Lignocellulosic biomass is a large renewable resource of carbon that can be used as a substrate in the production of biofuels and biochemicals contrary to the polluting and diminishing fossil hydrocarbon sources. In nature, the carbon from lignocellulosic substrates including wood is utilized and recycled by fungi, most belonging to wood-colonizing and litter-decomposing Basidiomycota of the class Agaricomycetes [1–3]. The wood-decaying Polyporales species have been divided into white-rot and brown-rot fungi based on their visually observable decay types and differences in carbohydrate-active enzyme (CAZyme) encoding gene repertoires [1, 4]. Especially, the white-rot fungi are interesting due to their ability to degrade all components of wood, including the recalcitrant, aromatic, and heterogeneous lignin polymers [2, 5].

Lignin degradation is an important step prior to industrial use of plant biomass and lignocellulose raw materials [6]. In the white-rot fungal lifestyle—before gaining access to the carbohydrate storages of cellulose and hemicelluloses—lignin barrier is attacked to facilitate utilization of these carbon and energy sources [2, 7]. Lignin modification is possible because of a wide array of extracellular oxidoreductases produced by white-rot fungi. These oxidoreductases are enzymes of CAZy auxiliary activity family 2 (AA2) [8] fungal class-II lignin-modifying peroxidases including lignin peroxidases (LiPs), manganese peroxidases (MnPs), and versatile peroxidases (VPs) that are important in lignin modification [2, 9, 10]. Class-II peroxidases require hydrogen peroxide which may be generated by other CAZy auxiliary activity enzymes belonging to copper radical oxidases (CROs, AA5) and glucose–methanol–choline superfamily (GMCs, AA3) oxidoreductases [11, 12]. Lignin-converting enzyme set also includes the dye-decolorizing peroxidases (DyPs) [10, 13] and laccases. Laccases are phenol-oxidizing multicopper oxidases (MCOs, CAZy class AA1) which may thereby potentially act on lignin substructures by the aid of aromatic mediator compounds [2, 5].

Crystalline cellulose is utilized by the white-rot fungi with the help of cellobiohydrolases belonging to CAZy glycoside hydrolase (GH) families GH6 and GH7 [1, 3]. For complete enzymatic degradation of cellulose chains, endoglucanases of several GH families (GH5, GH9, GH12, GH44, and GH45), family AA9 (GH61) lytic polysaccharide monooxygenases (LPMO), and β-glucosidases of families GH1 and GH3 are needed [2, 14]. In addition, Basidiomycota genomes encode a wide array of other carbohydrate-active enzymes such as carbohydrate esterases (CEs) and polysaccharide lyases (PLs) for degradation of wood components including hemicelluloses and pectins [14]. The genes expressed and proteins produced during growth on plant biomass material reflect specific lifestyle of each fungal species and its strategy utilized for lignocellulose conversion [2, 15–17].

Phlebia radiata is a saprobic, wood-colonizing white-rot species of Agaricomycetes order Polyporales and phlebioid clade, and it is the taxonomic type species of the genus Phlebia [18, 19]. In nature, Phlebia species are mainly found colonizing deciduous wood and to some extent, also on coniferous wood [20, 21]. P. radiata and other Phlebia species are able to grow on Norway spruce (Picea abies) wood, producing wood-decaying enzymes [18, 22]. Spruce and coniferous wood from northern temperate and boreal forests are significant renewable feedstocks for forest-based industry [23]. To investigate the applicability of P. radiata isolate 79 for wood pre-treatment and lignocellulose bioconversions, we selected Norway spruce as its growth substrate for the proteomic and transcriptomic analyses.

Several lignin-modifying enzymes of P. radiata 79 were previously cloned and characterized, including three LiPs [24], two divergent MnPs [25], and two laccases [26, 27]. Especially, the lignin-modifying peroxidases (LiPs and MnPs) of P. radiata and near-related Phlebia isolates have demonstrated high activity and efficiency in oxidoreductive reactions, conversion and degradation of lignin-like molecules, and potential in biotechnological applications [28–31]. However, no complete proteomic or transcriptomic study of the fungus on its natural lignocellulose wood substrate has been conducted before.

Our aim was to analyze the time-dependent changes in protein and enzyme expression of P. radiata during 6 weeks of growth on wood under conditions mimicking the natural fungal habitat. Transcriptome analysis from two cultivation time points served as a support for the proteomics study and also provided additional information on gene expression during growth on wood. The genome assembly of P. radiata (to be discussed elsewhere) was functionally annotated and searched for CAZyme encoding genes which were upregulated and produced as proteins on spruce wood.

Genome sequencing of P. radiata wild-type dikaryon isolate 79 resulted with 40.92-Mb haploid size genome assembly including 14,113 predicted gene models (to be discussed elsewhere). To study the proteome of P. radiata, to recognize as many proteins as possible, and to identify time-dependent expression of lignocellulose degrading CAZymes on coniferous wood, total proteins from six time points (0, 7, 14, 21, 28, 42 days of growth) were extracted from solid-state spruce wood cultivations. In addition to proteomics, transcriptome on wood at growth time points of 14 and 28 days was compiled by RNA sequencing to facilitate analysis of differential gene expression by using the 14-day malt extract medium grown mycelia as reference.

Characteristics of P. radiata proteome and transcriptome on wood

In total, 1356 proteins were identified by peptide LC–MS/MS proteomics and mapping the peptide sequences against translated coding sequences of the gene models of P. radiata genome assembly (with at least two unique peptides mapping per protein, Additional file 1: Table S1). For each protein at each time point, the mean abundance value with standard deviation was calculated from the three biological replicate culture values (Additional file 1: Table S1). The biological replicate protein abundances had high coherence according to principal component analysis (Additional file 2: Figure S1a). The number of identified proteins increased up to 28 days then slightly decreased on day 42 (Table 1). This was in accordance with total protein concentrations measured from protein extracts of each time point (Additional file 3: Figure S2).

