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Applied and Environmental Microbiology logoLink to Applied and Environmental Microbiology
. 2014 Sep;80(18):5828–5835. doi: 10.1128/AEM.01604-14

Influence of Populus Genotype on Gene Expression by the Wood Decay Fungus Phanerochaete chrysosporium

Jill Gaskell a, Amber Marty b, Michael Mozuch a, Philip J Kersten a, Sandra Splinter BonDurant c, Grzegorz Sabat c, Ali Azarpira d, John Ralph d, Oleksandr Skyba e, Shawn D Mansfield e, Robert A Blanchette f, Dan Cullen a,
Editor: A A Brakhage
PMCID: PMC4178610  PMID: 25015893

Abstract

We examined gene expression patterns in the lignin-degrading fungus Phanerochaete chrysosporium when it colonizes hybrid poplar (Populus alba × tremula) and syringyl (S)-rich transgenic derivatives. A combination of microarrays and liquid chromatography-tandem mass spectrometry (LC-MS/MS) allowed detection of a total of 9,959 transcripts and 793 proteins. Comparisons of P. chrysosporium transcript abundance in medium containing poplar or glucose as a sole carbon source showed 113 regulated genes, 11 of which were significantly higher (>2-fold, P < 0.05) in transgenic line 64 relative to the parental line. Possibly related to the very large amounts of syringyl (S) units in this transgenic tree (94 mol% S), several oxidoreductases were among the upregulated genes. Peptides corresponding to a total of 18 oxidoreductases were identified in medium consisting of biomass from line 64 or 82 (85 mol% S) but not in the parental clone (65 mol% S). These results demonstrate that P. chrysosporium gene expression patterns are substantially influenced by lignin composition.

INTRODUCTION

Efficient and complete natural degradation of woody plant cell walls is generally ascribed to certain wood decay basidiomycetes. Collectively referred to as white rot fungi, these unique microbes are capable of degrading all cell wall components, including hemicelluloses, cellulose, and the more recalcitrant lignin (1). Commonly inhabiting woody debris and forest litter, these fungi play an important role in carbon cycling. To degrade and fully mineralize cell wall polymers, the model white rot fungus Phanerochaete chrysosporium employs a complex array of extracellular oxidative and hydrolytic systems (2).

Analysis of the P. chrysosporium genome revealed 177 putative glycoside hydrolases (3), most of which are likely involved in the degradation of cellulose or hemicellulose. On the basis of sequence comparisons, these enzymes were assigned to 45 glycoside hydrolase (GH) families (4; http://www.cazy.org/). Beyond GHs, considerable evidence supports a role for cellobiose dehydrogenase (CDH) and lytic polysaccharide monooxygenases (LPMOs) in the oxidative attack on cellulose and hemicellulose (58). Consistent with this view, elevated transcript levels and proteins corresponding to various GHs, CDH, and LPMOs have been observed in medium containing microcrystalline cellulose (912) and ground Populus grandidentata (13), Quercus rubra (1416), Pinus strobus (17), or Pinus nigra (18).

Woody feedstocks are increasingly viewed as sources for high-value, low-molecular-weight products (19). However, their conversion to simple, fermentable carbohydrates remains a formidable barrier, and harsh chemical treatments are typically employed to enhance substrate accessibility and lignin removal. In recent years, lignin composition in poplar has been modified by gene misregulation, and, in one case, altered lignin improved the efficiency of saccharification and fermentation to ethanol (20). The enzymatic mechanisms underlying lignin degradation remain uncertain, but recent analysis suggests that transgenic poplar with increased ratios of syringyl to guaiacyl lignin monomers are relatively more resistant to fungal attack (21).

