans media was fit to the one site – specific binding with Hill slope equation (solid line), while the data collected from the point of aggregation was fitted using a connecting line (dashed line). The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 38 RESULTS 7 pH 6 4 6 2 5 32 0 24 0 16 0 80 60 40 0 0 Bacterial Growth (OD600) OD.600 at Time of Aggregation pH at end point (24h) pH at Aggregation [mM MOPS] Figure 3-9. pH and bacterial growth of G. thermodenitrificans in buffered ASM. Increasing the concentration of MOPS mitigates the pH changes after 24 h (black columns) and at the point of bacterial aggregation (light grey column). Increasing the buffering allows G. thermodenitrificans to grow to a higher OD600 before aggregation (dark grey column). The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 39 RESULTS Bacterial Growth (OD600) A 7 No Carbon Source 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 Time (h) Bacterial Growth (OD600) B 7 Glycerol 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 32 Time (h) Figure 3-10. Growth of four representative Geobacillus species in MASM without carbohydrate or in the presence of glycerol. G. thermodenitrificans (circles), G. thermoglucosidans (squares), G. stearothermophilus (triangle) and G. kaustophilus (inverted triangle) grown in (A) MASM without carbohydrate supplementation showed a low baseline level of growth, OD600 ≈ 1. The four species growth in (B) MASM supplemented with glycerol showed G. thermodenitrificans, G. thermoglucosidans and G. stearothermophilus growing to a higher OD600 than their respective baseline in (A), while G. kaustophilus did not reach an OD600 greater than its no carbon baseline. G. thermodenitrificans OD600 decreased at 16 h (dashed line), which was ascribed to aggregation. Data from the growth of Geobacillus species was fitted to the one site – specific binding with Hill slope equation (solid line), while the data collected from the point of aggregation was fitted using a connecting line (dashed line). The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 40 RESULTS different: G. thermodenitrificans had a lag-phase of 2 h, followed by exponential growth to 16 h after inoculation. At 16 h, however, the OD600 decreases by 50% from its peak of 5 to 2.5 (dashed line on the figure); this is ascribed to aggregation or sporulation that is documented in Geobacillus. Samples were taken from these cultures at 24 h, and prepared for Scanning Electron Microscopy, to ascertain whether aggregation or sporulation had occurred. However, fixation was not optimal and the subsequent images were of insufficient quality to illustrate either possibility. G. thermoglucosidans had a long lag-phase of approximately 12 h, followed by exponential growth to 24 h, before entering stationary phase. G. stearothermophilus had a 6 h lag phase, an exponential phase to 16 h, followed by a typical stationary phase. G. kaustophilus did not grow beyond the baseline of OD600 ≈ 1, indicating that it was unable to metabolise the glycerol in the time available (24 h). 3.3.2. Geobacillus growth with C6 saccharides G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus and G. kaustophilus all grew to an OD600 between 5 and 6.5 when cultured in MASM -1 supplemented with 10 g l of glucose or cellobiose (Fig. 3-11). The growth kinetics of each bacterial species (Table 3-5) were similar in either medium containing the mono and di-saccharide, indicating that the bacteria had the capacity to catabolise the carbohydrate provided. G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus did not enter stationary phase, as is usually understood by the terminology, but underwent a drastic reduction in OD600, which we ascribe to aggregation. Unlike the other species investigated, G. kaustophilus showed no decrease in OD600 after exponential phase, but neither did it enter stationary phase, which may have been due to its longer lag-phase. Geobacillus were cultured in MASM supplemented with cellulose. However, because cellulose is insoluble, it was not feasible to monitor growth using OD600. Instead, aliquots were harvested from the medium and plated onto TGP-agar. The number of colony forming units (cfu) on plates indicated bacterial growth in the MASM-cellulose suspension. No Geobacillus species grew with cellulose as the additional substrate (Fig. 3-12). 3.3.3. Geobacillus growth with C5 saccharides All four Geobacillus species investigated grew to an OD600 between 4.5 and 6 when cultured in MASM supplemented with 10 g l-1 of xylose or arabinose except in the case of G. kaustophilus that did not grow on arabinose (Fig. 3-13). The growth kinetics of G. thermodenitrificans, G. thermoglucosidans and G. stearothermophilus (Table 3-5) were similar in either medium supplemented with the C5 monosaccharides, excluding G. stearothermophilus, which did not enter stationary phase in the presence of xylose, but rather experienced a decrease in OD600 that was ascribed to aggregation. 41 RESULTS A Bacterial Growth (OD600) 7 Glucose 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 32 24 28 32 Time (h) Bacterial Growth (OD600) B 7 Cellobiose 6 5 4 3 2 1 0 0 4 8 12 16 20 Time (h) Figure 3-11. Growth of four representative Geobacillus species investigated in the presence of C6 saccharides. G. thermodenitrificans (circles), G. thermoglucosidans (squares), G. stearothermophilus (triangle) and G. kaustophilus (inverted triangle) grown in MASM supplemented with glucose (A) showed growth to a higher OD600 than the MASM baseline (OD600 ≈ 1), however a decrease in OD600 (dahsed line) was observed in G. thermodenitrificans, G. thermoglucosidans and G. stearothermophilus. The four species grown in MASM supplemented with cellobiose (B) grew to OD600 between 5 and 6.5. A decrease in OD600 was observed in G. thermodenitrificans, G. thermoglucosidans and G. stearothermophilus (dashed line). The decrease in OD600 was ascribed to aggregation. Data from the growth of Geobacillus species was fitted to one site – specific binding with Hill slope equation (solid line), while the data collected from the point of aggregation was fitted using a connecting line (dashed line). The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 42 RESULTS μmax (h-1) on Range of Carbon Sources Geobacillus Spp. No C.S Gtn 0.85 Gth 0.48 Gst 0.68 Gkt 0.81 Range of relative error 0.860.84 0.470.49 0.670.69 0.790.82 Glucose 0.99 0.78 0.65 0.55 Range of relative error 0.981.0 0.770.80 0.650.65 0.530.56 Cellobiose 1.02 0.82 0.58 0.62 Range of relative error 1.021.03 0.760.89 0.550.62 0.610.62 Glycerol 0.94 0.66 0.64 0.59 Range of relative error 0.940.95 0.650.68 0.63064 0.580.60 Arabinose 0.77 0.70 0.57 0.37 Range of relative error 0.750.80 0.670.73 0.560.57 0.350.39 Xylose 0.77 0.71 0.77 0.33 Range of relative error 0.730.84 0.680.74 0.750.79 0.310.35 Xylan 0.84 0.76 0.50 0.59 Range of relative error 0.760.94 0.750.77 0.420.62 0.520.63 MASMRAPT 1.05 Range of relative error 0.931.1 RAPT 0.56 Range of relative error 0.510.72 Table 3-5. Maximal specific growth rates of the four Geobacillus species investigated on a range of carbon sources. Specific growth rates (μ) were calculated using μ = ln (x2 – x1)/ (t2 – t1) for each time point, where the specific growth rate is the slope of the line, maximal specific growth rate (μmax) was then selected. Error of μmax was calculated using standard deviation, which was then applied to the specific growth rate equation to create ± values for the μmax. G. thermodenitrificans (Gtn) displayed the fastest growth rate of the four species when grown on C6 saccharides. When grown on C5 saccharides G. thermodenitrificans (Gtn), G. thermoglucosidans (Gth) and G. stearothermophilus (Gst) shared a much similar maximal specific growth rates while G. kaustophilus (Gkt) was considerably lower. 