Time (d)	Number of identified proteinsa	Number of secreted proteinsb (percentage of identified proteins)
0	89	31 (35 %)
7	1009	150 (15 %)
14	1077	163 (15 %)
21	1149	170 (15 %)
28	1151	170 (15 %)
42	1035	157 (15 %)

The proteins were analyzed by peptide LC–MS/MS and identified by searching against translated gene models of P. radiata genome. The secreted proteins were recognized with Phobius prediction analysis [32]

^aProteins were identified from peptide LC–MS/MS analysis

^bSecreted proteins were identified with Phobius prediction

To estimate the number of secreted proteins in the total proteome, Phobius analysis [32] was performed. N-terminal signal peptide was predicted for 15 % (210) of the proteins (Fig. 1). This percentage was higher than the number of secreted proteins according to the in silico analysis of P. radiata gene models (10 %, Fig. 1). The number of secreted proteins may be an underestimation due to difficulties in recognition of the true 5’ initiation site (start Met codon) of gene model ORFs by computational methods. However, in silico analysis gave a rough estimation of the ratio of the number of theoretically predicted versus proteomics-obtained number of secreted proteins.

Overall, composition of P. radiata proteome was relatively constant in the course of spruce wood solid-state cultivation (Fig. 2b, c). In total, 823 (61 %) proteins were shared at each time point from day 7 to 42. As expected, we identified some proteins (89) at time point zero representing those introduced to the solid wood substrate within the fungal inoculum (cultivated on malt extract liquid medium for 14 days). Blast2GO searches showed that the identified proteins were divided into various functional categories (Fig. 2a). Based on the preliminary annotation of the gene models, proteins were divided into eight different categories: AA2 (class-II peroxidases), other AAs, CEs, GHs, peptidases, PLs, proteins with other functions, and proteins of unknown function. The majority of identified proteins (77 %) were classified as proteins with other functions that include an array of intracellular proteins involved in translation and in metabolic processes.

The transcriptomes of two biological replicate cultures on spruce wood at two time points (14 and 28 days) and from one time point (14 days) on malt extract reference medium, respectively, were analyzed by RNA-sequencing (Additional file 2: Figure S1b, c). According to the transcriptome analysis, 2 162 of the predicted P. radiata transcripts had significantly higher expression level (p < 0.05 and log2-fold change ≥1) and 1 820 had significantly lower (p < 0.05 and log2-fold change ≤−1) expression level at both or one of the time points on wood as compared with the malt extract cultivation. For specific transcripts, also more stringent p value and fold change threshold (p < 0.01 and log2-fold change ≥2) were applied to test for highly significant differences of gene expression between growth on wood and malt extract medium. The most highly upregulated transcripts on wood were recognized to encode candidate transporter proteins, hydrophobins, and candidate proteases together with various CAZymes (Table 2).

