We examined the relationship between the community structure of wood-decaying fungi, detected by high-throughput sequencing, and the decomposition rate using 13 years of data from a forest dynamics plot. For molecular analysis and wood density measurements, drill dust samples were collected from logs and stumps of Fagus and Quercus in the plot. Regression using a negative exponential model between wood density and time since death revealed that the decomposition rate of Fagus was greater than that of Quercus. The residual between the expected value obtained from the regression curve and the observed wood density was used as a decomposition rate index. Principal component analysis showed that the fungal community compositions of both Fagus and Quercus changed with time since death. Principal component analysis axis scores were used as an index of fungal community composition. A structural equation model for each wood genus was used to assess the effect of fungal community structure traits on the decomposition rate and how the fungal community structure was determined by the traits of coarse woody debris. Results of the structural equation model suggested that the decomposition rate of Fagus was affected by two fungal community composition components: one that was affected by time since death and another that was not affected by the traits of coarse woody debris. In contrast, the decomposition rate of Quercus was not affected by coarse woody debris traits or fungal community structure. These findings suggest that, in the case of Fagus coarse woody debris, the fungal community structure is related to the decomposition process of its host substrate. Because fungal community structure is affected partly by the decay stage and wood density of its substrate, these factors influence each other. Further research on interactive effects is needed to improve our understanding of the relationship between fungal community structure and the woody debris decomposition process.
Citation: Yamashita S, Masuya H, Abe S, Masaki T, Okabe K (2015) Relationship between the Decomposition Process of Coarse Woody Debris and Fungal Community Structure as Detected by High-Throughput Sequencing in a Deciduous Broad-Leaved Forest in Japan. PLoS ONE 10(6): e0131510. https://doi.org/10.1371/journal.pone.0131510
Editor: Ligia O. Martins, Universidade Nova de Lisboa, PORTUGAL
Received: February 20, 2015; Accepted: June 3, 2015; Published: June 25, 2015
Copyright: © 2015 Yamashita et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Data Availability: All relevant data are within the paper and its Supporting Information files.
Funding: This study was financially supported by the Japan Environment Agency, and the Environment Research and Technology Development Fund (S9) of the Ministry of the Environment, Japan (http://www.env.go.jp/policy/kenkyu/suishin/english/gaiyou/index.html) to KO.
Competing interests: The authors have declared that no competing interests exist.
In forest ecosystems, more than 90% of primary products flow directly into the decomposition process in the form of detritus . Many biotic factors, such as tree phylogenetic groups, size of trees, and decomposer communities, play an important role in the decomposition process [2, 3]. Variation in these factors among substrates causes marked differences in the decomposition process.
Diverse wood-decaying fungi inhabit woody debris and degrade cellulose, hemicellulose, and lignin more rapidly than do bacteria . Thus, wood-decaying fungi play the most important role in the decomposer community in the decomposition of woody debris [2, 4]. The high diversity of wood-decaying fungi implies a high functional diversity, and thus fungal diversity likely has a positive effect on the decomposition process. Experimental studies on the relationship between fungal diversity and litter and wood decomposition processes revealed positive , negative [6, 7], and neutral  relationships. These studies indicated that complementary effects accelerate degradation, whereas competitive interactions among diverse fungi impede decomposition activity during the initial stage of decomposition [6, 9]. However, few studies have investigated the relationship between fungal community structure and decomposition rate in the field (e.g., ).
Wood-decaying fungi have traditionally been evaluated by observation of fungal fruiting bodies. However, recent molecular studies have identified a great diversity of fungi among ecosystems, including the phyllosphere , forest soil [12, 13], root systems [14, 15], and woody debris [16, 17]. Several studies have revealed that species diversity and species composition determined by an inventory of fruiting bodies, mycelial extraction, or molecular techniques exhibit large differences [17, 18, 19]. Molecular techniques are thought to be more suitable than only the observation of fruiting bodies for detecting wood-inhabiting fungi in dead wood, because these methods may also detect fungal species that are not currently forming fruiting bodies. Therefore, in this study we applied a high-throughput sequencing technique to identify the fungal communities formed within coarse woody debris (CWD).