43 RESULTS A B 5×106 5×106 G. thermoglucoidans G. thermodenitrificans 4×106 CFU per ml CFU per ml 4×106 3×106 2×106 1 2 3 4 5 Time (days) 6 0 7 C 2 3 4 5 6 7 6 7 D G. stearothermophilus CFU per ml 4×106 CFU per ml 1 Time (days) 5×106 3×106 2×106 1×106 0 2×106 1×106 1×106 0 3×106 1 2 3 4 5 6 7 Time (days) 2.0×107 1.8×107 1.6×107 1.4×107 1.2×107 1.0×107 2.0×106 1.5×106 1.0×106 5.0×105 0.0 G. kaustophilus 1 2 3 4 5 Time (days) Figure 3-12. Growth of Geobacillus in MASM supplemented with microcrystalline cellulose (avicel). No Geobacillus species investigated grew to a higher cell density in the presence of cellulose (grey column) compared to its absence (black column) over 7 days. The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 44 RESULTS B 7 Bacterial Growth (OD600) Bacterial Growth (OD600) A Xylose 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 7 Arabinose 6 5 4 3 2 1 0 0 32 4 8 12 16 20 24 Time (h) Time (h) Bacterial Growth (OD600) C 7 Xylan 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 Time (h) Figure 3-13. Growth of Geobacillus in the presence of C5 saccharides. G. thermodenitrificans (circles), G. thermoglucosidans (squares), G. stearothermophilus (triangle) and G. kaustophilus (inverted triangle) cultured in MASM supplemented with xylose (A) grew to OD600 between 4.5 and 6.5, however, a decrease in OD600 was observed in G. thermodenitrificans (dashed line), which was ascribed to aggregation. (B) G. thermodenitrificans, G. thermoglucosidans and G. stearothermophilus grew in MASM supplemented with arabinose, however G. kaustophilus grew to a similar OD600 as the baseline for MASM (OD600 ≈ 1) indicating it cannot catabolise the C5 monosaccharide. (C) G. thermodenitrificans grew in the presence of xylan, while G. thermoglucosidans, G. stearothermophilus and G. kaustophilus grew to a similar OD600 as the baseline for MASM (OD600 ≈ 1) suggesting they cannot catabolise the polysaccharide. Data from the growth of Geobacillus species was fitted to the one site – specific binding with Hill slope equation (solid line), while the data collected from the point of aggregation was fitted using a connecting line (dashed line). The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 45 28 RESULTS G. kaustophilus had a lag-phase of 14 h, followed by exponential growth to 28 h before entering stationary phase when grown in the presence of xylose. These results indicate xylose can be catabolised by all four species investigated and arabinose by G. thermodenitrificans, G. thermoglucosidans and G. stearothermophilus. G. kaustophilus did not grow beyond the baseline of OD600 ≈ 1 in the presence of arabinose, indicating that it was unable to metabolise the C5 carbohydrate in the time available (24 h). Geobacillus were cultured in MASM supplemented with 10 g l-1 of xylan. G. thermodenitrificans grew to a final OD600 ≈ 5.5. G. thermodenitrificans had a lag-phase of 2 h, followed by exponential growth to 16 h after inoculation, before entering stationary phase. G. thermoglucosidans, G. stearothermophilus and G. kaustophilus did not grow beyond the baseline of OD600 ≈ 1 when cultured in xylan, indicating they were unable to metabolise the polysaccharide in the time available (24 h). 3.3.4. Geobacillus growth in hydrotreated lignocellulose (RAPT) Hydrotreated lignocellulose is a complex mix of C5 and C6 saccharides with varying levels of polymerization. To determine whether Geobacillus could grow in hydrotreated lignocellulose, G. thermodenitrificans was cultured in MASM, water or 160 mM MOPS, each supplemented with 10 ml l-1 of an industrial hydrotreated lignocellulose termed “RAPT” (Fig 3-14). RAPT is produced by Shell and the method of production is proprietary. G. thermodenitrificans grew in MASM supplemented with 10 ml l-1 of RAPT. After inoculation and a 4 h lag phase Geobacillus grew to an OD600 of ≈ 3.5. Following this, water supplemented with 10 ml l-1 of RAPT was used as a medium, however, incubating RAPT at 55 ˚C increased the rate of acid hydrolysis in the pre-treated RAPT and therefore acidified the media preventing G. thermodenitrificans growth. To overcome acidification, 160 mM MOPS was added as a buffering system. In the buffered media G. thermodenitrificans grew to an OD600 of ≈ 7. The growth kinetics of G. thermodenitrficans (Table 3-5) showed a lag phase of 6 h and an exponential phase of 10 h before reaching a typical stationary phase 16 h after inoculation, indicating that the bacteria had the capacity to grow solely on pre-treated lignocellulosic biomass. 3.4 Engineering xylan catabolism in Geobacillus thermoglucosidans G. thermoglucosidans, G. stearothermophilus and G. kaustophilus displayed no growth in the presence of cellulose or xylan as carbon sources, but were able to grow on the simpler saccharides, cellobiose, glucose, xylose and arabinose. Conversely, G. thermodenitrificans grew well on xylan, but not on cellulose. A genomic comparison between the four Geobacillus species revealed that G. thermodenitrificans, G. stearothermophilus and G. kaustophilus possess all the genes 46 RESULTS Bacterial Growth (OD600) 8 MASM-RAPT RAPT RAPT-MOPS 7 6 5 4 3 2 1 0 0 4 8 12 16 20 24 28 Time (h) Figure 3-14. Growth of G. thermodenitrificans in the presence of hydrotreated lignocellulose “RAPT”. G. thermodenitrificans was capable of growing in MASM supplemented with RAPT (black line), but not RAPT alone (dark grey line) unless it had been buffered with MOPS (light grey line) where the bacteria reached an OD 600 of ≈ 7. Data from the growth of G. thermodenitrificans was fitted using the one site – specific binding with Hill slope equation. The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 47 RESULTS to encode the enzymatic pathway for xylan degradation; it therefore appears that the absence of xylan catabolism in G. stearothermophilus and G. kaustophilus is not due to the lack of pathway competence, but possibly due to the enzymes not being expressed. However, time constraints did not allow the investigation of that hypothesis. In contrast, the molecular pathway for xylan catabolism in G. thermoglucosidans lacks a gene encoding the xylan 1-4-β-xylosidase enzyme. In G. thermodenitrificans, that enzyme is encoded by the xynB open reading frame (accession number YP_001125867.1). We therefore proposed that the incomplete xylan catabolic pathway in G. thermoglucosidans might be complemented by the G. thermodenitrificans xynB coding sequence (Gtn xynB) and confer xylan catabolic activity to the engineered G. thermoglucosidans. 