It is generally thought that lignin depolymerization is catalyzed by an array of oxidative enzymes, especially lignin peroxidase (LiP), manganese peroxidase (MnP), and versatile peroxidase (VP). Recent genome investigations reveal that all efficient lignin degraders possess some combination of these enzymes, all of which are class II members of the plant-fungal-prokaryotic peroxidase superfamily (22, 23). Ligninolytic peroxidases, together with auxiliary enzymes, have been classified into 10 families (24). Of these, class II peroxidases (family AA2), various glucose-methanol-choline (GMC) oxidoreductases (AA3), copper radical oxidases (CROs; AA5), benzoquinone reductases (AA6), and the aforementioned LPMOs (AA9) are expressed in P. chrysosporium cultures (reviewed in reference 25). Owing to the insolubility of the substrate, little is known of the influence of native lignin on gene expression. However, the secretomes of cultures amended with sulfonated lignin (11) or vanillin (2628), a probable degradation product, have been reported. Aldehyde dehydrogenases (AADs), CDH, copper radical oxidases, glutathione transferases, and benzoquinone reductases, all implicated in transformations of aromatic metabolites, were identified in these submerged cultures. Characterization of proteins extracted from colonized wood blocks has been more challenging, but Ravalason and coworkers successfully identified a copper radical oxidase in P. nigra wood chips decayed by P. chrysosporium strain CIRM-BRFM41 (18).

Substrate preference among certain wood decay fungi is well established (1, 29). Numerous studies involving defined medium have demonstrated the substantial influence of substrate on P. chrysosporium gene expression (reviewed in references 30 and 31). Differential transcriptional regulation and shifting secretome patterns have also been observed in comparisons of defined-medium cultures to cultures containing a woody substrate (13, 15, 18), and comparisons of white pine (Pinus strobus) to bigtooth aspen (Populus grandidentata) also showed significant modulation of gene expression in response to highly divergent substrates (17). In this study, we have examined gene expression in hybrid poplar lines with drastically different lignin compositions, a trait of considerable importance to many industrial processes.

MATERIALS AND METHODS

Culture conditions and characterization.

RNA and protein were obtained from P. chrysosporium strain RP78 (Forest Mycology Center, Forest Products Laboratory) grown in Highley's basal salt medium (32) containing 0.5% (wt/vol) glucose (Glc) or Wiley-milled (1-mm mesh) wood. For each of the three wood samples (parental hybrid clone line P717, transgenic line 82, and transgenic line 64) multiple branches were harvested, debarked, and dried. These samples were derived from independent trees that were clonally replicated and grown in a greenhouse for 2 years. The milled material was used as is, i.e., without solvent extraction. Two-liter Erlenmeyer flasks contained 250 ml of medium and were inoculated with approximately 107 P. chrysosporium spores scraped from the surface of YMPG (yeast extract, malt extract, peptone, glucose) agar. Cultures were incubated for 5 days on a rotary shaker (150 rpm) at 37°C. Carbohydrate and lignin composition levels of wood samples have been reported previously (21). Notably, line 64, line 82, and parental line P717 had similar overall lignin contents but feature approximately 94 mol%, 85 mol%, and 65 mol% syringyl units, respectively.

For RNA, mycelia from triplicate cultures were collected by filtration through Miracloth (Calbiochem, EMD Biosciences, Gibbstown, NJ), squeeze dried, and snap-frozen in liquid nitrogen. Pellets were stored at −80°C until use. For mass spectroscopic analysis, culture filtrates were stored at −20°C before use.

Expression microarrays.

P. chrysosporium Roche NimbleGen array designs are available under platform GPL18011 within the Gene Expression Omnibus (GEO; http://www.ncbi.nlm.nih.gov/geo/index.cgi). The arrays feature 9,927 gene targets and differ from the previously used design platform GPL8022 (10, 13, 17, 33) by the elimination of repetitive elements and the addition of 25 open reading frames (protein target identification [ID] numbers 150002 to 150027).

Total RNA was purified from frozen mycelial pellets, converted to Cy3-labeled cDNA, hybridized to microarrays, and scanned as described previously (13). The arrays used in these experiments were scanned on an Axon 4000B scanner (Molecular Dynamics), and data were extracted using NimbleScan, version 2.4. Quantile normalization and robust multiarray averaging (RMA) (34) were applied to the raw data using DNASTAR ArrayStar, version 4 (Madison, WI). Expression levels were based on log2 signals, and significant differences in expression were determined using a moderated t test (35) with a false discovery rate (FDR) (36) threshold set at a P value of <0.05.

