Skip to main content
Microbial Biotechnology logoLink to Microbial Biotechnology
. 2017 Mar 20;10(6):1546–1557. doi: 10.1111/1751-7915.12494

Caldicellulosiruptor saccharolyticus transcriptomes reveal consequences of chemical pretreatment and genetic modification of lignocellulose

Sara E Blumer‐Schuette 1,3, Jeffrey V Zurawski 1, Jonathan M Conway 1, Piyum Khatibi 1, Derrick L Lewis 1,4, Quanzi Li 2,5, Vincent L Chiang 2, Robert M Kelly 1,
PMCID: PMC5658599  PMID: 28322023

Summary

Recalcitrance of plant biomass is a major barrier for commercially feasible cellulosic biofuel production. Chemical and enzymatic assays have been developed to measure recalcitrance and carbohydrate composition; however, none of these assays can directly report which polysaccharides a candidate microbe will sense during growth on these substrates. Here, we propose using the transcriptomic response of the plant biomass‐deconstructing microbe, Caldicellulosiruptor saccharolyticus, as a direct measure of how suitable a sample of plant biomass may be for fermentation based on the bioavailability of polysaccharides. Key genes were identified using the global gene response of the microbe to model plant polysaccharides and various types of unpretreated, chemically pretreated and genetically modified plant biomass. While the majority of C. saccharolyticus genes responding were similar between plant biomasses; subtle differences were discernable, most importantly between chemically pretreated or genetically modified biomass that both exhibit similar levels of solubilization by the microbe. Furthermore, the results here present a new paradigm for assessing plant–microbe interactions that can be deployed as a biological assay to report on the complexity and recalcitrance of plant biomass.

Introduction

The production of biofuels and bioproducts from renewable feedstocks has triggered efforts to develop plants and microorganisms that can be integrated into efficient bioprocessing schemes (Gronenberg et al., 2013; Loqué et al., 2015). When considering plant biomass feedstocks, one of the most significant challenges is to reduce recalcitrance of plant biomass either by thermo/chemical pretreatment (Sun et al., 2016) or through the use of synthetic biology and genetic tools to breed plants with reduced recalcitrance (Shih et al., 2016). On the microbial side, the focus is on metabolic engineering strategies that enable both plant cell wall deconstruction to fermentable sugars and subsequent conversion of these sugars to a biofuel at acceptable yields and titres (Liao et al., 2016). Given the potential scale of biofuel processes, even small improvements in carbohydrate accessibility and conversion can translate into significant economic benefits (Tao et al., 2011). Thus, it is important to have insightful methods to assess the subtle differences in plant cell wall characteristics, as these relate to biomass recalcitrance and potential toxicity arising from lignin moieties that are released during deconstruction.

Current efforts for improving the conversion of plant biomass to biofuels typically involve a thermal and/or chemical pretreatment step to reduce lignin content and to partially hydrolyse hemicellulose, components that shield cellulose microfibrils from microbial attack (Singh et al., 2015). Chemical pretreatments historically have relied on acidic (Tucker et al., 1998) or alkaline (Holtzapple et al., 1991) mechanisms for disrupting the bonds between lignin and polysaccharides. Alternatively, or in conjunction with chemical pretreatment, carbohydrate or lignin biosynthetic pathways in model biomass feedstocks have been genetically manipulated to produce transgenic plants with biochemically altered cell walls and consequently lowered recalcitrance to cellulose conversion (Van Acker et al., 2014). For example, genetically modified aspen (Populus tremuloides), in which a 4‐coumarate‐CoA ligase (4CL) (Chen and Dixon, 2007) lignin biosynthesis gene was downregulated, resulted in reduced lignin and increased cellulose levels, thereby simultaneously reducing recalcitrance and increasing substrate availability for saccharification. Genetic modifications to plant cell walls have improved conversion by microbes fermenting reduced lignin hybrid poplar (Li et al., 2003) and switchgrass (Van Acker et al., 2014). Furthermore, pairing less‐recalcitrant, genetically modified switchgrass with wild type Clostridium thermocellum (Fu et al., 2011) or an engineered and evolved strain of C. thermocellum (M1570) (Yee et al., 2014) increased ethanol production. Additionally, natural variation of plant cell wall composition in Populus sp. (Studer et al., 2011) has created feedstocks with improved conversion properties for consolidated bioprocessing (Dumitrache et al., 2016).

Whether chemical or genetic pretreatment is used or natural variants with favourable properties are considered, it is important to determine how the availability of the carbohydrate content of plant biomass to microbial attack has been modified and to what extent. Given the complexity of plant cell wall composition, which has defining biochemical and physical characteristics, it is difficult to determine subtle, but important, changes that can arise from chemical and genetic pretreatments. While a number of advanced analytical tools have been developed along these lines, they can only report on the sum total of chemical changes, rather than the differences that may elicit differential responses by microbes. When considering microbial conversion, however, no analytical method is capable of directly reporting the extent to which the particular feedstock has become more amenable to microbial attack. This might best be done using a microbial‐based assay.

Among the possible choices for such a microbial assay is Caldicellulosiruptor saccharolyticus, a cellulolytic and xylanolytic bacterium, which is also capable of growth on a broad spectrum of carbohydrates (VanFossen et al., 2009) and acid‐pretreated (Blumer‐Schuette et al., 2010) and unpretreated biomass (Zurawski et al., 2015). Before‐and‐after analysis of the total carbohydrate content of feedstocks subjected to microbial treatment is capable of providing useful information on the suitability of a plant feedstock in supporting growth (Zurawski et al., 2015). Conversely, a more detailed view of compounds that the microbe senses and responds to (‘bioavailability’) could come from analysis of its transcriptome from growth on plant biomass feedstocks. Studies observing gene expression of either lignocellulosic fungi (Gaskell et al., 2014, 2016; Couturier et al., 2015) or lignocellulosic bacteria (Raman et al., 2009; VanFossen et al., 2011) grown on plant biomass feedstocks and sugars have so far focused on extracellular enzymes. Novel and useful insights into the plant biomass matrix in question could be obtained, based not only on the differential transcription of genes encoding glycoside hydrolases, but also including ATP‐binding cassette (ABC) sugar transporters and key metabolic pathway enzymes. Additionally, the transcriptome could reveal information concerning the impact of lignin modifications on the microbe, and whether this leads to a more easily deconstructed biomass. Here, we describe the use of C. saccharolyticus transcriptomes to probe for the bioavailable carbohydrate content of growth substrates and to evaluate recalcitrance of the substrate after chemical pretreatment or genetic modification of the plant biomass.