3.4.1 Plasmid constructs and transformation To transform Gtn xynB into G. thermoglucosidans, three plasmid constructs were generated. The plasmid backbone was from pS797 and the DNA fragments were synthesized by DNA2.0. For all constructs, the gene terminator was the pS718 fragment, which is a synthetic stem-loop terminator derived from the plasmids pS797. pXYNB (Fig. 3-15) contains the coding sequence of Gtn xynB with 100 base-pairs upstream of the ATG start codon, which we assumed represented the native promoter. In pPldhA::XYNB (Fig. 3-15), the 100 base-pairs upstream of the Gtn xynB coding sequence (PxynB) was replaced by the promoter sequence of the constitutively expressed ldhA gene from G. thermodenitrificans. Due to its function as a xylanase, and given the fact that xylan can probably not diffuse into bacterial cells, we hypothesized that Gtn xynB may be an extracellular enzyme. We therefore performed a SignalP 4.1 (CBS) scan on the primary amino-acid (AA) sequence (535 AA) of Gtn xynB. This scan revealed no obvious putative export signal. Typically, peptide export signals are 20-40 AA in length (99). We therefore fused the coding sequence for the 70 AA from the amino-terminus of Gtn xynB to the 5´ terminus of the SUPERFOLDER GREEN FLUORESCENT PROTEIN (sGFP; 104) coding sequence. sGFP is a heat tolerant variety of GFP and used as a fluorescent reporter in thermophilic bacteria. The fusion construct was located downstream of PxynB, and the resulting plasmid termed pXYNB70::sGFP (Fig. 3-16). Following conjugation with E. coli transformant strains, each carrying one of the three plasmids, and plating onto selective agar medium (TGP-agar with 12.5 µg ml-1 kanamycin), 12 G. thermoglucosidans colonies were retrieved for each construct. These colonies were then streaked onto selective plates, twice. A single colony out of the 12 was selected, transferred to 5 ml liquid TGP and incubated overnight. 1 ml of the bacterial suspensions from these cultures were transferred to 50 ml MASM 48 RESULTS Biobrick prefix Biobrick suffix PxynB promoter xynB pS718 terminator pXYNB Biobrick prefix Biobrick suffix ldhA promoter xynB pPldhA::XYNB pS718 terminator Figure 3-15. Plasmid constructs for G. thermoglucosidans xylan catabolism. Both plasmid constructs designed use the pS797 plasmid backbone and contain the coding sequence of Gtn xynB, and the pS718 gene terminator. pXYNB contains the 100 base-pair upstream coding sequence of xynB, which we assumed represented the native promoter, while pPldhA::XYNB contains the promoter sequence for the constitutively expressed ldhA gene from G. thermodenitrificans. 49 RESULTS Biobrick prefix Biobrick suffix PxynB promoter xynB 70 pXYNB70::sGFP sGFP pS718 terminator Figure 3-16. Plasmid construct for Gtn xynB cellular localization. The construct pXYNB70::sGFP contains the native promoter PxynB which drives expression of the 70 AA amino-terminus of Gtn xynB fused to 5´ terminus of the SUPERFOLDER GREEN FLUORESCENT PROTEIN (sGFP) coding sequence. The pS718 fragment is used as a gene terminator and the construct uses the pS797 backbone. 50 RESULTS supplemented with 10 g l-1 xylan and growth monitored. 3.4.2 Growth of Geobacillus thermoglucosidans engineered with xylanase Growth of the engineered G. thermoglucosidans was monitored by OD600. G. thermoglucosidans engineered with pXYNB grew no better than the wild-type bacterium in the presence or absence of xylan (Fig. 3-17), indicating that this strain was unable to catabolise xylan. G. thermoglucosidans engineered with pPldhA::XYNB appeared to have a shorter lag-phase than the wild-type, but the final OD600 and µmax (0.38 h-1) for the transformant was no greater than of the wild-type (Fig. 3-18, Table. 35). These data are therefore ambiguous, but it appears that xylan cannot sustain the growth of the engineered G. thermoglucosidans. However, due to time constraints, we were unable to perform important aspects of this series of experiments, notably transformation with the actual Gtn xynB sequences, as opposed to the presence of a functioning selectable marker, was not confirmed, and only one transformant colony per transformation was screened for growth in the presence of xylan. 3.4.3 Gtn xynB contains an active extracellular export signal G. thermoglucosidans engineered with pXYNB70::sGFP was grown in MASM supplemented with 10 g l-1 glucose, xylose or xylan. Bacteria grew in the presence of glucose and xylose but not in the presence of xylan. Following centrifugation, sGFP fluorescence was observed in the supernatant medium, but not in the cell pellet of cultures grown in the presence of glucose but not in the presence of xylose or xylan (Fig. 3-19). Consequently, it appears that the 70 AA N-terminus of Gtn xynB does indeed contain a signal sequence for the export of the protein from the bacterial cytosol. 51 Bacterial Growth (OD600) RESULTS 3 Gth pXYNB Gth WT Gth WT (No Xylan) 2 1 0 0 4 8 12 16 20 24 28 Time (h) Figure 3-17. Growth of G. thermoglucosidans engineered with pXYNB. G. thermoglucosidans (Gth) engineered with pXYNB and grown in MASM supplemented with xylan (black line) grew to no greater OD600 than the WT G. thermoglucosidans grown in MASM (dotted line) or MASM supplemented with xylan (grey line). Data from the growth of G. thermoglucosidans was fitted to one site – specific binding with Hill slope equation. The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 52 Bacterial Growth (OD600) RESULTS 3 Gth pPldhA::XYNB Gth WT Gth WT (No Xylan) 2 1 0 0 4 8 12 16 20 24 28 Time (h) Figure 3-18. Growth of G. thermoglucosidans engineered with pPldhA::XYNB. G. thermoglucosidans (Gth) engineered with pPldhA::XYNB and grown in MASM supplemented with xylan (black line) grew to no greater OD600 than the WT G. thermoglucosidans grown in MASM (dotted line) or MASM supplemented with xylan (grey line). Data from the growth of G. thermoglucosidans was fitted to one site – specific binding with Hill slope equation. The error bars shown represent the standard deviation at 95% confidence intervals using 4 degrees of freedom. 53 RESULTS Figure 3-19. Expression of sGFP in G. thermoglucosidans engineered with pXYNB70::sGFP. G. thermoglucosidans was grown for 24 h in MASM without carbohydrate supplementation (No C.S.) or in the presence of either glucose, xylose or xylan. After 24 h the cultures were pelleted by centrifugation and sGFP fluorescence was observed under UV light. The expression of sGFP was observed in the supernatant of cultures as opposed to the pellet therefore suggesting the presence of a signal sequence. When G. thermoglucosidans was grown in the presence of glucose a high level of GFP expression was observed, but not in the presence of xylose or xylan. However, this is qualitative data as cultures were only observed under UV light and further analysis is therefore required for quantifiable data. 54 DISCUSSION 4. DISCUSSION This investigation examined the input pathways for a range of mono-, di- and poly- saccharides in four representative examples of the Geobacillus genus: G. thermodenitrificans, G. thermoglucosidans, G. stearothermophilus and G. kaustophilus. 