Mass spectrometry.

Soluble extracellular protein was precipitated from culture filtrates by direct addition of solid trichloroacetic acid (TCA) to 10% (wt/vol), and trypsin-generated peptides were analyzed by nano-liquid chromatography-tandem mass spectrometry (nano-LC-MS/MS) using an Agilent 1100 Nanoflow system (Agilent, Palo Alto, CA) connected to a hybrid linear trap quadrupole-Orbitrap mass spectrometer (LTQ-Orbitrap; Thermo Fisher Scientific, San Jose, CA) equipped with a nanoelectrospray ion source as described previously (13). Using protein databases for P. chrysosporium (BestModels_2.0 [http://jgi.doe.gov/whiterot]), the MS/MS spectra were analyzed using an in-house Mascot search engine (version 2.2.07; Matrix Science, London, United Kingdom). Mascot searches were done with a fragment ion mass tolerance of 0.6 Da, parent ion tolerance of 15 ppm, and methionine oxidation as variable modification. Scaffold (version 4; Proteome Software, Inc., Portland, OR) was used to validate MS/MS-based peptide and protein identifications. Protein identifications were accepted if they contained at least two uniquely identified peptides and if protein probabilities exceeded 95.0% as determined by the Protein Prophet algorithm (37).

Detailed information on individual gene/protein models can be directly accessed via the Joint Genome Institute (JGI) genome portal (38). The protein pages include information from the Gene Ontology (GO) database for each InterPro domain. Function or putative function was assigned when determinations were supported by direct experimental evidence or when comparisons to known proteins revealed conserved catalytic features and/or significant alignment scores (bit scores of >150) to known proteins within the SwissProt database. All other proteins were designated hypothetical.

Microarray data accession number.

The MIAME (minimum information about a microarray experiment)-compliant (39) microarray expression data were deposited in NCBI's Gene Expression Omnibus under GEO accession number GSE52922.

RESULTS

Transcriptome analysis revealed 113 genes upregulated on poplar relative to glucose-grown cultures (Fig. 1). Seventy-nine of these were upregulated in the parental hybrid, P717, and these included a wide array of glycoside hydrolases (GHs), oxidoreductases, transporters, and hypothetical proteins. With exceptions, P. chrysosporium gene signal strength on Wiley-milled P717 was positively correlated (r = 0.96, n = 9,927) (see Data Set S1 in the supplemental material) with previously reported ball-milled Populus grandidentata (17). Notable outliers included genes encoding an endoxylanase (Phach1_7045), two lytic polysaccharide monooxygenases (LPMOs; Phach1_41563 and Phach1_41125), and a class 3 lipase (Phach1_2540), all of which exhibited high signal strength and significant upregulation on P717 relative to P. grandidentata. Possibly, these differences were influenced by wood composition, but substrate pretreatment may have also played a role. The Wiley-milled material used here is more coarsely ground and less accessible to enzyme penetration than pulverized ball-milled wood.

FIG 1.

FIG 1

Distribution of 113 genes whose transcripts accumulate >2-fold (P < 0.05) in poplar relative to glucose medium. Of these, cultures containing high-syringyl lines 82 and 64 as the sole carbon sources had 11 and 15 genes, respectively, showing no significant increases in the parental line P717. Eight genes were significantly upregulated in both transgenic lines, but not in P717. Detailed results for all genes are available in Data Set S1 in the supplemental material.

Transcripts for 34 functionally diverse genes accumulated uniquely in line 82 and/or 64, but not in P717, relative to glucose (Fig. 1). Of genes upregulated in transgenic material relative to P717, none showed significant up- or downregulation in line 82. However, the line containing the highest syringyl lignin content, line 64, significantly (P < 0.05) induced 11 genes (Table 1). This group included a flavin-dependent oxidoreductase, formate dehydrogenase, formaldehyde dehydrogenase, phenylalanine ammonia lyase, and several hypothetical proteins. Furthermore, another flavin-dependent oxidoreductase (Phach1_140680) and a transporter (Phach1_138238) showed significant upregulation in line 64 relative to line 82.