Results and discussion

Before evaluating C. saccharolyticus transcriptomes to discern features related to biomass recalcitrance and deconstruction, it was first necessary to establish that this bacterium was capable of deconstructing the various forms of lignocellulose tested. C. saccharolyticus has previously been demonstrated to grow on dilute acid‐pretreated (DAP) switchgrass (Panicum virgatum), DAP Populus hybrid (P. trichocarpa x deltoides) (Blumer‐Schuette et al., 2010) and unpretreated switchgrass (Zurawski et al., 2015) to differing extents. Aside from previous biomasses tested, we also sought to establish that C. saccharolyticus was capable of growth on related unpretreated biomasses, including wild type (P. trichocarpa) and genetically modified P. trichocarpa samples. As such, we elected to focus on poplar and switchgrass as representative plant biomasses for this study.

Solubilization of lignocellulose by C. saccharolyticus

Here, the solubilization of unpretreated Populus sp. (wild type Populus trichocarpa), genetically modified, lignin‐reduced Populus sp. (4CL antisense P. trichocarpa), DAP Populus and switchgrass was determined as a prelude to comparative transcriptomic analysis based on these plant biomasses. Mass loss attributed to C. saccharolyticus grown on lignin‐reduced or DAP Populus (21.3 ± 3.8% and 19.3 ± 1.0%, respectively, above abiotic controls) was higher than mass loss of wild‐type Populus or DAP switchgrass (11.5 ± 2.5% and 9.3 ± 3.1%, respectively, above abiotic controls, see Fig. 1A). It is interesting that the extent of biological solubilization for lignin‐reduced Populus either by chemical or by genetically modified means was comparable. The low level of biological solubilization during growth on DAP switchgrass can be partially attributed to the high level of abiotic solubilization (19.8 ± 2.6%), presumably due to water‐soluble oligosaccharides liberated by DAP.

Figure 1.

Figure 1

Solubilization of plant biomass by Caldicellulosiruptor saccharolyticus.

A. Percentage of mass loss after 7 day incubation at 70°C. Each column represents percentage of mass loss due to biotic (Csac, grey) or thermal (abiotic, black) means for each biomass tested.

B. Percentage of total mass loss attributed to glucans (black), xylan (grey) or inert material (white). Solubilization percentages are the means ± standard deviations (n = 3). as4CL, lignin‐reduced Populus trichocarpa; Ptri, unpretreated Ptrichocarpa; aPTD, dilute acid‐pretreated Populus trichocarpa x deltoides; aSWG, dilute acid‐pretreated switchgrass.

Quantitative saccharification was then used to determine relative levels of glucans, xylan, arabinans and inert material before and after deconstruction by C. saccharolyticus for four types of plant biomass assayed (Table S1). Previous reports of biological solubilization by a related species, C. bescii, determined that the relative levels of glucans, xylans and lignin remained constant throughout subsequent passages (Kataeva et al., 2013). These data establish which types of biomass had reduced levels of recalcitrance and presumably more bioavailable carbohydrates that were in turn solubilized.

Prior to supporting growth of C. saccharolyticus, unpretreated biomasses (wild type and lignin‐reduced) contained more xylan on a per gram basis (Table S1) than did either of the DAP biomasses (Populus or switchgrass). Interestingly, when comparing genetically modified to wild‐type biomass, the overall percentage of biomass solubilized from lignin‐reduced Populus was higher (Fig. 1A) in addition to the relative proportion of both xylan and inert material liberated from lignin‐reduced Populus (Fig. 1B).

With respect to DAP biomass, the majority of solubilized carbohydrates from DAP Populus were glucans, while both glucans and xylan were solubilized during growth on DAP switchgrass (Fig. 1B), which shares similarity to lignin‐reduced Populus. Given that C. saccharolyticus was able to solubilize each biomass tested, we used unpretreated, DAP and genetically modified plant biomass as a basis for examining differences in transcriptomes during C. saccharolyticus active growth. Ultimately, we sought to determine whether our test case microbe, C. saccharolyticus, could detect differentiating features of recalcitrance and carbohydrate bioavailability as they impact potential biocatalyst performance.

Complex polysaccharide transcriptomes

To provide a basis for discerning subtle changes in plant cell wall composition as a result of natural variation, chemical pretreatment or genetic modification, the transcriptional response of C. saccharolyticus to purified forms of key plant polysaccharides was first determined (Loop #1, Fig. 2A). Crystalline cellulose was selected as one of the structural carbohydrates used in this bioassay as it is the major carbohydrate found in plant cell walls (Pauly and Keegstra, 2010). Hemicellulose components were also selected based on their presence in plant cell walls including xylan (Timell, 1967), glucomannan (Whitney et al., 1998) and pectin (Xiao and Anderson, 2013). This information was then used to probe C. saccharolyticus transcriptomes growing on plant biomass samples for differentiating features related to recalcitrance and carbohydrate availability for microbial utilization.

Figure 2.

Figure 2

Transcriptional response experimental design and meta‐analysis. Experimental loop design is illustrated using arrows, which collectively represent a microarray slide hybridized with two treatments (Cy3 or Cy5 labelled). Arrows in panels A, B and C indicate the Cy3‐labelled (green circle) and Cy5‐labelled (red triangle) conditions respectively. Data from each loop were processed separately as described in experimental methods.

A. Microarray Loop #1: KGM, konjac glucomannan; Avicel, crystalline cellulose; pectin; and xylan, birchwood xylan.

B. Microarray Loop #2: aPTD, dilute acid‐pretreated Populus sp.; Ptri, unpretreated Populus sp.; aSWG, dilute acid‐pretreated switchgrass; as4CL, genetically modified Populus sp.

C. Microarray Loop #3: Ptri_2, unpretreated Populus sp.; 7‐1 and 7‐2, genetically modified Populus sp., downregulated for cellulose levels.

D. Two‐dimensional scatterplot of the first two principal components: blue squares, Loop #2; orange circles, Loop #1; green triangles, Loop #3. Principal components analysis (PCA) plot was compiled in JMP Genomics (SAS Institute, Cary, NC, USA).

Summary of the transcriptional response to complex polysaccharides

When comparing the global gene transcription patterns of C. saccharolyticus grown on model plant polysaccharides, crystalline cellulose triggered the largest transcriptional response, relative to the other carbohydrates tested. Approximately two‐third of the annotated open reading frames (ORFs) in the C. saccharolyticus genome responded for the contrasts between cellulose and the hemicelluloses: glucomannan, pectin or xylan. For example, 817 ORFs were upregulated and 900 downregulated during growth on crystalline cellulose when compared with xylan (Table S2). In addition, the global gene transcription profile of crystalline cellulose was also significantly different from other plant polysaccharides, as demonstrated by principal components analysis (Fig. 2D) and two‐way hierarchal clustering (Fig. S1). While crystalline cellulose induced the greatest physiological response among carbohydrates tested, C. saccharolyticus also responded selectively to hemicellulose with around 1/4 to 1/7 of genes from the C. saccharolyticus genome up‐ or downregulated in comparisons between glucomannan, pectin and xylan (Table S2).