Gene id	Top 50 day 14	Top 50 day 28	Log2fc day 14	Log2fc day 28	Protein abundance (% of total MS intensity)					Function	Family
					7 days	14 days	21 days	28 days	42 days
Minus.g6827	x		10.72	4.49	1.03	1.08	0.26	0.01	0.00	Lignin peroxidase (LiP2)	AA2
Minus.g11349	x	x	10.32	8.74	0.79	0.61	0.46	0.39	0.37	Alcohol oxidase	AA3
Plus.g9320	x	x	10.16	9.36	0.03	0.06	0.05	0.07	0.06	Lytic polysaccharide monooxygenase	AA9
Plus.g11539	x	x	9.96	8.43	0.02	0.07	0.10	0.14	0.07	Lytic polysaccharide monooxygenase	AA9
Plus.g2118	x	x	9.7	9.59						Oligopeptide transporter
Minus.g10274	x	x	9.24	7.95						Lytic polysaccharide monooxygenase	AA9
Minus.g3073	x		8.71	1.72	0.91	0.32	0.10	0.00	0.00	Lignin peroxidase 1 (LiP1)	AA2
Plus.g1419	x	x	8.55	7.25	8.33	3.86	3.76	3.08	3.81	Manganese peroxidase (MnP1-long)	AA2
Plus.g1442	x	x	8.52	7.86	0.00	0.03	0.03	0.06	0.07	Acid protease, family A01A
Minus.g10376	x	x	8.46	6.4						Hypothetical protein
Minus.g3552	x	x	8.46	5.49	0.03	0.06	0.05	0.03	0.01	Lytic polysaccharide monooxygenase	AA9
Plus.g12321	x	x	8.43	7.48	0.01	0.01	0.03	0.01	0.01	Acetyl xylan esterase	CE1
Plus.g10527	x	x	8.07	8.37	0.00	0.05	0.14	0.06	0.04	Copper radical oxidase	AA5
Minus.g8138	x		8.07	5.16						Hypothetical protein
Plus.g10872	x	x	7.62	6.5	0.29	0.39	0.23	0.45	0.68	Tripeptidyl peptidase, family S53
Minus.g4805	x		7.62	4.5	0.15	0.15	0.11	0.06	0.02	Glutathione transferase
Plus.g6944	x	x	7.61	7.75	0.00	0.00	0.01	0.02	0.03	Carboxypeptidase, family S10
Minus.g2657	x	x	7.59	5.73						MFS general substrate transporter
Minus.g3349	x	x	7.32	6.01						Carbohydrate-binding module family 1 protein	CBM1
Plus.g4342	x	x	7.2	7.32	0.20	0.32	0.22	0.23	0.10	Cellobiohydrolase	GH6
Minus.g4996	x	x	7.19	7.06						Sugar transporter
Plus.g8760	x		7.19	3.71	0.15	0.22	0.10	0.01	0.00	s-adenosyl-l-methionine-dependent methyltransferase
Minus.g11037	x		7.18	0.36	0.00	0.02	0.00	0.00	0.00	β-1,4-endoxylanase	GH10
Plus.g12778	x	x	7.12	7.36	0.06	0.14	0.28	0.70	1.29	GDSL-like lipase acylhydrolase
Minus.g8600	x	x	7.08	6.33	0.00	0.01	0.02	0.15	0.16	Oxalate decarboxylase
Minus.g3792	x	x	7.07	6.02						Hypothetical protein
Plus.g3697	x		7.02	4.94	0.01	0.04	0.04	0.02	0.01	β-1,4-endoxylanase	GH11
Minus.g3846	x		6.96	5.43						Hypothetical protein
Plus.g6610	x	x	6.89	5.87						Hexose transporter
Minus.g10273	x	x	6.86	5.93						Lytic polysaccharide monooxygenase	AA9
Minus.g927	x	x	6.83	6.58	0.14	0.19	0.22	0.21	0.21	Tripeptidyl peptidase, family S53
Plus.g6929	x	x	6.83	6.5						Hydrophobin
Minus.g7795	x	x	6.73	6.38	0.05	0.07	0.11	0.08	0.05	Clavaminate synthase
Minus.g3957	x	x	6.7	6.6	0.02	0.04	0.05	0.09	0.13	Acetylesterase	CE16
Plus.g11538	x		6.59	3.44	0.02	0.12	0.08	0.04	0.01	Lytic polysaccharide monooxygenase	AA9
Plus.g5095	x		6.58	2.97	0.00	0.04	0.03	0.01	0.01	NAD-binding oxidoreductase
Minus.g2367	x		6.55	3.09	0.50	0.46	0.26	0.06	0.01	s-adenosyl-l-methionine-dependent methyltransferase
Plus.g8273	x		6.5	5.14						Grp1/Fun34/YaaH domain transporter protein
Plus.g13374	x		6.48	5.25	0.02	0.07	0.06	0.05	0.02	Lytic polysaccharide monooxygenase	AA9
Plus.g11441	x		6.46	3.65	1.65	2.24	1.93	1.23	1.09	NAD-dependent formate dehydrogenase
Minus.g3726	x		6.36	4.61	0.00	0.01	0.02	0.01	0.01	Dihydrodipicolinate synthetase
Plus.g917	x	x	6.33	6.17						Hydrophobin
Plus.g3219	x	x	6.29	7.06	0.00	0.00	0.00	0.01	0.01	Carboxylesterase
Plus.g4436	x		6.27	3.9						Hypothetical protein
Minus.g9081	x		6.26	5.03	0.02	0.06	0.08	0.11	0.05	Exo-β-1,3/1,6-glucanase	GH131
Minus.g12191	x	x	6.23	5.7	0.07	0.11	0.07	0.09	0.03	β-1,4-endoxylanase	GH10
Plus.g4845	x		6.19	4.84	0.35	0.42	0.53	0.58	0.50	Short-chain dehydrogenase/reductase SDR
Minus.g11036	x		6.18	4.12	0.03	0.03	0.02	0.02	0.01	β-1,4-endoxylanase	GH10
Minus.g9727	x	x	6.16	5.67						MFS general substrate transporter
Minus.g9590	x	x	6.14	5.76	0.03	0.09	0.15	0.27	0.21	Peptidase, family G1
Minus.g8467		x	6.13	5.61	0.04	0.05	0.08	0.07	0.09	Homoserine O-acetyltransferase
Minus.g5595		x	6.07	5.55	0.16	0.54	0.34	0.18	0.04	Cellobiohydrolase	GH7
Minus.g10025		x	6.04	5.58	0.02	0.01	0.01	0.02	0.01	Acetylesterase	CE16
Minus.g9239		x	5.92	5.93	0.00	0.01	0.06	0.03	0.06	Unknown protein
Plus.g4481		x	5.74	5.57						Cupredoxin domain protein
Plus.g5796		x	5.7	6.17	0.02	0.01	0.02	0.01	0.02	Exo-β-1,3/1,6-glucanase	GH131
Plus.g8890		x	5.7	5.6						Hydrophobin
Minus.g5364		x	5.57	5.65	0.00	0.02	0.06	0.11	0.27	α-glucuronidase	GH115
Minus.g7830		x	5.46	5.71	0.20	0.37	0.57	0.82	1.14	Alpha/beta-hydrolase
Plus.g8163		x	5.4	6.73	0.01	0.05	0.13	0.39	0.53	Cellobiohydrolase	GH7
Plus.g4813		x	5.37	7.76	0.09	0.44	0.64	1.21	1.65	GMC oxidoreductase	AA3
Plus.g7451		x	5.36	5.51	0.09	0.22	0.16	0.18	0.09	β-1,4-endoglucanase	GH5_5
Minus.g3151		x	5.23	6.27	0.01	0.05	0.08	0.17	0.13	Mannosyl-oligosaccharide 1,2-α-mannosidase	GH47
Plus.g8155		x	5.22	6.2						WSC-domain-containing protein
Plus.g6787		x	5.2	5.47						APC amino acid permease
Minus.g4639		x	5.06	5.73						Glycoside hydrolase family 92 protein	GH92
Minus.g1646		x	4.95	5.72						Oligopeptide transporter
Minus.g10423		x	4.07	5.49						Oligopeptide transporter
Plus.g4812		x	3.24	5.79						Hypothetical protein

Abundance values are given for proteins identified by peptide LC–MS/MS

Wood-decay enzyme set of P. radiata

The emphasis of this study was on CAZyme encoding genes and especially on those identified as proteins and with known functions in degradation of plant cell wall components. The proportion of CAZymes, including GHs and CEs, was 7 % of the total proteome (Fig. 2). The auxiliary oxidoreductase activities covered 2 % of the total proteome with the AA2 family class-II peroxidases representing 32 % of this protein pool, that is 1 % of the total proteome. The proportion of GH proteins of the total proteome was relatively high (18 % of total proteome) at time point zero indicating active enzymatic carbohydrate utilization occurring by the fungal hyphae already in the malt extract inoculum cultivation. Overall distribution of proteins according to their CAZy families showed a large variety of functions (Additional file 4: Figure S3).

The number of upregulated transcripts and the number of detected proteins functionally annotated to correspond to plant cell wall degrading enzymes were compared, and the proportions were shown to be consistent (Fig. 3). Large proportion of the genes was upregulated and translated to proteins indicating active degradation of lignocellulose. In general, from the approximately 300 transcripts predicted to encode CAZymes belonging to different GH, CE, PL, and cellulose-binding module (CBM) families (excluding glycosyltransferases, GTs) together with AA9 lytic polysaccharide monooxygenases, AA2 class-II lignin-modifying peroxidases, and AA1 laccases, 141 were expressed on a significantly higher level on both or one of the transcriptome time points (14 and 28 days) on wood as compared with the 14-day malt extract cultivation. 107 of the transcripts were upregulated at both time points on wood (Fig. 4a). Majority (61 %) of these putatively encode activities against the plant cell wall (Fig. 4b). Moreover, majority of the transcripts upregulated at both time points on wood and coding for plant cell wall degrading activities were present in the proteome (85 %) (Fig. 4c).