We investigated the relationship between fungal community structure and the decomposition process by using 13 years of data obtained from a forest dynamics plot. First, we calculated regression curves for the decomposition of two dominant tree genera in a 6-hectare (ha) plot and then evaluated the relative decomposition rates for individual pieces of CWD. We next surveyed fungal community structure in CWD using a high-throughput sequencing technique. Finally, we performed structural equation modeling to reveal the relationships among CWD traits, fungal community structure, and decomposition processes. The decay conditions of CWD determine the fungal community structure, which in turn affects the decomposition process. In this study, we focused on the effect of fungal communities on the decomposition process, rather than on the effect of decay conditions on fungal communities.
Materials and Methods
This study was conducted in a broad-leaved, old-growth forest in Ogawa Forest Reserve (36'56"N, 80 140'35"E; 610–660 m above sea level; permission from the Ibaraki District Forest Office of the Forestry Agency in Japan) in the southern part of the Abukuma Mountains along the Pacific Coast of Japan . The mean annual air temperature and annual precipitation in this forest reserve are 10.7°C and 1910 mm, respectively . Within the 6-ha plot established in this forest, species belonging to Fagaceae are dominant, with Quercus serrata as the most predominant species (total basal area: 8.58 m2/ha), followed by Fagus japonica (6.66 m2/ha), Fagus crenata (2.77 m2/ha), Castanea crenata (1.34 m2/ha), and Quercus mongolica var. grosseserrata (1.20 m2/ha) . Carpinus laxiflora, a member of Betulaceae, has a total basal area of 1.36 m2/ha. All individual trees with a diameter at breast height (DBH) ≥ 10 cm in the 6-ha plot were marked by numbered tags, and we recorded the DBH, tree species, location in the plot, and mortality of each individual every 5 years beginning in 1997.
Characteristics of coarse woody debris
CWD (length ≥ 1 m, DBH ≥ 11 cm), including fallen trunks and snags of Fagus and Quercus, was searched for in the plot in late September 2012. Individual pieces of CWD were identified using numbered tags. If tags were absent from a piece of CWD, the piece was identified using information on DBH, spatial position in the plot, and tree species.
In mid-October 2012, we drilled to a depth of 10 cm into the side of each piece of Fagus and Quercus CWD using a drill bit (2 cm in diameter) and collected drill dust samples from five holes to measure the wood density. Samples were collected at the center, at both ends, and midway between the center and each end of the CWD. If the diameter of the CWD at either end was smaller than 10 cm, we collected samples at the point at which the diameter was 11 cm. In the case of a dead tree that was still standing (i.e., a snag), we collected drill dust from points 20, 60, 100, 140, and 180 cm above the forest floor. Each sample was placed individually in a vinyl bag and transported to the laboratory. For each drill dust sample, we recorded dry weight to the nearest 0.01 g using an electronic balance after oven drying at 70°C for 72 h.
We collected another set of drill dust samples for extraction of fungal DNA from 10 holes (1 cm in diameter, 10 cm in depth) in the CWD. The arrangement of the holes was identical to that used for the wood density measurement, but drill dust was obtained from both sides of the CWD. Before drilling, we flame-sterilized the drill bit and the surface of the CWD after spraying with ethanol. All drill dust samples from each piece of CWD were placed in a single sterilized vinyl bag and stored at -20°C until molecular analysis.