Insights into how C. saccharolyticus responds to purified plant biomass polysaccharides are useful in discerning its response to different plant biomasses. Major gene categories responding to the various purified plant polysaccharides are summarized in Fig. 3. This list includes extracellular enzymes that were highly upregulated on either cellulose or xylan (Table 1), ABC transporters (Table S3), intracellular enzymes (Table S4) and metabolic enzymes (Table S5) that were selectively upregulated on either cellulose, xylan, KGM or pectin.

Figure 3.

Figure 3

Representation of polysaccharide‐responsive genes from C. saccharolyticus. Each side of the hexagon corresponds to functional groupings of relevant genes. Colour blocks in inner rings indicate upregulation of genes within functional categories. Inner ring colours correspond to crystalline cellulose (outermost, blue); xylan (second ring, red); konjac glucomannan (third ring, green); and pectin (innermost ring, purple). For gene locus numbers in each functional category, refer to Table S6.

Table 1.

Extracellular Carbohydrate Active Enzymes from Caldicellulosiruptor saccharolyticus

Fold changea
Locus tag Annotation/Activity SigP TM AA CAZy Family Cellulose versus Xylan versus
KGM P X CC KGM P
Csac_0408 α‐Amylase Y N 514 GH13 4.3
Csac_0678 Endoglucanase/endo‐1,4‐β‐xylanase Y N 756 GH5, CBM28 12.8 11.4 8.8
Csac_0689 Pullulanase Y N 1136 CBM41, CBM48,GH13, CBM20 10.7 2.4 4.4
Csac_0696 Endo‐1,4‐β‐xylanase Y N 686 2× CBM22, GH10 148.6 35.7 31.3
Csac_0719 Acetyl xylan esterase N Y 299 CE4
Csac_1076 Endo‐1,4‐β‐glucanase (CelA) Y N 1751 GH9, 3× CBM3, GH48 2.2 7.4 3.3 2.2
Csac_1077 Endo‐1,4‐β‐glucanase/β‐1,4‐mannanase; endo‐1,4‐β‐xylanase (ManA) Y N 1303 GH5, 2× CBM3, GH44 60.9 89.3 35.1 2.6
Csac_1078 Endo‐1,4‐β‐xylanase/endo‐1,4‐β‐glucanase; β‐1,4‐glucomannanase (CelB) Y N 1039 GH10, CBM3, GH5 3.3 2.7
Csac_1079 Endo‐1,4‐β‐glucanase (CelC) Y N 1127 GH9, 3× CBM3 8.6 8.4 4.8
Csac_1081 Protein α‐mannosyltransferase N Y 565 GT39 2.9
Csac_1085 Endoglucanase/xyloglucanase Y N 931 GH74, CBM3 2.8
Csac_1560 Endo‐1,5‐α‐L‐arabinase Y N 488 GH43 20.8 2.7 5.8
Csac_2009 Acetyl xylan esterase Y N 258 CE4
Csac_2410 Endo‐1,4‐β‐xylanase (XynE) Y N 700 2 × CBM22, GH10 5.6 4.3 2.3
Csac_2411 α‐L‐Arabinofuranosidase (XynF) Y N 1347 GH43, CBM22, GH43, CBM6 2.3 2.5 1.9
Csac_2371 Acetyl xylan esterase Y N 322 CE4
Csac_2519 Carbohydrate binding protein Y N 628 CBM32
Csac_2528 Endoglucanase Y N 611 GH5 2.8
Csac_2722 Hypothetical protein/carbohydrate binding Y N 2593 GHnc 3.8

SigP, signal peptide; TM, transmembrane domain; AA, amino acid length; CC, crystalline cellulose; KGM, konjac glucomannan; P, pectin; X, xylan.

a. Fold change values are calculated from log2 ratios of crystalline cellulose or xylan versus other conditions listed in the columns below. Grey shading indicates statistical significance.

Overall, among all the candidate genetic markers of bioavailability, there are five upregulated, carbohydrate‐responsive loci that consist of CAZymes, their neighbouring ABC transporter and often metabolic enzymes, which serve as promising candidates to probe for the bioavailability of crystalline cellulose (Csac_0678, Csac_0679‐Csac_0681; GDL, Csac_1028‐Csac_1032), glucomannan (Csac_0294, Csac_0296, Csac_0297‐Csac_0301) and pectin (Csac_0354‐Csac_0356, Csac_0358‐Csac_0361). An ABC transporter that specifically responds to birchwood xylan (Csac_2692‐Csac_2694, 2696), but not oat spelt xylan (VanFossen et al., 2009), was also identified. In addition to enzymes and carbohydrate transporters, nitrogen metabolism loci were also upregulated in response to growth on crystalline cellulose (Fig. 3, Table S6). Moving forwards, the identified loci were used as probes to identify the bioavailability of polysaccharides in plant biomasses that were either chemically pretreated or genetically modified.

Transcriptional response to plant biomass

As discussed above, the transcriptome of C. saccharolyticus was highly responsive to purified forms of plant biomass‐related polysaccharides as growth substrates, especially crystalline cellulose (see Fig. 3). The next step was to determine whether the bacterium's transcriptome reflected differences in recalcitrance and carbohydrate availability between DAP and unpretreated biomass feedstocks (Loop #2, Fig. 2B). In addition to the biomasses discussed above, an experimental loop was designed to look at genetically altered Populus species that were modified to reduce the amount of cellulose produced (Loop #3, Fig. 2C). The global transcriptional response of C. saccharolyticus to all biomass substrates tested clustered together with crystalline cellulose, but distinctly from xylan, pectin and glucomannan when using principal components analysis (Fig. 2D) or hierarchal clustering (Fig. S1). Furthermore, quantitative saccharification data also identified glucans as contributing the most to mass loss (Fig. 1B) during growth. Because the global transcriptional response of C. saccharolyticus during growth on crystalline cellulose resembles that of the response to plant biomass, crystalline cellulose appears to be overwhelmingly responded to by C. saccharolyticus, even in heterogeneous plant biomass. A summary of functional groups of genes upregulated in all plant biomass contrasts is found in Table 4.

Table 4.

Characteristics of transcriptional response of C. saccharolyticus to selected plant biomasses

graphic file with name MBT2-10-1546-g005.jpg

While plant biomasses are a complex matrix of the same essential components, i.e. lignin, cellulose and hemicellulose, the hypothesis proposed here is that subtle compositional differences in the plant cell walls (naturally or through chemical pretreatment or genetic modification) should elicit detectable and differentiating transcriptional responses during degradation by C. saccharolyticus. Supporting this assumption, the number of genes whose expression levels changed by twofold or more was, as expected, significantly lower for the plant biomass contrasts, with at most 1.6% of total genes from the C. saccharolyticus genome responding (DAP versus lignin‐reduced Populus, Table 2). However, certain signatures were apparent that corresponded with chemical pretreatment or genetic modifications to which the various biomasses were subjected.

Table 2.