Upregulated transcripts involved in attack on lignin were encoding several class-II lignin modifying peroxidases, both LiPs and MnPs, upregulation being apparent at both time points on wood and being in agreement with the proteome data at the same time points (Fig. 5). The 20 most abundant CAZy proteins identified in the proteome samples included the most upregulated class-II peroxidases (Table 3). Moreover, transcripts for LiP2, LiP3, MnP1-long, and MnP3-short were highly significantly accumulated (p < 0.01, log2-fold change ≥2) during the wood cultivations.

Gene ID	Predicted function	Protein abundances						Average abundance on days 7–42	Transcripts up-regulated on wood
		Cultivation time (days)
		0	7	14	21	28	42
Plus.g1419	AA2: MnP1-Long	0.00	8.33	3.86	3.76	3.08	3.81	4.57	x
Plus.g11059	AA2: LiP3	0.00	5.37	4.32	2.58	1.10	0.70	2.81	x
Minus.g4265	AA5_1; glyoxal oxidase	0.00	2.32	1.25	0.75	0.88	2.10	1.46	x
Plus.g4813	AA3: GMC oxidoreductase	0.00	0.09	0.44	0.64	1.21	1.65	0.81	x
Plus.g10562	AA2: MnP2-Long	0.00	0.45	0.25	0.41	0.65	1.30	0.61	x
Minus.g11349	AA3: GMC oxidoreductase	0.00	0.79	0.61	0.46	0.39	0.37	0.52	x
Minus.g6827	AA2: LiP2	0.00	1.03	1.08	0.26	0.01	0.00	0.48	x
Minus.g7380	CE1	0.00	0.39	0.28	0.33	0.30	0.49	0.36	x
Plus.g453	AA2: MnP3-short	0.00	1.13	0.40	0.10	0.06	0.06	0.35	x
Minus.g2306	GH3	2.80	0.33	0.38	0.35	0.27	0.29	0.32
Minus.g3073	AA2: LiP1	0.00	0.91	0.32	0.10	0.00	0.00	0.27	x
Minus.g5595	GH7	0.00	0.16	0.54	0.34	0.18	0.04	0.25	x
Plus.g8163	GH7	0.00	0.01	0.05	0.13	0.39	0.53	0.22	x
Minus.g6399	GH3	0.01	0.11	0.15	0.20	0.25	0.40	0.22	x
Plus.g4342	GH6	0.00	0.20	0.32	0.22	0.23	0.10	0.22	x
Plus.g637	CE16	0.00	0.18	0.13	0.15	0.27	0.33	0.21	x
Minus.g12190	GH10	0.00	0.24	0.23	0.21	0.22	0.08	0.19	x
Minus.g11677	GH28	0.76	0.53	0.16	0.04	0.02	0.01	0.15
Plus.g7451	GH5	0.00	0.09	0.22	0.16	0.18	0.09	0.15	x
Plus.g9628	AA8-AA3_1: CDH	0.00	0.18	0.24	0.10	0.11	0.04	0.14	x
	Proportion (%) of total proteome	3.57	22.84	15.22	11.27	9.81	12.38	14.30

Gene ID corresponds to annotated gene locus on the P. radiata genome assembly. Protein abundances are calculated based on mass spectrometric signal intensity values per each time point. Up-regulated transcripts refer to transcripts with significantly higher level of expression (p < 0.05 and log2-fold change ≥1) on wood as compared to the malt extract cultivations at both time points

MnP manganese peroxidase; LiP lignin peroxidase; CE carbohydrate esterase; CDH cellobiose dehydrogenase; GH glycoside hydrolase; GLOX glyoxal oxidase

The single dye-decolorizing peroxide encoding gene (DyP) which was annotated in the genome was transcriptionally up-regulated only at the earlier time point (14 days) on wood. Quite surprisingly, the respective protein was not detected in the proteome at any of the studied time points, from 0 to 42 days of wood colonization. Contrary to the DyP transcription response, a novel class-II peroxidase MnP6-long together with the previously cloned LiP4 was identified in the proteomes, although not observed being upregulated in the wood transcriptomes. In fact, both corresponding genes were downregulated at the later time point (28 days) on wood as compared with the malt extract reference transcriptome. On the contrary to the peroxidases, none of the five annotated laccase-encoding genes were regulated on wood, and Lacc1 protein was the only laccase enzyme present in the proteomes, taking into account all the time points analyzed. Noticeable is, however, that laccase activity was detected at every time point in the protein extracts of wood cultures (Additional file 3: Figure S2).

A large number of additional AA accessory oxidoreductases were found in the proteomes including alcohol oxidases, copper radical oxidases, one glyoxal oxidase (GLOX), GMC oxidoreductases, alcohol and aryl-alcohol dehydrogenases, one cellobiose dehydrogenase (CDH), and one benzoquinone reductase. Of this pool of H₂O₂ producing and other important oxidoreductive activities possessing enzymes, 11 were upregulated as transcripts at both time points on wood, with one alcohol oxidase gene transcript having the highest fold change. Transcripts for two alcohol oxidases, an aryl-alcohol oxidase, a GMC oxidoreductase, a GLOX, a copper radical oxidase, and a cellobiose dehydrogenase were highly significantly accumulated during the wood cultivations (Fig. 5).

Transcripts from a number of different CAZy families, including activities against cellulose (Fig. 6) and hemicelluloses (Fig. 7), were upregulated independent of the time point on wood, and encode enzyme candidates, for example, AA9 LPMOs, cellobiohydrolases, β-1,4-glucosidases, β-xylosidases, β-1,4-endoglucanases, exo-β-1,3/1,6-glucanases, β-1,4-endomannanases, β-mannosidases, an acetyl xylan esterase, glucuronoyl esterases, acetylesterases, β-1,4-endoxylanases, an α-glucuronidase, an arabinofuranosidase, β-galactosidases, and xyloglucanases. Several of these genes, including seven genes encoding the AA9 LPMOs, were significantly differentially expressed on wood. These CAZy families were also present in the proteomes at least by one representative, and several of them were detected as being the most abundant CAZymes produced (Table 3).