TABLE 1.

P. chrysosporium genes upregulated in colonization of transgenic poplar line 82 or 64 relative to parental hybrid line P717

graphic file with name zam01814-5657-t01.jpg

a

GH, glycoside hydrolase; PAL, phenylalanine ammonia lyase; FAD-OR, favin-dependent oxidoreductases similar to salicylate monooxygenase. Hypothetical proteins Phach1_5249 and Phach1_140079 were detected in previous reports (17), and the latter protein model featured a predicted secretion signal. Transmembrane helices were predicted for Phach1_5249, Phach1_6166 and Phach1_5352.

b

P717, wild-type parental hybrid.

c

Shading highlights significant upregulation (>2-fold; P < 0.05).

d

emPAI, exponentially modified protein abundance index.

LC-MS/MS-based secretome analysis unambiguously identified 793 proteins, each defined by ≥2 unique peptides. These proteins were broadly categorized as glycoside hydrolases (70 proteins), oxidoreductases (32), auxiliary/other proteins implicated in lignocellulose degradation (14), peptidases (15), hypotheticals (343), and miscellaneous (315) (Fig. 2). Peptides corresponding to high-oxidation-potential peroxidases were not detected, but 18 oxidoreductases were found exclusively in the transgenic lines (Table 2). All of these proteins could play a direct or indirect role in the transformation and degradation of lignin metabolites. Increased levels of glycoside hydrolases in the transgenic lines (Table 3) likely reflect broad shifts in accessibility of cellulose and hemicelluloses. Polysaccharide access might be altered by lowered molecular weight and increased proportions of β-O-4 bonds associated with lignins derived from high levels of syringyl monomer (40).

FIG 2.

FIG 2

Distribution of proteins in broad functional categories. Miscellaneous proteins include those without secretion signals and homologous to abundant, known, intracellular proteins involved in central metabolism and protein synthesis. These are likely the result of hyphal lysis during cultivation. Detailed listings of all detected proteins are available in Data Set S1 in the supplemental material.

TABLE 2.

P. chrysosporium oxidoreductases upregulated in lines 82 and/or 64 but not P717a

Protein distribution and ID no. Putative function Domainb Comment (reference) Microarray signal (log2)
LC-MS/MS data (emPAI)
P717 82 64
Proteins in filtrates of line 82
    6771 Oxidoreductase PF01408 1482 1382 1289 0.119
    8211 GMC oxidoreductase AA3_2 416 425 429 0.100
    10221 Alcohol dehydrogenase PF00248 3053 3060 4084 0.234
    9149 GMC oxidoreductase, possible glucose oxidase IPR001395 Model 5′ region needs editing 2863 3010 3117 0.093
    1321 Flavin-containing monooxygenasec PF01494, PF01360 ∼PcFMO1 (28) 11700 12117 10235 0.025
Proteins in filtrates of lines 82 and 64
    133289 Aldehyde dehydrogenase PF00171 438 456 564 0.154, 0.377d
    134181 Aryl-alcohol dehydrogenase PF00248 68% identity to Phach1_11055 (53) 378 363 420 0.126, 0.252d
    3442 Oxidoreductase PF00107 Model 3′ terminus needs editing 2071 2018 2162 0.054, 0.050d
Proteins in filtrates of line 64
    133757 Formate dehydrogenase PF00389, PF02826 463 471 513 0.365
    6283 Flavin-containing monooxygenase PF00743, PF13738 1268 1293 1557 0.151
    127288 Catalase PF00199 1728 1689 1755 0.090
    7965 FAD-dependent oxidoreductase PF01360 Related to salicylate hydroxylase 1559 1055 4715 0.116
    7129 Alcohol dehydrogenase PF00107 529 586 717 0.298
    1173 Oxidoreductase PF01408 358 377 384 0.120
    10307 1,4-benzoquinone reductase AA6 1214 1091 1203 0.249
    5793 Alcohol dehydrogenase PF00107 1287 1370 1899 0.369
    1056 Oxidoreductase PF00107 2382 2684 3110 0.133
    132896 Flavin-containing monooxygenase PF00743, PF13738 1371 1486 2073 0.079
    128306 Catalase PF00199 1211 1148 1210 0.081
a