Transcriptionally responsive ORFs (≥ twofold) for each biomass tested.a , b

as4CL Ptri aPTD aSWG
as4CL 3 24 6
Ptri 21 28 3
aPTD 19 14 12
aSWG 30 2 26

as4CL, lignin‐reduced Populus trichocarpa; Ptri, wild type P. trichocarpa; aPTD, dilute acid‐pretreated Populus trichocarpa x deltoides; aSWG, dilute acid‐pretreated switchgrass.

a. log10 p‐value ≥ 5.59 used for statistical significance.

b. Fold changes are read as the treatment in columns versus the treatment in rows.

Effect of dilute acid pretreatment (DAP)

As expected, we observed that DAP increased the biosolubilization of Populus by C. saccharolyticus from 11.5% (wild‐type) to 19.3% (DAP Populus) mass loss (Fig. 1B). Surprisingly, only 1.6% of genes from the C. saccharolyticus genome responded significantly to the differences between DAP and wild‐type Populus (Table 2). Given the chemical modifications to biomass during DAP, we expected that genes involved in hydrolysis or metabolism of simpler carbohydrates will be upregulated. The reduced recalcitrance of DAP Populus in comparison with wild type was confirmed with the upregulation of a monosaccharide ABC transporter (Csac_0240‐0242). In addition, we postulate that cellulose is now more bioavailable, as genes from the glutamate synthase locus and a predicted secreted protein (Csac_1052) were also upregulated, similar to the response observed for crystalline cellulose (Table S7).

Genes upregulated on unpretreated wild‐type Populus should reflect the recalcitrance of the tissue. Indeed, some markers of nutritional stress are upregulated during growth on wild type Populus, including annotated iron and iron sulfur proteins (Csac_0445, rubrerythrin; Csac_1990, rubredoxin), which have also been observed to be upregulated during stress by related clostridia (Hillmann et al., 2006; Venkataramanan et al., 2015). Aside from stress, stimulation of certain genes reflected the heterogeneity of unpretreated biomass. Genes corresponding to hemicellulose ABC transporters were upregulated (Csac_0297 and Csac_2696, respectively, see Tables S3 and S6), supporting quantitative saccharification data (Fig. 1B) that hemicellulose is bioavailable in wild type Populus. Genes encoding a putative GH20 family enzyme also responded; these were also upregulated on hemicelluloses in Loop #1 (Csac_2538, Tables S4 and S6). Additionally, xylose metabolism genes were upregulated, including a xylose isomerase (Csac_1154), consistent with the bacterium's hydrolysis and metabolism of hemicellulose components in the unpretreated biomass.

Aside from recalcitrance, the differential response of C. saccharolyticus to both DAP biomass types (switchgrass versus poplar) should reflect the previously observed differences in glucan and xylan composition (Fig. 1B) of the respective biomass. As expected, the largest fold changes with respect to DAP switchgrass centred on xylan hydrolysis and metabolism with genes upregulated for the transport (Sector 5, Fig. 4; Csac_2412, Csac_2419, Csac_2696) and metabolism of xylooligosaccharides (Csac_1154, Table S7). These results from the contrast between the two DAP samples confirm quantitative saccharification data (Table S1), demonstrating that more xylan is bioavailable in DAP switchgrass compared with DAP Populus and that the presence of both cellulose and xylan triggers a stronger response in the xylan degradation locus (XDL; Sector 5, Fig. 4), compared with cellulose or xylan alone (Table S7).

Figure 4.

Figure 4

Heat plot comparing plant biomasses utilized by C. saccharolyticus. From outside to inside: aSWG, dilute acid‐pretreated switchgrass; aPTD, dilute acid‐pretreated Populus sp.; as4CL, lignin‐reduced genetically modified Populus sp.; Ptri ‐1 and Ptri‐2, Populus sp.; 7‐1 and 7‐2, cellulose‐reduced Populus sp. Sector 1, Csac_0292‐0294, Csac_0296‐Csac_0299; Sector 2, Csac_0389‐Csac_0402; Sector 3, Csac_0678‐Csac_0681; Sector 4, Csac_1076‐1080, Csac_1085, Csac_1091; Sector 5, Csac_2404‐Csac_2420. Gene loci included that are ABC transporters or glycoside hydrolases are indicated by blue and orange shading in the fifth ring. LSMeans values for genes represented here can be found in Table S7.

Response to genetically modified Populus

We also sought to determine whether C. saccharolyticus would continue to prove useful as a microbial assay probing for differences in the bioavailability of polysaccharides between unpretreated biomass and genetically modified tissue. Biomasses with differing xylan, lignin and cellulose levels were assayed (Table S1), including Populus tissue with reduced levels of either lignin (as4CL) or cellulose (7‐1 and 7‐2). When comparing the transcriptional response of C. saccharolyticus to lignin‐reduced tissue versus wild type, we expected to observe genes responding similar to those observed in comparison of less‐recalcitrant DAP Populus with wild type.

Interestingly, while both lignin‐reduced and DAP Populus have reduced recalcitrance, the differential response of C. saccharolyticus grown on lignin‐reduced versus wild type Populus was in contrast to the comparison of DAP Populus versus wild type. Polysaccharides should be present in the lignin‐reduced Populus tissues that are absent from DAP Populus as a result of chemical hydrolysis during DAP. Strong upregulation of mannan metabolism genes (Sector 1, Fig. 4) and a xylan‐responsive ABC transporter gene locus (Csac_2692‐2694, 2696, Table S7) supports this assertion. Furthermore, higher levels of lignin‐reduced Populus biomass was solubilized by C. saccharolyticus (Fig. 1A), with a larger proportion of xylan solubilized in comparison with wild type (Fig. 1B).

Genetically modified biomass with lowered cellulose content (Populus sp. ‘7‐1’ and ‘7‐2’) was then used to determine whether C. saccharolyticus could distinguish between other genetic modifications related to polysaccharide abundance and recalcitrance. Similar to the earlier comparisons between genetically modified and unpretreated Populus, modest changes in gene expression were observed, with < 4% of total genes from the C. saccharolyticus genome responding to a reduction in the cellulose content of the biomass. The number of genes up‐ or downregulated also increased with the severity of cellulose reduction when compared with wild type (Table 3), and we expected to observe less cellulose‐responsive loci upregulated. The most striking differences were observed from the response of C. saccharolyticus to the most cellulose‐reduced tissue (7‐2, Table S1). Accordingly, some cellulose‐responsive genes were downregulated, including the genetic locus, Csac_0678‐Csac_0681 (Sector 3, Fig. 4), which includes cellulose‐responsive endoglucanase and ABC transporter. More so than upregulation of the GDL, this locus (Tables S6 and S7) appears to be a better indicator of the bioavailability of cellulose as detected by C. saccharolyticus.

Table 3.

Transcriptionally responsive ORFs (≥ twofold) for each biomass tested.a , b

Ptri 7‐1 7‐2
Ptri 56 62
7‐1 10 17
7‐2 22 20

Ptri, wild type Populus trichocarpa; 7‐1, moderately cellulose‐reduced P. trichocarpa; 7‐2, severely cellulose‐reduced P. trichocarpa.

a. log10 p‐value ≥ 5.36 used for statistical significance.

b. Fold changes are read as the treatment in columns versus the treatment in rows.