A number of pectin-degrading CAZy genes, both lyases and hydrolases were expressed as transcripts on wood encoding for activities against polygalacturonan and rhamnogalacturonan, ester linkages (pectinesterase) and galactan. Many of these genes were upregulated at both time points on wood (Fig. 7). From these, three GH28 polygalacturonases, one CE8 pectinesterase, and the only PL4 rhamnogalacturonan lyase identified were highly significantly differentially expressed as transcripts. All of these—except one polygalacturonase enzyme—were also found as proteins in the proteome on wood. In addition, a candidate GH43 galactan 1,3-β-D-galactosidase possibly involved in degradation of arabinogalactan and transcripts encoding CBM1 modules and one cytochrome b562 iron reductase with a CBM1 domain were upregulated at both time points on wood (also when more stringent p-value and fold change were applied). From these, only the GH43 protein was present in the proteome.

In total, a portion (7.3–8.6 %) of the proteins identified in the total proteome on wood was classified as proteins with unknown function. Although none of these were among the 20 most abundant proteins produced on wood (Additional file 1: Table S1), they may include a few candidates that are important for fungal wood decay, thus presenting interesting targets for future studies. One of these is the transcriptionally highly upregulated P. radiata gene model minus.g9239 with unknown function but with the corresponding peptides discovered in the wood proteome (Table 2).

Dynamics of plant cell wall degrading enzymes

When time-dependency of protein expression was studied, it was noticed that despite the fact that protein numbers within each functional category were somewhat constant during the cultivation (Fig. 2), differences in relative abundances of the proteins were observed (Fig. 8). When fungal proteins predicted to be important for wood decay were analyzed at every time point, the largest expansion seemingly occurred in the pool of identified proteins (of the overall protein production) during the first cultivation week. The abundances of the lignin-attack associated proteins peaked at growth day 7, and as the cultivation time advanced, abundances of these proteins started to decline. The only exception was the class-II peroxidase MnP2-long, the abundance of which started to increase again on cultivation day 17 (Additional file 5: Table S2).

Especially, the LiP abundance was decreasing, whereas MnP proteins were either constantly produced or demonstrating a less dramatic decline in protein abundances during the cultivation. This phenomenon was also observed in the transcriptome with the expression of especially LiP transcripts decreasing after 14 days on spruce wood. The MnP enzyme activities were constant on wood and detected also from the last time point (Additional file 3: Figure S2). Accessory oxidoreductase enzymes demonstrated likewise constant protein production during the cultivation. The abundancy of one GLOX protein (encoded by the gene model minus.g4265) of family AA5_1 declined between days 21 and 28 then increasing again until the end of the cultivation on wood (day 42). In addition, various dehydrogenases belonging to GMC oxidoreductases were produced with low protein abundances.

Cellulose degrading enzymes peaked in the proteomes on wood on cultivation day 14 (Fig. 8). Of the CAZy family GH7 cellobiohydrolases, relative abundance of one protein (encoded by the gene model minus.g5595) was clearly decreasing during the cultivation whereas the abundance of another GH7 protein (encoded by the gene plus.g8163) increased. The transcriptome data indicated corresponding differences in gene expression indicating that these two GH7 cellobiohydrolase encoding genes are under differential regulation. Relatively low cellobiohydrolase activities were, however, measured after the third week of cultivation on wood (Additional file 3: Figure S2). The highest abundance of β-glucosidases was detected for proteins of CAZy family GH3 while family GH1 proteins remained low in abundance. β-glucosidase activities in turn were measured throughout the cultivation (Additional file 3: Figure S2). Relative abundances of hemicellulose degrading enzymes increased in the proteome on wood during the active growth of P. radiata, and xylanase activity was detected at time points 7, 28 and 42 (Fig. 8; Additional file 3: Figure S2). Production of CAZy family GH35 β-1,4-galactosidase, a GH51 α-arabinofuranosidase and a GH115 α-glucuronidase proteins increased during the cultivation. The total abundance of pectin degrading proteins was quite low during the cultivation on wood.

To follow the dynamics of fungal cell wall degradation and hyphal autolysis, abundances of twelve chitinase and β-glucanase proteins belonging to GH families 5, 13, 16, 18, 20, 55, 72, and 92 were followed. Abundances of these proteins were increasing up to day 28 of the wood cultivation (Fig. 8). It is of interest that the abundance of peptidases (protease activity proteins) followed a similar pattern although the protein numbers (number of individual gene products) and their abundances were higher. Identified peptidases represented 27 different MEROPS peptidase families. Majority of the peptidases were assigned to A01A and T01A subfamilies. The top three most abundant peptidases included a family M28 metalloprotease, an A01 aspartyl peptidase and an S53 tripeptidyl peptidase.

Decay of spruce wood by P. radiata

Vertical and transverse sections of spruce wood samples were observed by field-emission scanning electron microscopy. Intact xylem and wood cell wall ultrastructure with tracheid bordered pits were observable in non-inoculated spruce wood (Fig. 9a, b). After 42 days of growth, P. radiata hyphae were visible particularly inside the tracheids (in tracheid lumen) and attached to secondary cell walls (Fig. 9e, f). In fungal colonized wood samples, a few enlarged bordered pits and thinning of tracheid cell walls were noticeable (Fig. 9c, d).

Supporting results were obtained by lignin analyses at first determining the gravimetric Klason lignin content and by more accurate analytical methods (Table 4). Klason lignin content and total yield of aromatic compounds detected by pyrolysis–GC/MS analyses were relatively constant in the fungal decayed wood samples compared to non-inoculated wood but some changes were, however, observed in lignin structure and polymerization stage. By pyrolysis–GC/MS analyses, in total, 20 compounds originating from lignin substructure units were tentatively identified according to MS spectra and reference compounds (Table 4). Increase in the abundance of monomeric phenolic compounds such as methylated phenols and guaiacol was probably caused by attack on lignin moieties resulting with decrease in the molecular size of polymeric lignin and release of oligomeric and monomeric substructures during fungal decay. This was also observed as an increase in the content of acid soluble lignin. The ratio of phenylmethane and phenylethane units to phenylpropane units (Ph-C1,C2/Ph-C3 ratio) increased after fungal cultivation indicating that a part of the side chain linkages of lignin substructures were cleaved. Lignin oxidative and degradative activity was also observed as increment of the amount of phenolic compounds, such as vanillin and coniferyl aldehyde (Table 4).