The Venn diagram in Fig. 2 shows the distribution of all detected proteins. Only proteins with ≥2 unique peptides are considered significant.

b

Pfam (http://pfam.sanger.ac.uk/), auxiliary activity families (http://www.cazy.org/Auxiliary-Activities.html), or InterPro domains (https://www.ebi.ac.uk/interpro/) are listed. See Data Set S1 in the supplemental material or individual protein pages on the JGI portal (http://genome.jgi-psf.org/Phchr1/Phchr1.home.html) for additional information.

c

Gene model extends beyond likely 3′ terminus; corrected gene equivalent to vanillin-induced protein PcFMO1 of P. chrysosporium strain ME446.

d

emPAI values for line 82 and line 64, respectively.

TABLE 3.

P. chrysosporium CAZy proteins identified in line 82 and/or 64

Protein distribution and ID no. Putative function Comment (reference) Microarray signal (log2)
LC-MS/MS data (emPAI)
P717 82 64
Proteins in filtrates of line 82
    31049 AA9 lytic polysaccharide monooxygenase C-terminal CBM1a 11,570 10,399 3,779 0.252
    4449 GH28 exopolygalacturonase Epg28B (33) 2,548 2,798 2,738 0.172
    135833 GH31 alpha-glucosidase 1,489 1,577 1,446 0.073
    121774 GH5_22 endo-beta-1,4-glucanase Probable β-1,4-glucanase (54) 1,786 1,701 1,384 0.097
    128446 GH37 neutral trehalase 1,991 2,194 1,771 0.059
Proteins in filtrates of lines 82 and 64
    138596 GH3 beta-glucosidase 6,419 6,953 3,935 0.056, 0.052b
    139732 GH10 endo-1,4-beta-xylanase 5′ CBM1 1,935 1,887 1,729 0.319, 0.212b
Proteins in filtrates of line 64
    40899 GH18 probable chitinase 5′ incomplete 1,266 1,354 1,083 0.258
    126964 GH7 exocellobiohydrolase Cel7A 1,024 1,121 1,090 0.107
    35305 GH38 alpha-mannosidase 5′ incomplete 2,776 2,948 2,916 0.040
a

CBM1, family 1 carbohydrate-binding module.

b

emPAI values for line 82 and line 64, respectively.

DISCUSSION

Our results demonstrate the influence of lignin composition on P. chrysosporium gene expression. In particular, secretome and transcriptome profiles highlight a role for various proteins in response to an increased ratio of syringyl/guaiacyl monomers in the lignin polymer. It is unclear whether similar expression patterns would be observed in solid wood under natural conditions. Presumably, Wiley mill grinding or other commercial pretreatments enhance enzyme accessibility.