Levels of xylan increased in the genetically modified tissue as cellulose was reduced (Table S1), and this appears to have also increased the recalcitrance of the cellulose‐reduced tissue (7‐1 and 7‐2). Most xylan‐responsive genes were repressed in response to growth on cellulose‐reduced tissue (7‐2), including enzymes and ABC transporters from the XDL (Sector 5, Fig. 4). Other polysaccharide‐responsive ABC transporters were upregulated instead, such as the predicted glucomannan transporter (Sector 1, Fig. 4: Csac_0297‐0301), an ABC transporter cluster with an unknown preferred substrate (Sector 2, Fig. 4: Csac_0391‐0394) and an α‐glucan ABC transporter (Table S3: Csac_0427‐0431).

Additional genetic loci that can serve as indicators of nutritional stress due to increased recalcitrance include α‐glucan transport/metabolism and chemotaxis. Turnover of stored α‐glucan reserves can be used as indicators of biomass recalcitrance, as the microbe will need to rely on previously stored carbohydrates to support growth. Comparing the most recalcitrant cellulose‐reduced biomass with wild type, many enzymes upregulated are involved in α‐glucan hydrolysis GH family 13, 15 and GT family 35 (Csac_0130, Csac_0203, Csac_0408, Csac_0426 and Csac_0429, see Table S7). In contrast, genes involved in the synthesis of glycogen were downregulated, supporting the assumption that the microbe is relying on energy stores for growth. Additionally, a predicted chemotaxis cluster was also upregulated in comparison with wild type (Csac_0811‐0812, 0814, 0816, Table S7). Previous reports identified the upregulation of homologous chemotaxis clusters in response to crystalline cellulose in C. bescii and C. kronotskyensis, but not C. saccharolyticus (Zurawski et al., 2015). In cases of extreme recalcitrance, as seen here, it appears that nutritional stress serves as an alternate signal for the genetic regulation of C. saccharolyticus chemotaxis genes (Table S7).

Comparison between strategies to reduce biomass recalcitrance

Potential insights into the bioavailability of carbohydrates and recalcitrance were next examined for the transcriptional response of C. saccharolyticus to DAP and lignin‐reduced Populus, to ascertain any differences arising from chemical pretreatment and genetic modification. Because both tissues are less recalcitrant, we expected to observe differential regulation of polysaccharide‐responsive genes and not the previously identified stress loci. Surprisingly, there were more differences between DAP and lignin‐reduced Populus, which are genetically similar, than DAP switchgrass and lignin‐reduced Populus, which compares biomass across species. Genes found to be upregulated in response to lignin‐reduced Populus were indicative of the diversity of carbohydrates, primarily hemicellulose, left in unpretreated, genetically modified tissue. Gene loci previously identified as markers for the bioavailability of (gluco‐)mannan (Csac_0296‐Csac_0301; Sector 1, Fig. 4) and xylan (Csac_1154, Csac_2694‐Csac_2696; Table S7) were upregulated. Additional transporters previously tied to xylan transport (Zurawski et al., 2015) were also upregulated, including transporters from the XDL (Csac_2412; Csac_2417‐Csac_2419; Sector 5, Fig. 4). Besides ABC transporters, a resistance, nodulation and division (RND)‐type transporter (Csac_1474) was upregulated. This gene was also upregulated on both glucomannan and pectin (Table S7). Proteins containing this domain (MMPL, PF03176) often have no assigned function, although in a related clostridial species, C. acetobutylicum, a homologue of Csac_1474 was observed to be upregulated in response to fermentation products such as butanol (Schwarz et al., 2012), acetate and butyrate (Alsaker et al., 2010).

In contrast, the differential response to DAP Populus included upregulation of cellulose‐responsive enzymes in the GDL (Csac_1077‐Csac_1080) and both glutamate synthase clusters (Table 1). Other previously identified enzymes involved with cellulose hydrolysis and metabolism were equally induced by both DAP and lignin‐reduced Populus. Given the broad substrate preference of C. saccharolyticus, it appears that genetic modification of biomass has certain favourable attributes, as it reduces recalcitrance without deleting fermentable sugars, such as mannans and xylans. Additionally, C. saccharolyticus is able to balance its nitrogen needs better during growth on lignin‐reduced Populus biomass in comparison with DAP Populus, potentially reducing the levels of exogenous nitrogen that would need to be added through the culture medium.

Conclusions

The main features of the transcriptional responses to chemically pretreated, genetically modified and unpretreated biomasses are summarized in Table 4. Connections between the transcriptional responses of C. saccharolyticus to various carbohydrate types (cellulose, xylan, glucomannan and pectin) allude to their bioavailability in plant biomass. With < 5% of the total genome from C. saccharolyticus responding in any given comparison between plant biomass types, transcriptional data from comparisons between plant biomass‐related polysaccharides (Table S6) gave insights on how C. saccharolyticus responds to subtle compositional differences.

Chemical pretreatment improved solubilization of DAP Populus in comparison with wild type (Fig. 1) and also increased the bioavailability of cellulose in that comparison which was observed both in solubilization (Fig. 1B) and in transcriptional response (Table 4). DAP switchgrass provided more oligosaccharides for growth than wild type Populus (Fig. 1A), and genes involved in monosaccharide transport were accordingly upregulated (Table 4). However, it appears that these oligosaccharides from DAP switchgrass were readily soluble, resulting in lower biological solubilization of the insoluble biomass by C. saccharolyticus (Fig. 1A).

Comparing the response of C. saccharolyticus to DAP or genetically modified lignin‐reduced Populus (as4CL), more cellulose appears to be bioavailable in DAP Populus based on transcriptional response (Table 4). However, additional polysaccharides, such as mannan and xylan, that appear to be available in lignin‐reduced Populus are solubilized (Fig. 1B), and in addition, no nitrogen stress was apparent during growth (Table 4). Given that both biomasses were solubilized to similar extents (Fig. 1A), we propose that the genetically modified lignin‐reduced Populus tissue would be a superior biomass feedstock as it allows C. saccharolyticus to balance carbon and nitrogen needs. In comparison with genetically modified cellulose‐reduced tissue, the increased recalcitrance of cellulose‐reduced Populus (7‐1 and 7‐2) could be inferred by the downregulation of key hydrolytic loci: Csac_0678‐0680 and the XDL (Sectors 3 and 5, Fig. 4), and the upregulation of mannan metabolism genes and stress responses, chemotaxis and α‐glucan metabolism (Table 4).