4.1.1 Catabolism of carbohydrates in the Geobacillus genus In previous reports, species of the genus Geobacillus have attracted a lot of attention with their ability to grow on a wide range of C5 and C6 saccharides at high temperatures (105). Having developed MASM to mitigate acidification and delay aggregation of Geobacillus we were able to monitor bacterial growth on a range of these carbohydrates. Our studies of the four Geobacillus species support these findings having demonstrated growth on glycerol (excluding G. kaustophilus), glucose, cellobiose, xylose and arabinose (excluding G. kaustophilus), which typically compose the pre-treated lignocellulosic hydrolysate “RAPT”. G. thermodenitrificans was capable of using “RAPT” as the sole source of carbon for its growth. The catabolism of cellulose and xylan, the carbohydrate components of lignocellulose, were also investigated. In agreement with recent studies we found that the four Geobacillus species investigated were predicted to contain a number of cellulose and xylan degrading genes (17, 84, 106), however when cultured in xylan, only G. thermodenitrificans could grow. Moreover, none of the four species was capable of growing on cellulose. These findings add to current reports of cellulase and xylanase activity by demonstrating that natively produced cellulases and xylanases are largely incapable of supporting growth. The lack of growth on these polysaccharides could be linked to reports of low lignocellulosic enzyme activity in Geobacillus species (21, 30, 96). It was therefore hypothesised that cellulases and xylanases were being produced but expressing a very low activity that is not capable of supporting bacterial growth, hence, not sufficient for the industrial application of bioprocessing lignocellulose to biofuel (106). Certain species of the genus Geobacillus are able to ferment mono- and disaccharides, making it a strong candidate for a microbial chassis that can produce biofuels from glycerol and pre-treated lignocellulosic biomass. However, the direct conversion of untreated lignocellulose to biofuel is hypothesised to be a more economical and sustainable bioprocess. Currently Geobacillus does not have the catabolic potential to degrade cellulose and xylan at a rate to support its own growth, therefore additional engineering will be required if its to be used as a chassis for onestep consolidated bioprocessing. 55 DISCUSSION 4.2.1 Transgene expression To improve the input pathway of the Geobacillus genus we attempted to engineer G. thermoglucosidans to grow on xylan. G. thermoglucosidans lacked a xylan 1-4-βxylosidase predicted in G. thermodenitrificans genome, which suggested an incomplete xylan catabolic pathway. It was hypothesised that engineering the enzyme Gtn xynB would complete the pathway and allow G. thermoglucosidans to catabolise xylan. Engineering this gene into G. thermoglucosidans required successful transfection of plasmid DNA. (105). Limited strains of Geobacillus have successfully been transformed In most cases highly specialised and time consuming methods were used, thereby making this problem an urgent area for individual and detailed study. However, our findings contradict the literature as G. thermoglucosidans proved amenable to genetic manipulation. All three constructs (pXYNB, pPldhA::XYNB and pXYNB70::sGFP) were successfully transformed. G. thermoglucosidans engineered with pXYNB and pPldhA::XYNB showed no difference in bacterial growth compared to the wild-type bacteria in the presence or absence of xylan. However, more research is necessary before obtaining a definitive answer about whether Gtn xynB is about to catabolise xylan. Further research into the number of screened colonies is necessary since only 1 transformant for both plasmids was grown on xylan. Moreover, since the gene expression of Gtn xynB was not investigated further research is required for its validation (107, 108). In addition to the gene expression the enzyme could be purified (109) and assayed for activity using pnitrophenyl β-d-xylopyranoside (p-NPX) (109, 110). Additional biochemical characterisation of xynB such as the optimal temperature for growth, thermostability and the effect of pH on activity could also be investigated. Studies of G. thermoglucosidans engineered with pXYNB70::sGFP provided evidence that the 70 AA N-terminus of Gtn xynB contains a signal sequence, which was not predicted by SignalP 4.1 (CBS). In future work the identified 70 AA sequence can be used to improve secretion of engineered cellulases and xylanases. In addition to this novel signal sequence, a previously reported signal peptide from G. thermoglucosidans C56-YS93 endo-β-1,4-xylanase has been identified (99). Evidence from B. subtilis highlights the importance of using a signal peptide that works well in concert with the protein to be expressed (111, 112). With two identified signal sequences and a number of genes encoding strongly predicted signal peptides in G. thermoglucosidans NCIMB 11955, SignalP 4.1 (CBS), (99) there is potential to further investigate the improvements that would be gained by the refinement of secretion of lignocellulose degrading enzymes. 56 DISCUSSION When growing G. thermoglucosidans engineered with pXYNB70::sGFP expression of sGFP was not observed in the presence of xylose or xylan. Expression of sGFP was observed in the presence of glucose. However, this experiment was initially carried out to identify whether the sequence of Gtn xynB contained a signal sequence and therefore the fluorescence of bacterial cultures was only observed under UV light. Therefore our analysis of the GFP expression when grown on alternative carbohydrates is completely qualitative and further research needs to be carried out to provide quantifiable data. These improvements could be achieved by analysing GFP expression using flow cytometry, which would provide a per cell intensity for GFP expression. None the less, considering the qualitative data, G. thermoglucosidans does not grow in the presence of xylan, but does in the presence of xylose. Therefore the concept of a growth dependent promoter can be excluded. It appears the native promoter may require glucose to induce the system. This result is important because Gtn xynB catalyses the degradation of xylan (108) yet our results suggest it’s induced by glucose, which is neither a substrate nor product of the enzyme. While there is no evidence the result could be explained by Geobacillus growing in lignocellulosic environments where cellulose and xylan would both be present. Glucose is the product of cellulose degradation and may therefore be in plentiful supply. Hence the native promoter, PxynB, could be primed by the glucose and therefore express Gtn xynB, which in turn produces the xylan 1-4-β-xylosidase and degrades xylan. While the finding was unexpected it raises a number of questions for future research. Carrying this concept forward and the hypothesis that a glucose and xylan mix will give a higher level of bacterial growth compared to glucose on its own, it would be interesting to titre the concentration of glucose to establish a minimal concentration that induces fluorescence of sGFP. Using this minimal concentration of glucose and a range of xylan concentrations the growth of G. thermoglucosidans engineered with pXYNB could then be monitored. If the catabolism of xylan was regulated by glucose it would be interesting to understand the global metabolism of Geobacillus by combining metabolic analysis with transcriptome analysis. Growing the bacteria on “RAPT” would provide a complex mix of C5 and C6 saccharides allowing the investigation into whether or not genes under the control of one metabolic pathway interfere with another. 