Transcript accumulation in media containing ground transgenic lines as sole carbon sources identified several regulated genes, including the flavin-binding oxidoreductases Phach1_7965 and Phach1_140680. Featuring InterPro domain IPR003042 (aromatic-ring hydroxylases), these putative monooxygenases are closely related (66% identity) and feature predicted secretion signals (Table 1; see also Data Set S1 in the supplemental material). Given their structure and relatively high transcript accumulation in the high-syringyl lignin substrate (line 64), it seems probable that these enzymes are involved in the degradation of aromatic metabolites. Upregulation of formate dehydrogenase genes encoding Phach1_140211 (Table 1) and Phach1_133757 (Table 2) may be in response to formate accumulation via the glyoxylate cycle although simultaneous increases in the expression of oxalate decarboxylase were not observed as they were in earlier studies of P. chrysosporium (17) and Dichomitus squalens (41). Nevertheless, relatively high protein levels (exponentially modified protein abundance index [emPAI] value of 1.04) (see Data Set S1 in the supplemental material) of an oxalate decarboxylase (Phach1_12177) were detected in the parental line P7171. Formate can also be generated by the successive activities of methanol oxidase (Phach1_126879) and formaldehyde dehydrogenase (Phach1_127127) (42). The latter Zn-dependent enzyme is upregulated in line 64 relative to P717 (Table 1) while the former is highly expressed in all media (see Data Set S1). Glutamate dehydrogenase Phach1_133063 and ABC transporter Phach1_138238 responses are likely induced by H2O2 and lignin-derived metabolites (43), respectively, in line 64 (Table 1). Transcript accumulation of a glucoamylase (GH15; Phach1_138813) and a 1,3-β-glucosidase (GH55; Phach1_8072) cannot be easily explained by the higher ratio of syringyl/guaiacyl monomers in line 64. Neither starch nor β-1,3-glucans are significant constituents of mature wood, but the saplings used here likely contain elevated levels. Moreover, peptides corresponding to GH15s and GH55s have been detected when various white rot fungi, including P. chrysosporium, were cultivated on mature aspen sapwood (22, 23).

In addition to their regulation, genes featuring high transcript levels undoubtedly play an important role in lignocellulose degradation. For examples, genes encoding CBH2 (GH6; Phlgi_133052), CDH (AA3_1; Phlbi_11098), an LPMO (AA9; formerly GH61; Phlgi_129325), and endoglucanase EG38 (GH5; Phlbi_6458) were among the 30 highest microarray signals observed on the parental line P717 (see Data Set S1 in the supplemental material). Along these lines, the aforementioned Phlgi_126879 accumulated at very high levels in all four media. A probable ortholog of Gloeophyllum trabeum methanol oxidase (89% identical) (44), the substrate (methanol) can be produced by lignin demethoxylation, a process common to a wide range of wood decay fungi (for example, see reference 45).

In addition to transcript analysis, protein identifications support an important role for many oxidoreductases. Among the more interesting proteins detected by LC-MS/MS, two additional flavin-containing monooxygenases, Phach1_1321 and Phach1_132896, were identified in filtrates of cultures containing line 82 and line 64, respectively (Table 2). The Phach1_1321 protein is orthologous to P. chrysosporium MO1 (PcFMO1), a flavin monooxygenase previously identified in P. chrysosporium strain ME446 cultures supplemented with vanillin (28). A closely related ME446 gene, PcFMO2, corresponds to Phach1_137230 in the RP78 genome. Although we could not detect Phach1_137230 peptides in culture filtrates, its transcripts are relatively high in line 82 relative to Glc medium (2.1-fold; P < 0.02) (see Data Set S1 in the supplemental material). Interestingly, these flavin monooxygenases were, like the aforementioned Phach1_1321 and Phach1_132896, part of a family of >34 related genes, 16 of which are located on scaffold 15. In fact, eight related genes were localized to a 32-kb region which contains Phach1_140680, Phach1_7965, Phach1_1321, and Phach1_32896. Clustering of functionally related genes in P. chrysosporium had been previously observed for LiP- and CRO-encoding genes (46, 47), but regulation is not strictly coordinated among these tightly linked sequences. Thus, a putative flavin-containing monooxygenase (Phlgi_6283) is 89% identical to Phlgi_132896 and similarly expressed on line 64 (Table 2), and yet it resides on a separate scaffold.