In this proof‐of‐principle study, we elected to focus on two varieties of plant biomass (switchgrass and Populus) that had previously been demonstrated to support growth of C. saccharolyticus. Certainly, when considering alternate plant biomass feedstocks to support microbial growth, this system can be used to gain insights into the polysaccharides that are readily bioavailable for the microbe, in addition to highlighting other nutritional requirements for medium composition. Overall, we demonstrated the use of microbial transcriptome‐based methods for evaluating the conversion potential of unpretreated and genetically modified Populus varieties in comparison with DAP Populus and DAP switchgrass. Moving forwards, transcriptome‐based assays will become more comprehensive as additional data are generated and more is understood about the microbial biochemistry and metabolic processes of the indicator microorganism.

Experimental procedures

Microbial cultivation

Caldicellulosiruptor saccharolyticus (DSM 8903) was obtained as a freeze‐dried culture from the German Collection of Microorganisms and Cell Cultures [DSMZ (http://www.dsmz.de)]. After reanimation, C. saccharolyticus was maintained on DSMZ640 medium at 70°C with the following changes: Trypticase, FeCl3 x 6H2O, resazurin and cysteine‐HCl x H2O were omitted and 0.5% (w/v) Na2S x 9H2O was added as a reducing agent, and cellobiose was substituted with various carbon sources. Polysaccharides and biomass used include the following: crystalline cellulose (Avicel PH‐101, FMC); glucomannan (konjac); pectin (practical grade); birchwood xylan (Sigma); dilute acid‐pretreated switchgrass [Panicum virgatum, −20/+80 mesh fraction; pretreatment in a Sunds reactor at the National Renewable Energy Laboratory (NREL) (Raman et al., 2009)], dilute acid‐pretreated poplar [Populus trichocarpa x deltoides, provided by NREL (Jung et al., 2010)], P. trichocarpa and genetically modified as4CL, 7‐1 and 7‐2 P. trichocarpa (ground to 80 mesh in a Wiley mill). For the biomass microarray experiment, all polysaccharides and biomass were added at a concentration of 1 g l−1, noting that acid‐treated poplar and switchgrass were added at a wet weight. All cultures were subcultured four times on the applicable substrate in 50 ml batch cultures under N2 headspace in 125 ml serum bottles prior to inoculation for cell harvesting. Cell densities (cells per ml) were monitored using epifluorescence microscopy, as described before (VanFossen et al., 2009).

Biomass solubilization and quantitative saccharification

Biomass substrates tested in microarray Loop #2 were also used to assess the solubilization ability of C. saccharolyticus as described by Zurawski et al. (2015). Solubilization is defined here as the amount of mass loss after 7 days corrected for the amount of mass loss by abiotic (thermal) factors. Mass loss was determined as the mass difference between the biomass used to prepare cultures (0.25 g) and insoluble biomass remaining after harvest. Quantitative saccharification of selected biomass before and after solubilization studies used a modified NREL protocol as previously described (Zurawski et al., 2015).

RNA isolation and processing

Cultures (500 ml) in 1 l 45 mm diameter screw top bottles were inoculated with cells in exponential phase to a density of 1 × 106 cells ml−1. Cells were harvested when the culture reached mid‐log phase, typically between 1–4 × 107 cells ml−1, as determined by epifluorescence microscopy. In the case of biomass cultures, harvested culture was first filtered to remove insoluble plant material or polysaccharides through a coffee filter into chilled centrifuge bottles, then rapidly cooled in an ethanol‐dry ice bath, after which the cells were centrifuged at 4226 × g for 15 minutes and the cell pellet was stored at −80°C. RNA was extracted as described before (van de Werken et al., 2008) using TRIzol reagent (Invitrogen, Carlsbad, CA, USA) and columns from a RNeasy kit (Qiagen, Germantown, MD, USA). Biological repeats were used for all conditions, and total RNA was pooled prior to the reverse transcriptase reaction. For both four‐slide loop experiments, pooled total RNA was used for reverse transcription reaction with amino allyl‐labelled dUTP (Ambion, Carlsbad, CA, USA) as described in protocols devised by The Institute for Genomic Research (TIGR, ftp://ftp.jcvi.org/pub/data/PFGRC/MAIN/pdf_files/protocols/M009.pdf). Labelled cDNA was purified and conjugated to Cy3 or Cy5 reactive dyes (GE Healthcare, Marlborough, MA, USA) as described previously by TIGR for oligonucleotide microarrays (ftp://ftp.jcvi.org/pub/data/PFGRC/MAIN/pdf_files/protocols/M008.pdf). For hybridization to microarray slides, loop design was used, which requires labelling of cDNA from each experimental condition with Cy3 and Cy5 dyes, independently. Loop design allows for data from each experimental condition to be directly compared with each other, without the need for a single reference condition (Kerr and Churchill, 2001). Each microarray slide was then hybridized with Cy3‐ and Cy5‐labelled cDNA from two different experimental conditions, as seen in Fig. 2.

Transcriptomic analysis

Oligonucleotide probes representing 2679 C. saccharolyticus ORFs were designed as described before (van de Werken et al., 2008). Probes were printed in‐house on UltraGAPS slides (Corning, Oneonta, NY, USA) using a QarrayMini arrayer (Genetix, New Milton, UK). Each oligonucleotide probe was spotted five times in a random pattern. Hybridized microarray slides were imaged with a GenePix 4000B microarray scanner (Molecular Devices, Sunnyvale, CA, USA), and signal intensity for each probe after excitation at 635 and 532 nm was calculated using genepix pro (6.0; Molecular Devices) before import into JMP Genomics 4.0 (SAS Institute, Cary, NC, USA). anova, loess or quantile normalization of intensity data was used prior to applying a mixed‐effects model statistical analysis (Wolfinger et al., 2001) as described previously (Pysz et al., 2004). Genes that were differentially transcribed twofold or more and also met a Bonferroni significance cut‐off equal to or below a −log10 (p‐value) of 5.36 (Loop #1) or 5.59 (Loops #2 and 3) are defined here as being either up‐ or downregulated. Further statistical analysis was conducted using JMP Genomics, including principal components analysis and hierarchal clustering (two‐way using the Ward method).

Data for both microarray loop design experiments were deposited with the Gene Expression Omnibus (GEO) database hosted at the National Center for Biotechnology Information (http://www.ncbi.nlm.nih.gov/geo/). The microarray platform designed for C. saccharolyticus is available as accession number GPL6681. The experimental series accession numbers are as follows: GSE90445 for Loops 1, 2 and 3. Accession numbers for experimental data are as follows: GSM2401354, GSM2401355, GSM2401356 and GSM2401357 for Loop #1; GSM2401358, GSM2401359, GSM2401360 and GSM240161 for Loop #2 and GSM240162, GSM240163 and GSM240164 for Loop #3.

Conflict of Interest

None declared.

Supporting information

Fig. S1. Hierarchical clustering of the global C. saccharolyticus transcriptional response to polysaccharide or plant biomass.

Table S1. Compositional analysis of biomass feedstocks used in this study.

Table S2. Significant changes in expression > 2‐fold for each complex polysaccharide testeda,b.

Table S3. LSMeans values for ABC transporter loci.