4.3.1 Wider aspect In order to develop Geobacillus as an efficient producer of biofuel from lignocellulose, a concerted effort to engineer the genome needs to be made. There are currently two barriers preventing the use of lignocellulose as a renewable 57 DISCUSSION substrate. These include overcoming the recalcitrance of lignin to allow access to the carbohydrates (cellulose and xylan) and also engineering the catabolism of cellulose and xylan. We investigated the later. To successfully degrade cellulose Geobacillus needs to be engineered to increase expression of a free enzyme system of endo- and exoglucanases and other glycosyl hydrolases to optimal levels therefore mitigating the low expression levels shown by native bacteria. G. thermoglucosidasius NCIMB 11955 has been previously engineered to grow on cellulose by overexpressing and secreting Cel5A from Thermotoga maritima (99). Bacillus subtilis growth on amorphous cellulose has also been previously achieved by overexpressing the native BsCel5 (82). Engineering E. coli with the endocellulase Cel from Bacillus sp. D04 and the β-glucosidase Cel3A from Cellvibrio japonicus (77) has also been shown to provide a cellulolytic system capable of catabolising cellulose and allowing E. coli to grow on ionic- liquid-pretreated switchgrass. These examples show that cellulose catabolism can be attained with as few as two enzymes although the reported efficiencies are too low for an industrial bioprocess. While the bioconversion of xylan is possible in G. thermodenitrificans, it is important to explore engineering its catabolism in the other three species as they may possess potential downstream metabolic advantages for the production of biofuels. Successful engineering of xylan catabolism in E. coli used two xylanases: an endoxylanase catalytic domain (Xyn10B) from Clostridium stercorarium and a xylanase (Xsa) from Bacteroides ovatus. Xylan catabolism occurred when both genes were fused to OsmY, an efficient excretion fusion partner. The report showed the sole expression of Xyn10B was not sufficient for growth on xylan; both enzymes were required (79). In another report, E. coli was engineered with the endoxylanase Xyn10B from Clostridium stercorarium and the xylobiosidase gly43F from C. japonics (77). These examples prove xylan catabolism can be achieved with as few as two enzymes, however, the reported efficiencies were too low for an industrial bioprocess. Enzymes are also needed to debranch the substituents of xylan such as acetyl, arabinosyl, xylosyl, glucuronic acid, 4-O-methylglucuronic acid and ferulic acid substituents (38). Our results demonstrate the catabolism of arabinose and xylose, however the catabolism of acetyl, glucuronic acid, 4-O-methylglucuronic acid and ferulic acid were not investigated. If Geobacillus cannot catabolise these substituents the xylan backbone could be blocked from the active site of xylanases therefore preventing degradation. This could be overcome with the engineering the expression of enzymes such as arabinosidase, glucuronidase, acetylxylan esterase and feruloyl esterase (38). 58 DISCUSSION The reported efficiency for substrate conversion of these cellulolytic and xylanolytic systems is very low (77, 79). degradation Geobacillus could be To achieve optimal cellulose and xylan engineered to express and secrete a minicellulosome. Cellulosomes are large, extracellular multi-enzyme complexes, which are designed for the efficient deconstruction of cellulose and hemicellulose (113). Minicellulosomes are smaller and less complex artificial versions tailored for optimal enzymal synergy to act against complex polysaccharide substrates and therefore increasing enzyme efficiency (114). Minicellulosomes have been engineered in Bacillus subtilis where they successfully digested the constituents of plant cell walls (115, 116); this can be used as a starting point for future research. 59 CONCLUSION 5. CONCLUSION The genomic survey identified a number of cellulose and xylan degrading genes predicted in the genome of each representative Geobacillus species investigated. The re-formulated MASM mitigated pH change and delayed aggregation, which allowed the carbohydrate catabolism of the Geobacillus to be investigated. The four representative Geobacillus species catabolised a wide range of C5 and C6 saccharides that compose cellulose and xylan. However, cellulose and xylan were not catabolised to support growth, except in the case of G. thermodenitrificans that grew on xylan. Engineering Gtn xynB into G. thermoglucosidans did not allow bacterial growth on xylan, however, it revealed a signal peptide sequence and suggested the xylanase was induced by glucose rather than xylan or xylose. 60 BIBLIOGRAPHY 6. BIBLIOGRAPHY (1) John, U. M. (2013). Contribution of the ethanol industry to the economy of the United States (Renewable Fuels Association, Washington, DC). (2) Lynd, L. R., Laser, M. S., Bransby, D., Dale, B. E., Davison, B., Hamilton, R., Himmel, M., Keller, M., McMillan, J. D., Sheehan, J., Wyman, C. E. (2008). How biotech can transform biofuels. Nat. Biotechnol. 26(2): 169-172. (3) Himmel, M. E., Ding, S. Y., Johnson, D. K., Adney, W. S., Nimlos, M. R., Brady, J. W., Foust, T. D. (2007). Biomass recalcitrance: Engineering plants and enzymes for biofuels production. Science. 315(5813): 804-807. (4) Kerr, R. A. (2007). Climate Change. Global warming is changing the world. Science. 316(5822): 188-190. (5) Peralta-Yahya, P. P., Zhang, F., del Cardayre, S. B., Keasling, J. D. (2012). Microbial engineering for the production of advanced biofuels. Nature. 488: 320328. (6) Tilman, D., Socolow, R., Foley, J. A., Hill, J., Larson, E., Lynd, L., Pacala, S., Reilly, J., Searchinger, T., Somerville, C., Williams, R. (2009). Energy. Beneficial biofuels-The food, energy, and environment trilemma. Science. 325(5938): 270271. (7) Gronenberg, L. S., Marcheschi, R. J., Liao, J. C. (2013). Next generation biofuel engineering in prokaryotes. Curr. Opin. Chem. Biol. 17(3): 462-471. (8) Tuck, C. O., Pérez, E., Horváth, I. T., Sheldon, R. A., Poliakoff, M. (2012). Valorization of biomass: deriving more value from waste. Science. 337(6095): 695696. (9) Sommerville, C., Bauer, S., Brininstool, G., Facette, M., Hamann, T., Milne, J., Osbourne, E., Paredez, A., Persson, S., Raab, T., et al. (2004) Toward a system approach to understanding plant cell walls. Science. 306: 2206-2211. (10) Cosgrove, D. J. (2005). Growth of the plant cell wall. Nature. 6: 850-861. (11) Popper, Z. A., Michel, G., Hervé, C., Domozych, D. S., Willats, W. G. T., Tuohy, M. G., Kloareg, B., Stengel, D. B. (2011). Evolution and diversity of plant cell walls: From algae to flowering plants. Annu. Rev. Plant Biol. 62: 567-590. (12) Sorek, N., Yeats, T. H., Szemenyei, H., Youngs, H., & Somerville, C. R. (2014). The implications of lignocellulosic biomass chemical composition for the production of advanced biofuels. BioScience. 64(3): 192. (13) Jordan, D. B., Bowman, M. J., Braker, J. D., Dien, B. S., Hector, R. E., Lee, C. C., Mertens, J. A., Wagschal, K. (2012). Plant cell walls to ethanol. Biochem. J. 442(2): 241-252. (14) Somerville, C. (2006). Cellulose synthesis in higher plants. Annu. Rev. Cell Dev. Biol. 22: 53-78. 