RT	Peak name	Spruce wood (%)	After 6 weeks of fungal growth (%)	Change (%)
		Mean	Mean
7.126	Phenol (hydroxybenzene)	0.29 ± 0.08	0.50 ± 0.09	+72
8.401	2-methylphenol	0.11 ± 0.03	0.16 ± 0.03	+45
8.753	4-methylphenol, (4-methylguaiacol)	0.25 ± 0.06	0.33 ± 0.05	+32
9.01	2-methoxyphenol, (Guaiacol)	3.33 ± 0.24	4.69 ± 0.30	+41
10.437	2-methoxy-3-methylphenol	0.76 ± 1.22	1.24 ± 0.99	+63
10.64	2-methoxy-4-methylphenol	3.19 ± 0.47	2.44 ± 0.47	−24
11.89	2-methoxy-4-ethylphenol, (ethylguaiacol)	0.83 ± 0.10	0.73 ± 0.08	−18
12.428	4-vinylguaiacol	3.17 ± 0.29	3.22 ± 0.39	+2
12.994	Eugenol, 4-allylguaiacol	0.57 ± 0.05	0.45 ± 0.02	−21
13.129	2-methoxy-4-propylphenol, (4-propylguaiacol)	0.31 ± 0.03	0.26 ± 0.04	−16
13.626	Vanillin	1.27 ± 0.56	1.45 ± 0.71	+14
13.692	2-methoxy-4-(1-propenyl)phenol, (isoeugenol, cis)	0.27 ± 0.02	0.23 ± 0.02	−15
14.274	2-methoxy-4-(1-propenyl)phenol, (isoeugenol, trans)	1.78 ± 0.18	1.47 ± 0.25	−17
14.355	1-(4-hydroxy-3-methoxyphenyl)ethanone, (guaiacylacetone)	1.06 ± 0.65	0.86 ± 0.65	−19
14.733	1-(4-hydroxy-3-methoxyphenyl)ethanone (acetovanillone)	0.98 ± 0.46	0.54 ± 0.47	−45
15.201	Phenol, 2-methoxy-4-propan-1-ol, (dihydroconiferyl alcohol)	0.81 ± 0.54	0.35 ± 0.27	−57
15.749	Coniferyl alcohol, cis	0.47 ± 0.25	0.24 ± 0.17	−49
15.867	1-(4-hydroxy-3-methoxyphenyl)propanone, (propiovanillone)	0.58 ± 0.27	0.35 ± 0.30	−40
16.657	Coniferyl alcohol, trans	0.60 ± 0.46	0.35 ± 0.46	−42
17.673	Coniferyl aldehyde	0.51 ± 0.35	0.52 ± 0.59	+2
Pyrolysis lignin (area aromatics/total)		21.3 ± 0.7	20.4 ± 2.0	−4
Gravimetric (Klason) lignin		25.8 ± 0.33	26.1 ± 0.51	+1
Acid soluble lignin		0.30 ± 0.04	0.68 ± 0.23	+127
Pch-C1,2/Pch-C3 ratioa		0.03	0.08	+167

Relative peak areas (%) of lignin-derived pyrolysis product compounds identified with pyrolysis–GC/MS. Gravimetric and acid soluble lignin contents are also shown. The values are calculated from two biological replicates where 3–4 technical replicates were taken for pyrolysis samples, and from three biological replicates each of which with two technical replicate samples for Klason lignin determination

^aRatio of phenylmethane and phenylethane to phenylpropane type compounds

White-rot fungal secretomes on various lignocelluloses have been investigated largely concentrating on the model white-rot fungus, Agaricomycetes Polyporales species Phanerochaete chrysosporium [16, 33, 34]. Similar studies on phlebioid clade fungi, including Phanerochaete carnosa [35], Phlebiopsis gigantea [36] and Irpex lacteus [37], as well as on the other white-rot Polyporales species Ganoderma lucidum [38], Ceriporiopsis subvermispora [39, 40], Pycnoporus cinnabarinus [41], Pycnoporus coccineus [42], and Trametes trogii [43], were conducted recently. In addition, lignocellulose-decay proteomics and transcriptomics of the order Agaricales white-rot species Pleurotus ostreatus have been elucidated [44, 45]. With these data and the accumulating genomic knowledge on fungi, however, it is evident that there are some differences in gene numbers but larger variations in gene expression and CAZy protein production between the white-rot fungal species. Moreover, these differences seem to be more fungal species and isolate dependent than influenced by, e.g., the type of wood and lignocellulose used as growth substrate [35, 42, 45].

Regarding this, we aimed at characterisation of the CAZy proteins in the total proteome on wood of an efficient lignin-degrading white rot species, P. radiata, isolate 79, not fully investigated by omics approach before but with a recently sequenced and annotated genome available. This allowed us to perform an extensive and deep time point study on the proteome and transcriptome while the fungus is colonizing wood. Moreover, the time point study allowed us to observe dynamic changes in the abundances of P. radiata proteins expressed on wood, and to gain insight into regulation of CAZy gene expression by transcriptome analyses. Our results confirm that the wood-decaying enzyme repertoire of P. radiata is functional and composed of a variety of CAZy families including the auxiliary oxidoreductases, a set of lignin-modifying peroxidases accompanied by H₂O₂ producing enzymes and LPMOs, and a selection of hydrolases, esterases and lyases, all needed for complete degradation of the polymeric lignocellulose components.

The wood-decay machinery of P. radiata is typical for a traditional white-rot fungus (including various class-II lignin-modifying peroxidases, laccase, CDH, GMC oxidoreductases, GLOXs, LPMOs, cellulases of GH5, GH6, GH7 families) [1–3, 46]. However, some unique features like high expression of several LiPs and both long- and short-MnPs but low expression of laccase differentiate P. radiata from many other white-rot species of Polyporales. Strong expression of multiple lignin-modifying LiP and MnP class-II peroxidases, together with H₂O₂ producing oxidoreductases (GLOX, GMCs) and GH6 and GH7 cellobiohydrolases is more similar to the spectrum of CAZymes expressed by P. chrysosporium [7, 47]. In another phlebioid clade species, Phlebiopsis gigantea, ten genes codifying for class-II peroxidases were identified, but none of these were detected as secreted proteins in pine wood containing cultures [36]. Instead, one DyP (dye-decolorizing peroxidase) was identified in the P. gigantea secretome [36]. In our study, the only DyP encoding gene annotated in P. radiata genome was detected in the wood transcriptome but not identified in the proteome. These findings pinpoint that each phlebioid species expresses a unique array of CAZy and oxidoreductase enzymes and have an exquisite strategy for colonization and decay of wood.