DNA extraction and PCR
After mixing thoroughly, each drill dust sample was frozen in liquid nitrogen and crushed using a mortar and pestle. DNA was extracted from the drill dust sample (300 mg) using the DNeasy Plant Mini Kit (Qiagen). We obtained 48 total DNA samples from the wood. The method of Caporaso et al.  was adapted for molecular analysis. In brief, the V9 region of 18S ribosomal DNA was targeted. Genomic DNA samples, at a 1:10 dilution, were PCR-amplified in triplicate reactions using primers tagged for each sample, and each 1-μl DNA sample was added to a 25-μl reaction mixture containing 12.5 μl GoTaq premix (Promega Co. Ltd) and 10 pmol each primer (Illumina_Euk_1391f and Illumina_EukBr) . PCR was initiated by a 4-min denaturation step at 95°C, followed by 35 cycles of 45 s at 94°C, 60 s at 57°C, and 90 s at 72°C, with a final extension for 10 min at 72°C using a GeneAmp 9700 thermal cycler (Perkin-Elmer Applied Biosystems). Amplicons were purified by agarose gel electrophoresis, quantified using a Qubit 2.0 Fluorometer (Life Technologies Japan Co. Ltd.) and pooled at equimolar concentrations into a single volume. The pooled amplicon was sequenced by Illumina Miseq at Frontier Science Research Center, Miyazaki University. The raw sequencing data were deposited as BioProject ID PRJDB3758 on DDBJ Sequence Read Archive (http://trace.ddbj.nig.ac.jp/dra/index.html). The technique described above may also have resulted in detection of inactive fungi.
Operational taxonomic units
The sequencing data were de-noised and filtered using the QIIME software package version 1.8  (The mapping file required in QIIME was deposited in S1 Table). Our molecular analysis detected not only DNA derived from wood-decaying fungi but also DNA derived from other organisms belonging to Eukaryota. We eliminated eukaryotes other than fungi and included molecular operational taxonomic units (OTUs) belonging to Agaricomycotina, Saccharomycotina, Orbiliomycetes, Leotiomycetes, and Sordariomycetes in the analysis, because they are considered major wood-decaying fungi . We adopted the closed-reference OTU picking process as the OTU picking strategy in QIIME . In this process, reads are clustered against the reference sequence data, and the reads that do not align with sequences in the dataset are excluded. We used datasets comprising small subunit ribosomal RNA sequences from the Silva database release 111 , as a reference for each OTU in QIIME. In our preliminary analysis, many reads did not result in a sequence hit within the dataset, but the count of each was fewer than 100 reads. In addition, the phylogenetic position of unassigned reads cannot be determined using phylogenetic analysis, and their function cannot be predicted. Thus, such reads were excluded from the analysis.
In the dataset, the CWD samples varied in the number of obtained sequencing reads, which resulted in variance in the number of OTUs per CWD sample. To avoid the effect of differences in sequencing depth on the occurrence of OTUs, we applied rarefaction to the dataset using the "rrarefy" function in R. Before rarefying, all OTUs with fewer than 100 reads were excluded from the analysis to prevent inclusion of rare fungal OTUs in the results. The dataset was rarefied to a depth of 1,603 reads (minimum number of reads in the CWD samples; S2 Table). Read counts of each OTU were used as an indicator of abundance. When necessary, the dataset was divided into two groups according to tree genus.
We evaluated the decomposition rate index of each CWD. We assigned a time since death value to each CWD based on forest dynamics data. The year of death of the sampled tree was assigned as the midpoint between the year that tree survival was last confirmed and the year that tree mortality was confirmed. For example, 1999 was chosen as the year of death for trees that died at some point between 1997 and 2001. The time since death was then determined by calculating the difference between the survey year (2012) and the year of death.
The relationship between wood density and time since death was regressed by the following negative exponential model: where D is wood density, k is the decomposition constant (year-1), t is time since death, and a is a constant. Then, expected values of wood density for each CWD were estimated using the obtained regression. We constructed separate regression curves for Fagus and Quercus. Residuals between the expected value of wood density and the observed value were used as an index of the decomposition rate. Large positive index values indicate rapid decomposition, whereas large negative values indicate slow decomposition.