Table S4. Transcriptional response of intracellular CAZymes to polysaccharides.

Table S5. LSMeans Values of polysaccharide responsive genes.

Table S6. Major transcriptional responses of C. saccharolyticus to purified polysaccharides.

Table S7. LSMeans values of carbohydrate utilization proteins and biomass responsive genes.

Acknowledgements

The authors wish to acknowledge Dhaval Mistry for technical assistance.

Microbial Biotechnology (2017) 10(6), 1546–1557

Funding Information

This work was supported by the BioEnergy Science Center (BESC), a U.S. Department of Energy Bioenergy Research Center supported by the Office of Biological and Environmental Research in the DOE Office of Science. JM Conway acknowledges support from a US DoEd GAANN Fellowship (P200A100004‐12).

References

  1. Alsaker, K.V. , Paredes, C. , and Papoutsakis, E.T. (2010) Metabolite stress and tolerance in the production of biofuels and chemicals: gene‐expression‐based systems analysis of butanol, butyrate, and acetate stresses in the anaerobe Clostridium acetobutylicum . Biotechnol Bioeng 105: 1131–1147. [DOI] [PubMed] [Google Scholar]
  2. Blumer‐Schuette, S.E. , Lewis, D.L. , and Kelly, R.M. (2010) Phylogenetic, microbiological, and glycoside hydrolase diversities within the extremely thermophilic, plant biomass‐degrading genus Caldicellulosiruptor . Appl Environ Microbiol 76: 8084–8092. [DOI] [PMC free article] [PubMed] [Google Scholar]
  3. Chen, F. , and Dixon, R.A. (2007) Lignin modification improves fermentable sugar yields for biofuel production. Nat Biotechnol 25: 759–761. [DOI] [PubMed] [Google Scholar]
  4. Couturier, M. , Navarro, D. , Chevret, D. , Henrissat, B. , Piumi, F. , Ruiz‐Dueñas, F.J. , et al (2015) Enhanced degradation of softwood versus hardwood by the white‐rot fungus Pycnoporus coccineus . Biotechnol Biofuels 8: 216. [DOI] [PMC free article] [PubMed] [Google Scholar]
  5. Dumitrache, A. , Akinosho, H. , Rodriguez, M. , Meng, X. , Yoo, C.G. , Natzke, J. , et al (2016) Consolidated bioprocessing of Populus using Clostridium (Ruminiclostridium) thermocellum: a case study on the impact of lignin composition and structure. Biotechnol Biofuels 9: 31. [DOI] [PMC free article] [PubMed] [Google Scholar]
  6. Fu, C. , Mielenz, J.R. , Xiao, X. , Ge, Y. , Hamilton, C.Y. , Rodriguez, M. , et al (2011) Genetic manipulation of lignin reduces recalcitrance and improves ethanol production from switchgrass. Proc Natl Acad Sci USA 108: 3803–3808. [DOI] [PMC free article] [PubMed] [Google Scholar]
  7. Gaskell, J. , Marty, A. , Mozuch, M. , Kersten, P.J. , BonDurant, S.S. , Sabat, G. , et al (2014) Influence of Populus genotype on gene expression by the wood decay fungus Phanerochaete chrysosporium . Appl Environ Microbiol 80: 5828–5835. [DOI] [PMC free article] [PubMed] [Google Scholar]
  8. Gaskell, J. , Blanchette, R.A. , Stewart, P.E. , BonDurant, S.S. , Adams, M. , Sabat, G. , et al (2016) Transcriptome and secretome analyses of the wood decay fungus Wolfiporia cocos support alternative mechanisms of lignocellulose conversion. Appl Environ Microbiol 82: 3979–3987. [DOI] [PMC free article] [PubMed] [Google Scholar]
  9. Gronenberg, L.S. , Marcheschi, R.J. , and Liao, J.C. (2013) Next generation biofuel engineering in prokaryotes. Curr Op Chem Biol 17: 462–471. [DOI] [PMC free article] [PubMed] [Google Scholar]
  10. Hillmann, F. , Fischer, R.‐J. , and Bahl, H. (2006) The rubrerythrin‐like protein Hsp21 of Clostridium acetobutylicum is a general stress protein. Arch Microbiol 185: 270–276. [DOI] [PubMed] [Google Scholar]
  11. Holtzapple, M. , Jun, J.‐H. , Ashok, G. , Patibandla, S. , and Dale, B. (1991) The ammonia freeze explosion (AFEX) process. Appl Biochem Biotechnol 28–29: 59–74. [Google Scholar]
  12. Jung, S. , Foston, M. , Sullards, M.C. , and Ragauskas, A.J. (2010) Surface characterization of dilute acid pretreated populus deltoides by ToF‐SIMS. Energy Fuels 24: 1347–1357. [Google Scholar]
  13. Kataeva, I. , Foston, M.B. , Yang, S.‐J. , Pattathil, S. , Biswal, A.K. , Ii, F.L.P. , et al (2013) Carbohydrate and lignin are simultaneously solubilized from unpretreated switchgrass by microbial action at high temperature. Energy Environ Sci 6: 2186–2195. [Google Scholar]
  14. Kerr, M.K. , and Churchill, G.A. (2001) Experimental design for gene expression microarrays. Biostatistics 2: 183–201. [DOI] [PubMed] [Google Scholar]
  15. Li, L. , Zhou, Y. , Cheng, X. , Sun, J. , Marita, J.M. , Ralph, J. , and Chiang, V.L. (2003) Combinatorial modification of multiple lignin traits in trees through multigene cotransformation. Proc Natl Acad Sci USA 100: 4939–4944. [DOI] [PMC free article] [PubMed] [Google Scholar]
  16. Liao, J.C. , Mi, L. , Pontrelli, S. , and Luo, S. (2016) Fuelling the future: microbial engineering for the production of sustainable biofuels. Nat Rev Microbiol 14: 288–304. [DOI] [PubMed] [Google Scholar]
  17. Loqué, D. , Scheller, H.V. , and Pauly, M. (2015) Engineering of plant cell walls for enhanced biofuel production. Curr Op Plant Biol 25: 151–161. [DOI] [PubMed] [Google Scholar]
  18. Pauly, M. , and Keegstra, K. (2010) Plant cell wall polymers as precursors for biofuels. Curr Opin Plant Biol 13: 304–311. [DOI] [PubMed] [Google Scholar]
  19. Pysz, M.A. , Conners, S.B. , Montero, C.I. , Shockley, K.R. , Johnson, M.R. , Ward, D.E. , and Kelly, R.M. (2004) Transcriptional analysis of biofilm formation processes in the anaerobic, hyperthermophilic bacterium Thermotoga maritima . Appl Environ Microbiol 70: 6098–6112. [DOI] [PMC free article] [PubMed] [Google Scholar]