Preliminary annotation of the P. radiata genome assembly revealed ten genes for class-II lignin-modifying peroxidases. Of the four LiPs, the well-characterized LiP3 enzyme [30] was the most abundant protein in the proteome with high expression level on wood, although transcriptionally not as strongly upregulated as LiP2 and LiP1 encoding genes. Three of the P. radiata LiP encoding genes (LiP1, LiP3, and LiP4) have been cloned and characterized with the respective transcripts shown to be expressed by the fungus on milled spruce and alder wood supplemented cultures [24]. Furthermore, LiP1 protein was previously detected in Norway spruce shavings containing bioreactor cultivations of P. radiata [48].

Similar to LiP production, variations were observed in this study for expression of the six MnP encoding genes as transcripts and proteins on spruce wood. A novel P. radiata long-MnP1 encoding gene was observed as highly upregulated on spruce wood and correspondingly produced in high protein amounts throughout the cultivation. In contrast, of the two previously cloned and characterized P. radiata MnPs [25], expression of the long-MnP2 showed an increasing tendency, while the short-MnP3 demonstrated protein decline during the six-week surveillance on wood. This indicates that the multiple class-II lignin-modifying peroxidase encoding genes are differentially regulated in fungi, with some genes being quickly responsive to the wood substrate while transcription of the others may be more subjected to time and fungal growth-dependent regulation.

Previously on solid-state wheat straw lignocellulose cultures of P. radiata 79, LiP2 enzyme was detected as one of the major extracellular proteins produced by the fungus together with a few GLOXs [49]. Moreover, LiP and GLOX activities were observed to decline between cultivation days 14 and 28 [49], accordingly as is observed in our present study for the several LiPs indicating a decline in protein abundances in the later stages of the six-week cultivation on spruce wood. Taken together, our results confirm the previous observations for P. radiata and indicate synergistic action of GLOXs and LiPs when the fungus is growing on lignocelluloses likewise is reported for P. chrysosporium [7, 50, 51].

Together with the CRO glyoxal oxidases of the CAZy family AA5, GMC aryl-alcohol oxidases from CAZy family AA3 may also supply extracellular hydrogen peroxide for the fungal wood decay and class-II peroxidases, and AA3 oxidoreductases may also act as coupled activities to aryl-alcohol dehydrogenases [52]. Both AA3 and AA5 proteins were detected on P. radiata spruce wood cultivations together with various other alcohol oxidases and dehydrogenases possibly working as accessory oxidoreductive enzymes and having a role in enhancing attack on wood lignin. Expression of the latter transcripts may be a result of active intracellular modification of lignin metabolites as is reported for P. chrysosporium [47].

Laccase activities were measured in our spruce wood cultivation and in previous studies on wood-containing cultures of P. radiata [18, 53]. Five laccase encoding genes are recognized in the P. radiata genome. However, only one laccase protein, that is the well characterized P. radiata Lacc1 [26, 27], was identified in constant but low amounts in the wood proteomes at the time points studied. Lacc1 protein has been repeatedly detected in liquid media and solid lignocellulose cultures of the fungus [49, 53–56] emphasizing its main role in P. radiata secretome regardless of the growth substrate and carbon source. The transcriptome revealed that several laccase encoding genes were expressed on wood although lacc1 gene had clearly the highest transcript abundances. None of the laccase encoding genes, however, was significantly upregulated on wood, which indicates constant expression in particular for lacc1.

The constant expression of laccase encoding genes with only one secreted protein may reflect the evolutionary relationship of P. radiata and systematic placement in the phlebioid clade of Polyporales. Phlebioid clade includes fungal species completely lacking laccase encoding genes in their genomes, such as Phanerochaete chrysosporium, Phanerochaete carnosa, and Phlebiopsis gigantea [36, 57, 58]. On the contrary, lignocellulose secretomes of more far-related white-rot fungal species from other systematic clades and orders of Agaricomycetes demonstrate a wider array of laccase proteins, e.g., in C. subvermispora (three detected laccases on lignocellulose), Pleurotus eryngii (four detected laccases), and Pleurotus ostreatus (four detected laccases) [39, 43, 45, 59]. In this respect, the phlebioid white-rot fungi demonstrate their own type of (less or non-laccase dependent) strategies of wood-decay.

In addition to lignin attack, cellulose degradation by white-rot fungi occurs via the combination of several divergent protein families, that is by cellobiohydrolases, LPMOs and CDH [60]. LPMOs from CAZy family AA9 are important in cellulose and hemicellulose degradation [61–63], and they may utilize various electron donors including CDH, haem proteins fused to cellulose-binding module (cytochrome b562-CBM1), or lignocellulose-derived and fungal produced di-phenols [63–65]. In addition, the GMC oxidoreductases, such as glucose oxidase and pyranose dehydrogenase, may participate in the redox system [63]. Transcripts of P. radiata encoding LPMOs and the assisting activities were identified on wood. Seven of the twelve annotated LPMO encoding genes were highly expressed and significantly upregulated on wood, and five of these were accordingly identified as peptides in the proteome. Moreover, supporting the oxidative and electron transfer oxidoreductive protein attack on wood generated by fungal produced LPMOs, CDH protein— having variable suggested catalytic roles [66]—was one of the most abundant CAZymes identified in the P. radiata wood proteome and was accordingly upregulated in the transcriptome.

Additional enzymes important in fungal carbohydrate metabolism and connected to wood-decay are aldose-1-epimerases (ALE) [67] that generate cellobiose β-anomers, which in turn are reducing substrates of CDH enzymes. Three putative ALEs were found in the wood proteome of P. radiata. One ale (gene model minus.g8594) was upregulated in the wood transcriptome. ALE encoding genes are apparently general in wood-decay fungi and identified in white-rot and brown-rot Polyporales genomes [67]. Corresponding peptides were supportively detected in secretomes of Phanerochaete chrysosporium but not in Phlebiopsis gigantea [13, 33, 63].