Fungal community structure was evaluated by the number of OTUs, OTU composition, and evenness. The unconstrained ordination method was used to compare fungal OTU composition among CWD samples. Detrended correspondence analysis (DCA) was performed as a preliminary analysis to assess the gradient length for each dataset. The results indicated that the lengths of the Fagus and Quercus CWD datasets were 2.222 and 1.779, respectively. These results suggest that the response curves could be monotonic, and thus we considered principal component analysis (PCA) to be appropriate. DCA and PCA were performed using PC-ORD version 6 . We used the PCA scores for the three axes (first, second, and third) as variables for the OTU composition of wood-decaying fungi in the following analysis. Number of read counts was log10-transformed before PCA analysis. Fungal OTUs with fewer than 10 reads after rarefaction were excluded from the analyses. We used Simpson’s measure of evenness (E1/d) [27, 28] as an index of evenness in the fungal community structure. E1/d ranges from 0 to 1 and takes a value of 1 when community composition is completely even.
We used a structural equation model (SEM) to determine how strongly fungal community traits affected the decomposition rate and how the fungal community structure was determined by CWD traits (DBH and time since death). We determined Pearson’s correlation coefficients between CWD and fungal community traits before conducting the SEM analysis to reduce the interactions among variables. If the absolute value of the coefficient was less than 0.2, we omitted the interactions among variables from the SEM analysis. We assumed that CWD traits affected fungal community traits and that both CWD and fungal community traits affected the decomposition rate. We also assumed that fungal community traits potentially vary relative to one another, with the exception of PCA scores. We evaluated the fitness of the model by performing a chi-squared test (p > 0.05 indicates a good fit) and by evaluating the comparative fit index (CFI > 0.95 indicates a good fit), the root mean square error of approximation (RMSEA < 0.05 indicates a good fit), and the standardized root mean square residual (SRMSR = 0 indicates a good fit). All variables were z-transformed for normalization before analysis. SEM analysis was performed using the “Lavaan” package in the R software for Windows 3.0.2 .
A two-way cluster analysis was conducted on the OTUs and the Fagus and Quercus CWDs to identify groups. We performed the analysis using Euclidean distances and Ward’s linkage method using PC-ORD version 6. The number of read counts was log10-transformed prior to analysis.
Decomposition process of coarse woody debris
In the study plot, 6, 16, and 11 pieces of Fagus CWD and 6, 2, and 7 pieces of Quercus CWD were obtained between 1997 and 2001, 2001 and 2005, and 2005 and 2009, respectively. The relationship between wood density and time since death was significant for Fagus (D = 0.4572e-0.085t, R² = 0.2412, p = 0.004), but not for Quercus (D = 0.5311e-0.020t, R² = 0.1548, p = 0.147; Fig 1).
A total of 421 OTUs of Eukaryota from 1,242,841 reads with a length of 250 bp were recorded, and 166 OTUs of fungi from a total of 1,028,993 reads were recorded. For wood-decaying fungi, 120 and 112 OTUs, including singletons, were collected from Fagus and Quercus, respectively. After excluding those OTUs with fewer than 100 reads, 70 OTUs belonging to wood-decaying fungi were recorded from Fagus and Quercus each (S2 and S3 Tables).
In Fagus CWD, the number of reads ranged from 1,603 to 89,661. Phallus hadriani (Agaricales), Neolentinus lepideus (Agaricales), Callistosporium graminicolor (Agaricales), Poria cocos (Agaricales), and Ceraceomyces borealis (Agaricales) were the dominant OTUs in Fagus (reads > 5%). After rarefication, the number of OTUs ranged from 18 to 48 (S1 Fig), and evenness ranged from 0.048 to 0.142.
In Quercus CWD, the numbers of reads ranged from 5,346 to 40,216. Hericium erinaceum (Agaricales), Basidiomycete INF1-B (Agaricales), N. lepideus, C. graminicolor, Artomyces pyxidatus (Agaricales), and Neobulgaria premonophila (Leotiales) were the dominant OTUs among Quercus (reads > 5%). After rarefication, the number of OTUs ranged from 20 to 44 (S1 Fig), and evenness ranged from 0.045 to 0.261.
OTUs from Agaricomycetes were dominant in both Fagus (S2 Fig) and Quercus (S3 Fig) CWDs. Of 33 Fagus CWDs, 29 were dominated by OTUs from Agaricomycotina, whereas four CWDs were dominated by Leotiales or Saccharomycotina. The relative abundance of the dominant OTUs ranged from 28.2 to 94.5% (58.0± 19.3; average± SD). Of 15 Quercus CWDs, 13 and 2 were dominated by Agaricomycotina and Leotiomycetes, respectively. The relative abundance of the dominant OTUs ranged from 23.0 to 94.6% (65.9 20.0, average SD).