Unambiguous protein identifications coupled with high transcript levels strongly support important roles for certain genes. For example, flavin adenine dinucleotide (FAD)-dependent oxidoreductases Phach1_7965 and Phach1_132896, alcohol dehydrogenase Phach1_5793, and benzoquinone reductase Phach1_10307 are highly expressed during growth on line 64 (Table 2). The last enzyme has been implicated in quinone cycling (48), and vanillin-induced upregulation has been observed (26). In this connection, increased transcript levels of phenylalanine ammonium lyase (Table 1) could impart enhanced biogenesis of veratryl alcohol and related aromatic compounds (49). A metabolite of P. chrysosporium, veratryl alcohol, has been implicated in ligninolysis as a diffusible oxidant or LiP stabilizer (30). We also observed high expression of alcohol dehydrogenases Phach1_10221 and Phach1_5793, both of which may participate in the reductive detoxification of various lignin-derived aldehydes (42). Also consistent with an active ligninolytic system, a GMC oxidoreductase (Phach1_9149) with similarity to Aspergillus niger glucose oxidase (22% identity) was detected in cultures containing line 64. This enzyme generates glucono-1,5-lactone and H2O2 from glucose. Possibly, catalases Phach1_127288 and Phach1_128306 serve to modulate toxic accumulations of peroxide which would otherwise impact the integrity of membranes.

Impressive levels of LPMO (Phach1_31049) were detected (Table 3). This metallo-monooxygenase boosts cellulose degradation (57, 50), and recent investigations have demonstrated LPMO activity on hemicellulose (8). All cultures also featured substantial protein and transcript levels for CDH and aldose epimerase (ALE1). Cellobiose β-anomer, the preferred CDH substrate (51), may be generated by ALE1. CDH and CBHs were previously identified in P. chrysosporium cultures (9, 17, 33, 52), and upregulated LPMOs (Table 3; see also Data Set S1 in the supplemental material) increase oxidative degradation of cellulose and xyloglucans.

Determining the precise role of these genes in lignocellulose degradation remains a task for future research, and elucidating the roles of the many hypothetical proteins is particularly challenging. For example, 343 of the 793 proteins identified are completely uncharacterized (Fig. 2). Similarly, 39 of the 113 upregulated proteins are hypothetical. Transcripts corresponding to Phach1_5249, Phach1_6166, Phach1_5352, and Phach1_140079 accumulated in transgenic line 64 relative to line P717. These four unlinked genes had little in common (<21% identity) except for the presence of one or more transmembrane helices in Phach1_5249, Phach1_6166, and Phach1_5352. The Phach1_5249 and Phach1_5352 transcript levels were also significantly higher in line 64 than in line 82, further demonstrating a response to high syringyl lignin content. Interestingly, four Phach1_5352 homologs were clustered within a 12-kb region of scaffold 27, but all were constitutively expressed at relatively low levels (see Data Set S1). Based on transcript levels and protein identifications, these genes are potentially important in lignocellulose degradation, but the data should be cautiously interpreted. Regulated expression and secretion do not guarantee full activity. Along these lines, the absence of detectable peptides must be regarded as equivocal without information related to turnover rates, substrate binding characteristics, and the frequency of trypsin cleavage sites. Nevertheless, high transcript levels associated with extracellular peptides warrant further examination of temporal expression patterns and biochemical properties.

Conversion efficiency barriers substantially complicate enzymatic “deconstruction” of forest biomass. Much effort is currently focused on improving wood utilization, particularly through identification/improvement of enzyme systems, genetic alterations in plant cell wall composition, and development of pretreatment processes. Our results demonstrate the importance of host genotype and suggest that commercial enzyme mixtures might be improved by tailoring enzyme components to specific feedstocks. P. chrysosporium provides a uniquely suited model system because it expresses all enzymatic and nonenzymatic components necessary to disassemble wood into useful monomers. The information gained may allow the further development of enzymatic systems for biomass treatment and help guide Populus breeding programs.

Supplementary Material

Supplemental material

ACKNOWLEDGMENTS

This work was supported by the National Research Initiative of the USDA Cooperative State Research, Education, and Extension Service (grant 2007-35504-18257) and by the Agriculture and Food Research Initiative, grant number 2011-67009-20056, from the USDA National Institute of Food and Agriculture to the Forest Products Laboratory. A.A. and J.R. were funded in part by the Department of Energy Great Lakes Bioenergy Research Center (DOE Office of Science BER DE-FC02-07ER64494).

Footnotes

Published ahead of print 11 July 2014

Supplemental material for this article may be found at http://dx.doi.org/10.1128/AEM.01604-14.

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