61 BIBLIOGRAPHY (15) Guerriero, G., Fugelstad, J., Bulone, V. (2010). What do we really know about cellulose biosynthesis in higher plants? J. Integr. Plant Biol. 52: 161-175. (16) Fernandes, A. N., Thomas, L. H., Altaner, C. M., Callow, P., Forsyth, V. T., Apperley, D. C., Kennedy, C. J., Jarvis, M. C. (2011). Nanostructure of cellulose microfibrils in spruce wood. Proc. Natl. Acad. Sci. USA. 108: E1195-E1203. (17) Assareh, R., Shahbani Zahiri, H., Akbari Noghabi, K., Aminzadeh, S., & Bakhshi Khaniki, G. (2012) Characterisation of the newly isolated Geobacillus sp. T1, the efficient cellulase-producer on untreated barley and wheat straws. Bioresour. Technol. 120: 99-105. (18) Barnard, D., Casanueva, A., Tuffin, M., Cowan, D. (2010). Extremophiles in biofuels synthesis. Environ. Technol. 31: 871-888. (19) Sánchez, C. (2009). Lignocellulosic residues: Biodegradation and bioconversion by fungi. Biotechnol. Adv. 27(2): 185-194. (20) Rastogi, G., Bhalla, A., Adhikari, A., Bischoff, K. M., Hughes, S. R., Christopher, L. P., Sani, R. K. (2010). Characterization of thermostable cellulases produced by Bacillus and Geobacillus strains. Bioresour. Technol. 101: 8798-8806. (21) Rastogi, G., Muppidi, G. L., Gurram, R. N., Adhikari, A., Bischoff, K. M., Hughes, S. R., Apel, W. A., Bang, S. S., Dixon, D. J., Sani, R. K. (2009). Isolation and characterization of cellulose-degrading bacteria from the deep subsurface of the Homestake gold mine, Lead, South Dakota, USA. J. Ind. Microbiol. Biotechnol. 36: 585-598. (22) Freier, D., Mothershed, C. P., Wigel, J. (1988). Characterization of Clostridium thermocellumJW20. Appl. Environ. Microbiol. 54: 204-211. (23) Hamilton-Brehm, S. D., et al. (2010). Caldicellulosiruptor obsidian sp. Nov., an anaerobic, extremely thermophilic, cellulyotic bacterium isolated from Obsidian Pool, Yellowstone National Park. Appl. Environ. Microbiol. 76: 1014-1020. (24) Kato, S., Haruta, S., Cui, Z. J., Ishii, M., Yokota, A., Igarashi, Y. (2004). Clostridium straminisolvens sp. Nov., a moderately thermophilic, aerotolerant and cellulolytic bacterium isolated from a cellulose-degrading bacterial community. Int. J. Syst. Evol. Microbiol. 54: 2043-2047. (25) Madden, R. H. (1983). Isolation and characterization of Clostridium stercorarium sp. nov., cellulolytic thermophile. Int. J. Syst. Bacteriol. 33: 837-840. (26) Rainey, F. A., Donnison, A. M., Janssen, P. H., Saul, D., Rodrigo, A., Bergquist, P. L., Daniel, R. M., Stackebrandt, E., Morgan, H. W. (1994). Description of Caldicellulosiruptor saccharolyticus gen. nov., sp. Nov: an abligaetly anaerobic, extremely thermophilic, cellulolytic bacterium. FEMS Microbiol. Lett. 120: 263-266. 62 BIBLIOGRAPHY (27) Lindenmuth, B. E., McDonald, K. A. (2011). Production and characterization of Acidothermus cellulolyticus endoglucanase in Pichia pastoris. PREP. 77(2): 153158. (28) Lo, Y. C., Huang, C. L., Cheng, C. Y., Lin, C. Y., & Chang, J. S. (2011). Characterization of cellulolytic enzymes and bioH2 production from anaerobic thermophilic Clostridium sp. TCW1. Bioresour. Technol. 102(18): 8384-8392. (29) Bischoff, K. M., Liu, S., Hughes, S. R. (2007). Cloning and characterization of a recombinant family 5 endoglucanase from Bacillus licheniformis strain B-41361. Process Biochem. 42(7): 1150-1154. (30) Tai, S. K., Lin, H. P., Kuo, J., Liu, J. K. (2004). Isolation and characterization of a cellulolytic Geobacillus thermoleovorans T4 strain from sugar refinery wastewater. Extremophiles. 8(5): 345-349. (31) Huang, X. P., & Monk, C. (2004). Purification and characterization of a cellulase (CMCase) from a newly isolated thermophilic aerobic bacterium Caldibacillus cellulovorans gen. nov., sp. nov. World J. Microbiol. Biotechnol. 20(1): 85-92. (32) Arantes, V., & Saddler, N. J. (2010). Access to cellulose limits the efficiency of enzymatic hydrolysis: the role of amorphogenesis. Biotechnol. biofuels. 3(1): 1-11. (33) Lynd, L. R., Weimer, P. J., Van Zyl, W. H., Pretorius, I. S. (2002). Microbial cellulose utilization: Fundamentals and biotechnology. Microbiol. Mol. Biol. Rev. 66(3): 506-577. (34) Lairson, L. L., Henrissat, B., Davies, G. J., & Withers, S. G. (2008). Glycosyl transferases: Structures, functions, and mechanisms. Annu. Rev. Biochem. 77: 521-555. (35) Pauly, M., Gille, S., Liu, L., Mansoori, N., de Souza, A., Schultink, A., Xiong, G. (2013). Hemicellulose biosynthesis. Planta. 238: 627-642. (36) Anand, A., Kumar, V., Satyanarayana, T. (2013). Characteristics of thermostable endoxylanase and β-xylosidase of the extremely thermophilic bacterium Geobacillus thermodenitrificans TSAA1 and its applicability in generating xylooligosaccharides and xylose from agro-residues. Extremophiles. 17(3): 357366. (37) Scheller, H. V., & Ulvskov, P. (2010). Hemicelluloses. Annu. Rev. Plant Biol. 61: 263-289. (38) Rennie, E. A. & Vibe Scheller, H. (2014). Xylan biosynthesis. Curr. Opin. Biotechnol. 26: 100-107. (39) Gírio, F. M., Fonseca, C., Carvalheiro, F., Duarte, L. C., Marques, S., & BogelŁukasik, R. (2010). Hemicelluloses for fuel ethanol: A review. Bioresour. Technol. 101(13): 4775-4800. 63 BIBLIOGRAPHY (40) Sunna, A., & Antranikian, G. (1997). Xylanolytic enzymes from fungi and bacteria. Crit. Rev. Biotechnol. 17(1): 39-67. (41) Collins, T., Gerday, C., Feller, G. (2005). Xylanases, xylanase families and extremophilic xylanases. FEMS Microbiol. Rev. 29(1): 3-23. (42) Lee, J. W., Park, J. Y., Kwon, M., Choi, I. G. (2009). Purification and characterization of a thermostable xylanase from the brown-rot fungus Laetiporus sulphureus. J. Biosci. Bioeng. 107(1): 33-37. (43) Maalej, I., Belhaj, I., Masmoudi, N. F., Belghith, H. (2009). Highly thermostable xylanase of the thermophilic fungus Talaromyces thermophilus: Purification and characterization. Appl. Biochem. Biotechnol. 158(1): 200-212. (44) Singh, S., Madlala, A. M., Prior, B. A. (2003). Thermomyces lanuginosus: Properties of strains and their hemicellulases. FEMS Microbiol. Rev. 27(1): 3-16. (45) Zhang, J., Siika-Aho, M., Puranen, T., Tang, M., Tenkanen, M., Viikari, L. (2011). Thermostable recombinant xylanases from Nonomuraea flexuosa and Thermoascus aurantiacus show distinct properties in the hydrolysis of xylans and pretreated wheat straw. Biotechnol. Biofuels. 4: 12. (46) Saleem, M., Aslam, F., Akhtar, M. S., Tariq, M., Rajoka, M. I. (2012). Characterization of a thermostable and alkaline xylanase from Bacillus sp. and its bleaching impact on wheat straw pulp. World J. Microbiol. Biotechnol. 28(2): 513522. (47) Shrinivas, A. J., Savitha, G., Raviranjan, K., Naik, G. R. (2010). A highly thermostable alkaline cellulase-free xylanase from thermoalkalophilic Bacillus sp. JB 99 suitable for paper and pulp industry: purification and characterization. Biochem. Biotechnol. 162: 2049-2057. (48) Sapre, M. P., Jha, H., Patil, M. B. (2005). Purification and characterization of a thermoalkalophilic xylanase from Bacillus sp. World J. Microbiol. Biotechnol. 21(5): 649-654. (49) Verma, D., & Satyanarayana, T. (2012). Cloning, expression and applicability of thermo-alkali-stable xylanase of Geobacillus thermoleovorans in generating xylooligosaccharides from agro-residues. Bioresour. Technol. 107: 333-338. (50) Wu, S., Liu, B., Zhang, X. (2006). Characterization of a recombinant thermostable xylanase from deep-sea thermophilic Geobacillus sp. MT-1 in east pacific. Appl. Microbiol. Biotechnology. 