CWDs were divided into two large clusters according to fungal OTU composition (Fig 2). Both Fagus and Quercus belonged to each group. Fungal OTUs were also divided into two groups. One group comprised OTUs with high abundance. In this group, Neolentinus lepideus (Agar2) and Callistosporium graminicolor (Agar3) were observed in almost all CWDs. Five OTUs from Leotiomycetes formed a small cluster in this group. The other group comprised OTUs with low abundance. OTUs belonging to the latter group were observed sporadically.
Each row represents a CWD, and each column represents an OTU. Columns are clustered according to the abundance of OTUs on CWDs, whereas rows are clustered according to the composition of OTUs. Numbers in the heat map show the matrix coding values, which were relative percent abundance within the matrix.
Principal component analysis
In the PCA results for OTU composition of Fagus CWD, the first, second, and third axes explained 12.4%, 8.0%, and 7.4% of the total variance in the OTU data, respectively (Fig 3). In the PCA diagram for PCA scores of the first and third axes, CWDs produced 9 or 13 years ago were plotted in the middle or upper area, respectively, along the PC3 axis, whereas some of the CWDs produced 5 years ago were plotted in the lower area along the PC3 axis.
Fungal OTUs are presented by subdivision or class to avoid redundancy.
In the PCA results for OTU composition of Quercus CWD, the first, second, and third axes explained 19.8%, 16.9%, and 12.8% of the total variance in the OTU data, respectively (Fig 4). In the PCA diagram for PCA scores of the first and second axes, all CWDs produced 13 years ago were plotted on the lower side, whereas five of seven CWDs produced 5 years ago were plotted on the upper side.
Structural equation model analysis
Pearson’s correlation coefficient was determined before SEM was performed. In Fagus, the relationships between DBH and evenness and between time since death and evenness and the PCA score of the third axes showed correlation coefficients greater than 0.2 (Table 1A). All of the fungal community structure traits were correlated moderately with the decomposition rate index (correlation coefficient > 0.2). The number of OTUs and the PCA scores of the second axes were significantly correlated with the decomposition rate index (p < 0.05, S4 Fig). CWD traits (DBH and time since death) were poorly correlated with the decomposition rate index (correlation coefficient < 0.2). In Quercus, DBH was moderately correlated with evenness and the PCA score of the first and third axes (Table 1B). Time since death was correlated with evenness and the PCA score of the second axis. The decomposition rate was moderately correlated with DBH and evenness. No indices of fungal community structure traits were significantly correlated with the decomposition rate index (p > 0.05, S5 Fig).
SEM for the decomposition process of Fagus CWD showed a nearly good fit: the p-value by chi-squared test was 0.113, CFI was 0.929, RMSEA was 0.117, and SRMSR was 0.064. In the SEM for Fagus (Fig 5), the strongest predictor of the decomposition rate index was the PCA scores of the second axis, with a standardized partial regression coefficient of 0.377 (p = 0.014). The standardized partial regression coefficient of PCA scores of the third axis and the decomposition rate index were 0.354 (p = 0.009). Time since death significantly affected the PCA scores of the third axis (standard coefficient = 0.410, p = 0.010). The number of OTUs varied with evenness and with the PCA scores of the first and second axes. Evenness varied with the PCA scores of the first axis.
Numbers beside the arrows represent path coefficients. All paths included in the analysis are presented. Straight single-headed arrows represent causal pathways. Curved, double-headed arrows indicate covarying variables. Thick, straight, black arrows indicate significant causal pathways at the level of p < 0.05. Thick, gray, curved arrows indicate significant covarying relationships at the level of p < 0.05. Dashed, straight, curved arrows indicate non-significance (p > 0.05).