To study the effects of hyphal growth on wood on the fungal cell wall reorganization and degradation, the abundances of fungal cell wall degrading proteins during the cultivation were followed together with peptidases. Abundances of these proteins increased over time, thus indicating the need of P. radiata to recycle essential nutrients and reorganize the fungal hyphae and cell wall upon growth and colonization of wood. It has been suggested that protease expression is connected to nitrogen acquisition from fungal produced and lignin-linked proteins in the nitrogen-limited wood environment [68–70]. Several other nitrogen metabolism associated transcripts were also upregulated in P. radiata on wood including oligopeptide transporters similar to as is observed in P. chrysosporium [7], although the corresponding proteins were absent from our proteome samples.

In addition to nutrient cycling and degradation of intracellular proteins, fungal proteases have been suggested to be important for β-1,4-endoglucanase activation [71] and cleavage of the CDH flavin-containing protein domain [72]. Proteases have previously been connected to the decline of extracellular LiP activities in fungal cultures [73, 74]. In this study, the initially very high and upregulated LiP abundances were slowly decreasing as protease abundances were increasing in the P. radiata wood proteome, thus indicating that some part of the highly secreted and produced enzymes may be degraded by the fungus’ own proteases to recycle the otherwise scarce organic nitrogen pool in the high C/N ratio wood environment. Overall, high peptidase abundances in secretomes of plant biomass-degrading saprotrophic Basidiomycota have been observed [75].

Differences between the abundances of expressed transcripts and detected proteins, and their relation to enzyme activity values at specific time points of the wood cultivation reflect differential and perhaps time-dependent regulation of fungal genes. Alternating processes of gene regulation occurring during (transcriptional regulation) and after transcription (post-transcriptional regulation) may affect the outcome of transcriptomics and proteomics studies. Distinct isoenzyme proteins that are products of individual genes may in turn be active only at certain phase of wood degradation or under specific environmental conditions such as ambient pH [76, 77]. Thus, gene expression analyses, protein detection, and enzymatic activity measurements are not always directly comparable. Moreover, low-molecular-weight proteins, proteins without trypsin cleavage sites or those left intact and attached to the wood matrix, as well as quickly degraded proteins are usually underestimated or lost entirely by peptide LC–MS/MS [39]. However, the clear correlation in time-dependent (higher at the earlier time points) production of proteins with transcript level expression of P. radiata genes encoding the various class-II peroxidases indicates strong transcriptional activation of the genes when the fungus is in contact with wood, a natural lignocellulose substrate for hyphal colonization and growth.

After 42 days of wood colonization, it appears that P. radiata causes simultaneous decay of spruce xylem components proceeding from the wood cell empty lumen side to secondary cell walls towards primary cell wall and tracheid middle lamellae. This is seen as evident thinning and erosion of the secondary cell walls, together with some erosion of middle lamellae and release of the tracheids. Similar wood-decay pattern is observed for other white-rot Polyporales species on gymnosperm wood [78]. Clear indication of degradation of lignin moieties and release of phenolic compounds during the cultivation period (42 days) was demonstrated by pyrolysis–GC/MS although the gravimetric Klason total lignin content (in relation to wood dry weight) demonstrated a slight increase. This may be explained by the apparent simultaneous degradation of wood cell wall cellulose and other polysaccharides at this stage, thus affecting the ratio of lignin content versus content of wood carbohydrates. Coinciding results were obtained in P. chrysosporium cultivations on softwood after 21 days [79].

In a previous study, up to 22 % decrease in Klason lignin content was obtained with the same fungus P. radiata 79 after 70 days of cultivation on Norway spruce wood chips [22]. In our study, spruce wood lignin was attacked and degraded during 42 days by P. radiata to some extent. Pyrolysis–GC/MS analysis demonstrated decrease in the amount of spruce wood phenylpropane units with concomitant increase in the number of smaller fragmented products from these lignin units, suggesting that especially the upregulated lignin peroxidases were actively attacking and converting the predominant non-phenolic structures of the spruce wood coniferous lignin. Lignin peroxidase LiP3 of P. radiata is an efficient oxidizer and degrader of non-phenolic lignin β-O-4 dimeric structures [30, 55]. P. radiata short-MnP3 is active against phenolic lignin compounds [29] and in decomposition of pine wood lignin [28]. Increment of phenolic units after fungal growth on lignocellulose was likewise observed in P. chrysosporium on pre-treated biomass [80]. Although chemical and structural evidence of spruce wood lignin decay was obtained with P. radiata, it appears that a somewhat longer cultivation time (than 6 weeks) is needed to observe a decrease in total lignin content as well as more dramatic wood ultrastructural changes leading to complete tracheid (wood fiber) separation by degradation of middle lamellae.

It appears that P. radiata initiates a strong oxidoreductase and lignin-attacking enzyme expression in contact with wood, which is seen in high transcription upregulation and protein production already during the first weeks upon wood colonization. After this, together with the lignin-attacking and auxiliary oxidoreductases, an array of cellulose and hemicellulose acting GH and CE enzymes is produced, with some changes in protein abundances in the course of the 6 week surveillance and growth on wood. Thus, after the initial lignin-attacking reactivity, at the second stage of wood decay, the P. radiata CAZyme repertoire is more targeted against the wood polysaccharides. The change of strategy is most likely to support supply of readily metabolized carbohydrates (sugars) for energy and biosynthetic metabolic processes. After 42 days of wood colonization, the fungal decay is seen as erosion of the wood cell walls with some release of the tracheids, with evident attack on the lignin subunits leading to release of phenolic and lignin-derived fragmented compounds.

In general, transcriptome analysis supported the proteomic results, thus confirming that majority of the identified CAZy encoding transcripts which were upregulated on wood were also present in the proteome. The transcriptome data indicated a pronounced role especially for a few lignin peroxidases (LiP2, LiP3) and manganese peroxidases (MnP1-long, MnP2-long, MnP3-short), various hydrogen peroxidase generating accessory enzymes (GLOX, AA3 AOX), CE acetyl xylan esterase, and lytic polysaccharide monooxygenases (LPMOs), when P. radiata is actively colonizing and degrading coniferous spruce wood. In addition, various CAZymes against cellulose, and both glucomannan and xylan type of hemicellulose together with constant expression of pectin-degrading enzymes were detected, all adding up to the impressive repertoire of lignocellulose-attacking enzymes expressed by P. radiata upon colonization of spruce wood.