72(6): 1210-1216. (51) Zhengqiang, J., Kobayashi, A., Ahsan, M. M., Lite, L., Kitaoka, M., Hayashi, K. (2001). Characterization of a thermostable family 10 endo-xylanase (XynB) from Thermotoga maritima that cleaves p-nitrophenyl-β-D-xyloside. J. Biosci. Bioeng. 92(5): 423-428. 64 BIBLIOGRAPHY (52) Simpson, H. D., Haufler, U. R., Daniel, R. M. (1991). An extremely thermostable xylanase from the thermophilic eubacterium Thermotoga. Biochem. J. 277(2): 413417. (53) Barabote, R. D., Parales, J. V., Guo, Y. Y., Labavitch, J. M., Parales, R. E., Berry, A. M. (2010). Xyn10A, a thermostable endoxylanase from Acidothermus cellulolyticus 11B. Appli. Environ. Microbiol. 76(21): 7363-7366. (54) Dheeran, P., Nandhagopal, N., Kumar, S., Jaiswal, Y. K., Adhikari, D. K. (2012). A novel thermostable xylanase of Paenibacillus macerans IIPSP3 isolated from the termite gut. J. Ind. Microbiol. Biotechnol. 39(6): 851-860. (55) Lee, T. H., Lim, P. O., Lee, Y. E. (2007). Cloning, characterization, and expression of xylanase A gene from Paenibacillus sp. DG-22 in Escherichia coli. J. Microbiol. Biotechnol. 17(1): 29-36. (56) Hung, K. S., Liu, S. M., Tzou, W. S., Lin, F. P., Pan, C. L., Fang, T. Y., Sun. K. H., Tang, S. J. (2011). Characterization of a novel GH10 thermostable, halophilic xylanase from the marine bacterium Thermoanaerobacterium saccharolyticum NTOU1. Process Biochem. 46(6): 1257-1263. (57) Sriyapai, T., Somyoonsap, P., Matsui, K., Kawai, F., Chansiri, K. (2011). Cloning of a thermostable xylanase from Actinomadura sp. S14 and its expression in Escherichia coli and Pichia pastoris. J. Biosci. Bioeng. 111(5): 528-536. (58) Bai, Y., Wang, J., Zhang, Z., Yang, P., Shi, P., Luo, H., Meng, K., Huang, H., Yao, B. (2010). A new xylanase from thermoacidophilic Alicyclobacillus sp. A4 with broad-range pH activity and pH stability. J. Ind. Microbiol. Biotechnol. 37(2): 187194. (59) Wang, Y., Wang, X., Tang, R., Yu, S., Zheng, B., Feng, Y. (2010). A novel thermostable cellulase from Fervidobacterium nodosum. Journal of Molecular Catalysis B: Enzymatic. 66(3-4): 294-301. (60) Kui, H., Luo, H., Shi, P., Bai, Y., Yuan, T., Wang, Y., Yang, P., Dong, S., Yao, B. (2010). Gene cloning, expression, and characterization of a thermostable xylanase from Nesterenkonia xinjiangensis CCTCC AA001025. Appl. Biochem. Biotechnol. 162(4): 953-965. (61) Khandeparkar, R., & Bhosle, N. B. (2006). Purification and characterization of thermoalkalophilic xylanase isolated from the Enterobacter sp. MTCC 5112. Res. Microbiol. 157(4): 315-325. (62) Saha, B. C. (2003). Hemicellulose bioconversion. J. Ind. Microbiol. Biotechnol. 30(5): 279-291. (63) Subramaniyan, S., & Prema, P. (2002). Biotechnology of microbial xylanases: Enzymology, molecular biology, and application. Crit. Rev. Biotechnol. 22(1): 3364. 65 BIBLIOGRAPHY (64) Espina, G., Eley, K., Pompidor, G., Schneider, T. R., Crennell, S. J., & Danson, M. J. (2014). A novel β-xylosidase structure from Geobacillus thermoglucosidasius: The first crystal structure of a glycoside hydrolase family GH52 enzyme reveals unpredicted similarity to other glycoside hydrolase folds. Acta Crystallogr. Sect. D: Biol. Crystallogr. 70(5): 1366-1374. (65) Brown, M. E., Chang, M. C. Y. (2014). Exploring bacterial lignin degradation. Curr. Opin. Chem. Biol. 19: 1-7. (66) Boerjan, W., Ralph, J., Baucher, M. (2003). Lignin biosynthesis. Annu. Rev. Plant Biol. 54: 519-546. (67) Vanholme, R., Demedts, B., Morreal, K., Ralph, J., Boerjan, W. (2010). Lignin biosynthesis and structure. Plant Physio. 153: 895-905. (68) Chen, F., Dixon, R. A. (2007). Lignin modification improves fermentable sugar yields for biofuel production. Nat. Biotechnol. 25: 759-761. (69) Ding, S. Y., Liu, Y. S., Zeng, Y., Himmel, M. E., Baker, J. O., Bayer, E. A. (2012). How does plant cell wall nanoscale architecture correlate with enzymatic digestibility? Science. 338: 1055-1060. (70) Kirk, T. K., & Farrell, R. L. (1987). Enzymatic "combustion": the microbial degradation of lignin. Annu. Rev. Microbiol. 41: 465-505. (71) ten Have, R., & Teunissen, P. J. M. (2001). Oxidative mechanisms involved in lignin degradation by white-rot fungi. Chem. Rev. 101(11): 3397-3413. (72) Thurston, C. F. (1994). The structure and function of fungal laccases. Microbiology. 140(1): 19-26. (73) Khindaria, A., Yamazaki, I., Aust, S. D. (1995). Veratryl alcohol oxidation by lignin peroxidase. Biochemistry. 34(51): 16860-16869. (74) Glenn, J. K., & Gold, M. H. (1985). Purification and characterization of an extracellular mn(II)-dependent peroxidase from the lignin-degrading basidiomycete, Phanerochaete chrysosporium. Arch. Biochem. Biophys. 242(2): 329-341. (75) Kuan, I. C., Johnson, K. A., Tien, M. (1993). Kinetic analysis of manganese peroxidase: The reaction with manganese complexes. J. Biol. Chem. 268(27): 20064-20070. (76) Olson, D. G., McBride, J. E., Shaw, A. J., Lynd, L. R. (2012). Recent progress in consolidated bioprocessing. Curr. Opin. Biotechnol. 23(3): 396-405. (77) Bokinsky, G., Peralta-Yahya, P. P., George, A., Holmes, B. M., Steen, E. J., Dietrich, J., Soon Lee, T., Tullman-Ercek, D., Voigt, C. A., Simmons, B. A., et al.. (2011). Synthesis of three advanced biofuels from ionic liquid-pretreated switchgrass using engineered Escherichia coli. Proc. Natl. Acad. Sci. USA. 108: 19949-19954. 66 BIBLIOGRAPHY (78) Linger, J. G., Adney, W. S., Darzins, A. (2010). Heterologous expression and extracellular secretion of cellulolytic enzymes by Zymomonas mobilis. Appl. Environ. Microbiol. 76(19): 6360-6369. (79) Steen, E. J., Kang, Y., Bokinsky. G., Hu, Z., Schirmer, A., McClure, A., del Cardayre, S. B., Keasling, J. D. (2010). Microbial production of fatty-acid-derived fuels and chemicals from plant biomass. Nature. 463: 559-562. (80) Mazzoli, R., Lamberti, C., Pessione, E. (2012). Engineering new metabolic capabilities in bacteria: lessons from recombinant cellulolytic strategies. Trends Biotechnol. 30: 111-119. (81) Soma, Y., Inokuma, K., Tanake, T., Ogino, C., Konodo, A., Okamoto, M., Hanai, T. (2012). Direct isopropanol production from cellobiose by engineered Escherichia coli using a synthetic pathway and a cell surface display system. J. Biosci. Bioeng. 114: 80-85. (82) Zhang, X. Z., Sathitsuksanoh, N., Zhu, Z., Percival Zhang, Y. H. (2011). One-step production of lactate from cellulose as the sole carbon source without any other organic nutrient by recombinant cellulolytic Bacillus subtilis. Metab. Eng. 13: 364372. (83) Anderson, T. D., Robson, S. A., Jiang, X. W., Malmirchegini, G. R., Fierobe, H. P. (2011). Assembly of minicellulosomes on the surface of Bacillus subtilis. Appl. Environ. Microbiol. 77: 4849-4858. (84) Zambare, V. P., Bhalla, A., Muthukumarappan, K., Sani, R. K., Christopher, L. P. (2011). Bioprocessing of agricultural residues to ethanol utilizing a cellulolytic extremophile. Extremophiles. 15: 611-618. (85) Liang, C. Xue, Y., Fioroni, M., Rodríguez-Ropero, F., Zhou, C., Schwaneberg, U., Ma, Y. (2011). Cloning and characterization of a thermostable and halo-tolerant endoglucanase from Thermoanaerobacter tengcongensis MB4. Appl. Microbiol. Biotechnol. 89: 315-326. (86) Yeoman, C. J., Han, Y., Dodd, D., Schroeder, C., Mackie, R. I., Cann, I. K. (2010). Thermostable enzymes as biocatalysts in the biofuel industry. Adv. Appl. Microbiol. 70: 1-55. (87) Viikari, L., Alapuranen, M., Puranen, T., Vehmaanpera, J., Siika-Aho, M. (2007) Thermostable enzymes in lignocellulose hydrolysis. Adv. Biochem. Eng. Biotechnol. 