The SEM results for the decomposition process of Quercus CWD showed a good fit: the p-value by chi-squared test was 0.916, CFI was 1.000, RMSEA was 0.000, and SRMSR was 0.085. In the SEM for Quercus (Fig 6), the strongest predictor of the decomposition rate index was the PCA scores of the first axis, with a standardized partial regression coefficient of 0.488 (p = 0.464), although this was not significant at the level of p < 0.05. No other factor showed a significant effect on the decomposition rate index. The PCA scores of the first and second axes were significantly affected by DBH (standard coefficient = -0.371, p = 0.008) and by the time since death (standard coefficient = -0.700, p < 0.001), respectively. The number of OTUs varied significantly with the PCA scores of the first and third axes.
This study focused on the relationships among CWD traits, fungal community structure, and decomposition processes of Fagus and Quercus CWD. Our analyses revealed three major findings: (1) the decomposition rate of Fagus was greater than that of Quercus, (2) the fungal community compositions of both Fagus and Quercus CWD changed over time, and (3) the decomposition rate of Fagus CWD was affected by two components of community composition, one that was affected by time since death and another that was not affected by CWD traits but was correlated with the number of OTUs. These findings suggest that fungal community structure is related to the decomposition process of its host substrate, and that the relationship between fungal community structure and decomposition rate is partly affected by CWD traits.
Succession—changes in species composition according to the progression of decay class or time since death of woody debris—has been well described for wood-decaying fungi and related microbes [10, 30, 31]. In a previous study of the fungal community formed on Fagus logs, fungal species differed with regard to the substrates that they could decompose efficiently, and fungal succession depended on the chemical traits of the substrate . Thus, it is possible that rapid changes in fungal community composition promote rapid decomposition.
Although many studies have examined the relationships between ecosystem functioning and community structure traits, most have been limited to grassland ecosystems  and crop–pollinator systems . With regard to a decomposition system, fungal diversity is thought to affect the decomposition process both positively  and negatively [6, 7]. In the SEM analysis, we did not detect a significant relationship between the number of OTUs and decomposition rate, but there was a significant relationship between fungal OTU composition and decomposition rate; moreover, the number of OTUs was significantly correlated with fungal community composition. Therefore, in the case of Fagus CWD, the fungal community composition is more strongly related to the decomposition rate than is species diversity.
Fungal community structure for both tree genera were not always explained by the CWD traits. Previous studies showed that the community structure of wood-decaying fungi in a log was affected by wood density, chemical components, moisture content, and log type (e.g., branch, fallen trunk, stump) [19, 35, 36, 37], and these factors may have determined the community composition at our study site. However, because fungal species appear to disperse randomly at the spatial scale of a few hundred meters , the spatial structure of CWD at our small study site may not have had a marked effect on the fungal community structure in this study. Elucidating the interaction between fungi and other saprotrophs, such as bacteria, is also important for understanding the decomposition process. The coexistence of fungi and bacteria stabilizes the decomposition process , and commensal interactions between wood-decaying fungi and nitrogen-fixing bacteria are assumed due to their pattern of co-occurrence in CWD . Further studies that include other saprotrophs are needed to understand the relationships between fungal community structure and the decomposition process (see also [41, 42] for wood-inhabiting Myxomycetes and bacteria detected by molecular technique and  for interaction between wood-decaying fungi and cryptogam species).
The relationship between fungal community structure and decomposition rate varied with tree genus. In Quercus, although the fungal community composition changed over the 13-year period, decomposition did not proceed much during this time. Possibly because of this slow decomposition rate and the small variation in the difference in decomposition rate among CWDs, our SEM analysis did not detect a significant relationship between fungal community structure and the decomposition rate of Quercus. This variation among tree genera in the relationship between fungal community structure and the decomposition process requires further research.
The history of community assembly is an important factor in the decomposition process of CWD. Fungi that arrive at a resource unit earlier than others exploit resources and change the chemical composition of CWD during the decay process [44, 45], and they sometimes competitively interact with other fungi that later colonize the resource . Thus, competitive interactions, including the production of secondary metabolites for antagonistic interactions, are important factors in the formation of fungal communities [46, 47]. Perhaps because of such processes, priority effects strongly influence the community structure of wood-decaying fungi and the resulting decomposition process [6, 48]. Such interspecific interactions among fungi also likely affected the assembly of the established fungal communities observed in this study.