  20. Raman, B. , Pan, C. , Hurst, G.B. , Rodriguez, M. Jr , McKeown, C.K. , Lankford, P.K. , et al (2009) Impact of pretreated switchgrass and biomass carbohydrates on Clostridium thermocellum ATCC 27405 cellulosome composition: a quantitative proteomic analysis. PLoS ONE 4: e5271. [DOI] [PMC free article] [PubMed] [Google Scholar]
  21. Schwarz, K.M. , Kuit, W. , Grimmler, C. , Ehrenreich, A. , and Kengen, S.W.M. (2012) A transcriptional study of acidogenic chemostat cells of Clostridium acetobutylicum – Cellular behavior in adaptation to n‐butanol. J Biotechnol 161: 366–377. [DOI] [PubMed] [Google Scholar]
  22. Shih, P.M. , Liang, Y. , and Loqué, D. (2016) Biotechnology and synthetic biology approaches for metabolic engineering of bioenergy crops. Plant J 87: 103–117. [DOI] [PubMed] [Google Scholar]
  23. Singh, S. , Cheng, G. , Sathitsuksanoh, N. , Wu, D. , Varanasi, P. , George, A. , et al (2015) Comparison of different biomass pretreatment techniques and their impact on chemistry and structure. Front Energy Res 2: 62. [Google Scholar]
  24. Studer, M.H. , Demartini, J.D. , Davis, M.F. , Sykes, R.W. , Davison, B. , Keller, M. , et al (2011) Lignin content in natural Populus variants affects sugar release. Proc Natl Acad Sci USA 108: 6300–6305. [DOI] [PMC free article] [PubMed] [Google Scholar]
  25. Sun, S. , Sun, S. , Cao, X. , and Sun, R. (2016) The role of pretreatment in improving the enzymatic hydrolysis of lignocellulosic materials. Bioresour Technol 199: 49–58. [DOI] [PubMed] [Google Scholar]
  26. Tao, L. , Aden, A. , Elander, R.T. , Pallapolu, V.R. , Lee, Y.Y. , Garlock, R.J. , et al (2011) Process and technoeconomic analysis of leading pretreatment technologies for lignocellulosic ethanol production using switchgrass. Bioresour Technol 102: 11105–11114. [DOI] [PubMed] [Google Scholar]
  27. Timell, T.E. (1967) Recent progress in the chemistry of wood hemicelluloses. Wood Sci Technol 1: 45–70. [Google Scholar]
  28. Tucker, M. , Farmer, J. , Keller, F. , Schell, D. , and Nguyan, Q. (1998) Comparison of yellow poplar pretreatment between NREL digester and sunds hydrolyzer. Appl Biochem Biotechnol 70–72: 25–35. [Google Scholar]
  29. Van Acker, R. , Leplé, J.‐C. , Aerts, D. , Storme, V. , Goeminne, G. , Ivens, B. , et al (2014) Improved saccharification and ethanol yield from field‐grown transgenic poplar deficient in cinnamoyl‐CoA reductase. Proc Natl Acad Sci USA 111: 845–850. [DOI] [PMC free article] [PubMed] [Google Scholar]
  30. VanFossen, A.L. , Verhaart, M.R. , Kengen, S.M. , and Kelly, R.M. (2009) Carbohydrate utilization patterns for the extremely thermophilic bacterium Caldicellulosiruptor saccharolyticus reveal broad growth substrate preferences. Appl Environ Microbiol 75: 7718–7724. [DOI] [PMC free article] [PubMed] [Google Scholar]
  31. VanFossen, A.L. , Ozdemir, I. , Zelin, S.L. , and Kelly, R.M. (2011) Glycoside hydrolase inventory drives plant polysaccharide deconstruction by the extremely thermophilic bacterium Caldicellulosiruptor saccharolyticus . Biotechnol Bioeng 108: 1559–1569. [DOI] [PubMed] [Google Scholar]
  32. Venkataramanan, K.P. , Min, L. , Hou, S. , Jones, S.W. , Ralston, M.T. , Lee, K.H. , and Papoutsakis, E.T. (2015) Complex and extensive post‐transcriptional regulation revealed by integrative proteomic and transcriptomic analysis of metabolite stress response in Clostridium acetobutylicum . Biotechnol Biofuels 8: 81. [DOI] [PMC free article] [PubMed] [Google Scholar]
  33. van de Werken, H.J. , Verhaart, M.R. , VanFossen, A.L. , Willquist, K. , Lewis, D.L. , Nichols, J.D. , et al (2008) Hydrogenomics of the extremely thermophilic bacterium Caldicellulosiruptor saccharolyticus . Appl Environ Microbiol 74: 6720–6729. [DOI] [PMC free article] [PubMed] [Google Scholar]
  34. Whitney, S.E.C. , Brigham, J.E. , Darke, A.H. , Reid, J.S.G. , and Gidley, M.J. (1998) Structural aspects of the interaction of mannan‐based polysaccharides with bacterial cellulose. Carbohydr Res 307: 299–309. [Google Scholar]
  35. Wolfinger, R.D. , Gibson, G. , Wolfinger, E.D. , Bennett, L. , Hamadeh, H. , Bushel, P. , et al (2001) Assessing gene significance from cDNA microarray expression data via mixed models. J Comput Biol 8: 625–637. [DOI] [PubMed] [Google Scholar]
  36. Xiao, C. , and Anderson, C.T. (2013) Roles of pectin in biomass yield and processing for biofuels. Front Plant Sci 4: 67. [DOI] [PMC free article] [PubMed] [Google Scholar]
  37. Yee, K.L. , Rodriguez, M. Jr , Thompson, O.A. , Fu, C. , Wang, Z.‐Y. , Davison, B.H. , and Mielenz, J.R. (2014) Consolidated bioprocessing of transgenic switchgrass by an engineered and evolved Clostridium thermocellum strain. Biotechnol Biofuels 7: 75. [DOI] [PMC free article] [PubMed] [Google Scholar]
  38. Zurawski, J.V. , Conway, J.M. , Lee, L.L. , Simpson, H. , Izquierdo, J.A. , Blumer‐Schuette, S. , et al (2015) Comparative analysis of extremely thermophilic Caldicellulosiruptor species reveals common and differentiating cellular strategies for plant biomass utilization. Appl Environ Microbiol 81: 7159–7170. [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Fig. S1. Hierarchical clustering of the global C. saccharolyticus transcriptional response to polysaccharide or plant biomass.

Table S1. Compositional analysis of biomass feedstocks used in this study.

Table S2. Significant changes in expression > 2‐fold for each complex polysaccharide testeda,b.

Table S3. LSMeans values for ABC transporter loci.

Table S4. Transcriptional response of intracellular CAZymes to polysaccharides.

Table S5. LSMeans Values of polysaccharide responsive genes.

Table S6. Major transcriptional responses of C. saccharolyticus to purified polysaccharides.

Table S7. LSMeans values of carbohydrate utilization proteins and biomass responsive genes.


Articles from Microbial Biotechnology are provided here courtesy of Wiley

RESOURCES