108: 121-145. (88) Haki, G.D., & Rakshit, S. K. (2003) Developments of industrially important thermostable enzymes: a review. Bioresour. Technol. 89: 17-34. (89) Zhang, J., Siika-Aho, M., Puranen, T., Tang, M., Tenkanen, M., Viiikari, L. (2011). Thermostable recombinant xylanases from Nonomuraea flexuosa and 67 BIBLIOGRAPHY Thermoascus aurantiacus show distinct properties in the hydrolysis of xylans and pretreated wheat straw. Biotechnol. Biofuels. 4: 12. (90) Taylor, M. P., Eley, K. L., Martin, S., Tuffin, M. I., Burton, S. G., Cowan, D. A. (2009). Thermophilic ethanologenesis: future prospects for second-generation bioethanol production. Trends Biotechnol. 27: 398-405. (91) Maki, V., Leung, K. T., Qin, W. (2009). The prospects of cellulase-producing bacteria for the bioconversion of lignocellulosic biomass. Int. J. Biol. Sci. 5: 500516. (92) Mai, V., & Wiegel, J. (2000). Advances in development of a genetic system for Thermoanaerobacterium spp.: expression of genes encoding hydrolytic enzymes, development of a second shuttle vector, and integration of genes into the chromosome. Appl. Environ. Microbiol. 66(11): 4817-4821. (93) McMullan, G., Christie, J. M., Rahman, T. J., Banat, I. M., Ternan, N. G., Marchant, R. (2004). Habitat, applications and genomics of the aerobic, thermophilic genus Geobacillus. Biochem. Soc. Trans. 32: 214-217. (94) Nazina, T. N., Tourova , T. P., Poltaraus, A. B., Novikova, E. V., Grigoryan, A. A., Ivanova, A. E., Lysenko, A. M., Petrunyaka, V. V., Osipov, G. A., Belyaev, S. S., et al. (2001). Taxonomic study of aerobic thermophilic bacilli: descriptions of Geobacillus subterraneus gen. nov., sp. nov. and Geobacillus uzenensis sp. nov. from petroleum reservoirs and transfer of Bacillus stearothermophilus, Bacillus thermo-catenulatus, Bacillus thermoleovorans, Bacillus kaustophilus, Bacillus thermoglucosidasius and Bacillus thermodenitrificans to Geobacillus as the new combinations G. stearothermophilus, G. thermocatenulatus, G. thermoleovorans, G. kaustophilus, G. thermoglucosidasius and G. thermodenitrificans. Int. J. Syst. Evol. Microbiol. 51: 433–446. (95) Cripps, R. E., Eley, K., Leak, D. K., Rudd, B., Taylor, M., Todd, M., Boakes, S., Martin, S., Atkinson, T. (2009). Metabolic engineering of Geobacillus thermoglucosidasius for high yield ethanol production. Metab. Eng. 11: 398-408. (96) Abdel-Fattah, Y. R., El-Helow, E. R., Ghanem, K. M., Lotfy, W. A. (2007). Application of factorial designs for optimization of avicelase production by a thermophilic Geobacillus isolate. Res. J. Microbiol. 2(1): 13-23. (97) Suzuki, H., & Yoshida, K. I. (2012). Genetic transformation of Geobacillus kaustophilus HTA426 by conjugative transfer of host-mimicking plasmids. J. Microbiol. Biotechnol. 22(9): 1279-1287. (98) Fong, J. C., Svenson, C. J., Nakasugi, K., Leong, C. T., Bowman, J. P., Chen, B., Glenn, D. R., Neilan, B. A., Rogers, P. L. (2006). Isolation and characterization of two novel ethanol-tolerant facultative-anaerobic thermophilic bacteria strains from waste compost. Extremophiles. 10(5): 363-372. 68 BIBLIOGRAPHY (99) Bartosiak-Jentys, J., Hussein, A. H., Lewis, C. J., Leak, D. J. (2013). Modular system for assessment of glycosyl hydrolase secretion in Geobacillus thermoglucosidasius. Microbiology (United Kingdom). 159(PART7): 1267-1275. (100) Chamkha, M., Mnif, S., Sayadi, S. (2008). Isolation of a thermophilic and halophilic tyrosol-degrading Geobacillus from a tunisian high-temperature oil field. FEMS Microbiol. Lett. 283(1): 23-29. (101) Chen, X. G., Stabnikova, O., Tay, J. H., Wang, J. Y., Tay, S. T. L. (2004). Thermoactive extracellular proteases of Geobacillus caldoproteolyticus, sp. nov., from sewage sludge. Extremophiles. 8(6): 489-498. (102) Gerasimova, J., & Kuisiene, N. (2012). Characterization of the novel xylanase from the thermophilic Geobacillus thermodenitrificans JK1. Microbiology (Russian Federation). 81(4): 418-424. (103) Contreras-Moreira, B., & Vinuesa, P. (2013). GET_HOMOLOGUES, a versatile software package for scalable and robust microbial pangenome analysis. Appli. Environ. Microbiol. 79(24): 7696-7701. (104) Pédelacq, J. D., Cabantous, S., Tran, T., Terwilliger, T. C., Waldo, G. S. (2006). Engineering and characterization of a superfolder green fluorescent protein. Nat. Biotechnol. 24(1): 79-88. (105) Rozanov, A. S., Meshcheryakova, I. A., Shekhovtsov, S. V., Peltek, S. E. (2014). Current state of genetic and metabolic engineering of the genus Geobacillus aimed at production of ethanol and organic acids. Russ. J. Genet: Appl. Res. 4(3): 218-226. (106) Bhalla, A., Bansal, N., Kumar, S., Bischoff, K. M., Sani, R. K. (2013). Improved lignocellulose conversion to biofuels with thermophilic bacteria and thermostable enzymes. Bioresour. Technol. 128: 751-759. (107) Cuebas, M., Villafane, A., Mcbride, M., Yee, N., Bini, E. (2011). Arsenate reduction and expression of multiple chromosomal ars operons in Geobacillus kaustophilus A1. Microbiology. 157(7): 2004-2011. (108) Feng, L., Wang, W., Cheng, J., Ren, Y., Zhao, G., Gao, C., Tang, Y., Liu, X., Han, W., Peng, X., Liu, R., Wang, L. (2007). Genome and proteome of long-chain alkane degrading Geobacillus thermodenitrificans NG80-2 isolated from a deepsubsurface oil reservoir. Proc. Natl. Acad. Sci. USA. 104(13): 5602-5607. (109) Bergdale, T. E., Hughes, S. R., Bang, S. S. (2014). Thermostable hemicellulases of a bacterium, Geobacillus sp. DC3, isolated from the former homestake gold mine in lead, south Dakota. Appl. Biochem. Biotechnol. 172(7): 3488-3501. (110) Anand, A., Kumar, V., Satyanarayana, T. (2013). Characteristics of thermostable endoxylanase and β-xylosidase of the extremely thermophilic 69 BIBLIOGRAPHY bacterium Geobacillus thermodenitrificans TSAA1 and its applicability in generating xylooligosaccharides and xylose from agro-residues. Extremophiles. 17(3): 357-366. (111) Brockmeier, U., Caspers, M., Freudl, R., Jockwer, A., Noll, T., Eggert, T. (2006). Systematic screening of all signal peptides from Bacillus subtilis: A powerful strategy in optimizing heterologous protein secretion in gram-positive bacteria. J. Mol. Biol. 362(3): 393-402. (112) Tjalsma, H., Bolhuis, A., Jongbloed, J. D. H., Bron, S., Van Dijl, J. M. (2000). Signal peptide-dependent protein transport in Bacillus subtilis: A genome-based survey of the secretome. Microbiol. Mol. Biol. Rev. 64(3): 515-547. (113) Kovács, K., Willson, B. J., Schwarz, K., Heap, J. T., Jackson, A., Bolam, D. N., Winzer, K., Minton, N. P. (2013). Secretion and assembly of functional minicellulosomes from synthetic chromosomal operons in Clostridium acetobutylicum ATCC 824. Biotechnol. Biofuels. 6(1): 117. (114) Xu, Q., Ding, S. Y., Brunecky, R., Bomble, Y. J., Himmel, M. E., Baker, J. O. (2013). Improving activity of minicellulosomes by integration of intra- and intermolecular synergies. Biotechnol. Biofuels. 6(1): 126. (115) Cho, H. Y., Yukawa, H., Inui, M., Doi, R. H., Wong, S. L. (2004). Production of minicellulosomes from Clostridium cellulovorans in Bacillus subtilis WB800. Appl. Environ. Microbiol. 70(9): 5704-5707. (116) Anderson, T. D., Miller, J. I., Fierobe, H. P., Clubb, R. T. (2013). Recombinant Bacillus subtilis that grows on untreated plant biomass. Appl. Environ. Microbiol. 79(3): 867-876. 70