We detected 70 OTUs of fungi within CWD of both Fagus and Quercus. In a previous study on fungal fruiting bodies conducted in the same study forest, 35 and 30 species were recorded in Fagus and Quercus CWD, respectively . Although the molecular techniques used here revealed high fungal diversity, none of the species detected by observation of fruiting bodies were present in the molecular dataset. Our field survey of fungal fruiting bodies was conducted in 2002 and was limited to aphyllophoraceous fungi, which may explain the discrepancies between these data. In addition, recent studies have reported that the fungal community structure detected by observation of fungal sporocarps is clearly different from that detected by mycelium extracted using a molecular technique [16, 18]. These findings indicate that recently developed methods using high-throughput sequencing fail to detect certain fungal species in CWD.
We used the estimated time since death to illustrate the temporal dynamics of both the decomposition process and fungal community structure. Wood decay stage, instead of time since death, is typically used as an index of CWD age. However, errors in the estimated time since death in this study may be smaller than those based on decay stage. For example, decay stages 3 to 7 in spruce covered CWD from less than 10 years to more than 70 years old . On the other hand, when the focus of the study is the decomposition process, the time since death is usually estimated more accurately than it was in this study. Although our recorded time since death and the actual time since death could differ by as much as 4 years because of our survey schedule, the shape of the curve seemed to be a reasonable expression of the decomposition process. In addition, our decomposition constant for Fagus (k = 0.085) fell within the range of 0.045 to 0.178 reported for Fagus sylvatica  and was similar to that reported from Germany (k = 0.089) . Likewise, our decomposition rate constant for Quercus (0.020) fell within the range of 0.0175 to 0.26 obtained from Quercus petrea . In Quercus, the loss of outer bark and sapwood occurs within 2 years of tree death . If the same pattern of decomposition is common to both genera, then we underestimated the decomposition rate of CWD in this study. However, our obtained values are not much different from those reported previously.
This is one of the few studies to examine the relationship between fungal community structure and decomposition process under natural conditions. We found that the community composition and evenness of wood-decaying fungi partly determined the decomposition rate of a dominant tree genus, Fagus, in a Japanese temperate forest. Because fungal community structure is partly affected by decay stage, wood density and macronutrient composition of its substrate, CWD traits affect the colonization and establishment of the fungal community, which in turn affects the condition of CWD. Evaluations of these interactive effects are necessary to understand the temporal dynamics of the relationships between fungal community structure and the decomposition process.
S2 Table. Raw data used in this study.
The number of reads was rarefied.
S3 Table. List of OTUs identified from CWD of Fagus and Quercus.
S1 Fig. Frequency distribution of the rarefied numbers of OTUs obtained from CWD of Fagus and Quercus.
S2 Fig. Fungal community composition of each Fagus CWD at higher taxonomic levels.
Abbreviations on each column represent the dominant OTU in each CWD. See S3 Table for the abbreviations.
S3 Fig. Fungal community composition in each Quercus CWD at higher taxonomic levels.
Abbreviations on each column represent the dominant OTU in each CWD. See S3 Table for the abbreviations.
S4 Fig. Residual between the expected wood density of Fagus CWD and the observed wood density plotted against the indices of fungal community traits formed on each CWD.
A large positive value of the residual indicates faster than expected decomposition.
S5 Fig. Residual between the expected wood density of a Quercus CWD and the observed wood density plotted against the indices of fungal community traits formed on each CWD.
A large positive value of the residual indicates faster than expected decomposition.
We thank Taisei Kikuchi (Faculty of Medicine, University of Miyazaki) for assistance with the molecular studies.
Conceived and designed the experiments: SY KO HM. Performed the experiments: SY HM SA TM. Analyzed the data: SY HM. Contributed reagents/materials/analysis tools: HM KO. Wrote the paper: SY HM.
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