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Research article

The effect of light and nitrogen availability on the caffeine, theophylline and allantoin contents in the leaves of Coffea arabica L.

  • Received: 29 June 2013 Accepted: 27 September 2013 Published: 27 September 2013
  • Caffeine is the most abundant and important purine alkaloid derived from several important crop, such as coffee, tea, cocoa, guarana, and other plants. In tea and coffee plants, caffeine is predominantly produced in the young buds of leaves and in immature fruits. The effect of light-stimulating caffeine biosynthesis is uncertain, but our results clearly show that light, independent of N-availability, increases caffeine (26%), allantoin (47%), and theophylline (8%) content in plants compared with those grown in a shaded (50% solar irradiation) environment. Caffeine is the major low-molecular-weight nitrogenous compound in coffee plants, and at times, it functions as a chemical defense for new bud leaves. Therefore, the primary question that remains is whether caffeine can serve as a nitrogen source for other metabolic pathways. If so, plants grown under a low nitrogen concentration should promote caffeine degradation, with the consequent use of nitrogen atoms (e.g., in NH3) for the construction of other nitrogen compounds that are used for the plant's metabolism. Our results provide strong evidence that caffeine is degraded into allantoin at low rates in N-deficient plants but not in N-enriched ones. By contrast, this degradation may represent a significant N-source in N-deficient plants.

    Citation: Marcelo F. Pompelli, Gilmara M. Pompelli, Antônio F. M. de Oliveira, Werner C. Antunes. The effect of light and nitrogen availability on the caffeine, theophylline and allantoin contents in the leaves of Coffea arabica L.[J]. AIMS Environmental Science, 2014, 1(1): 1-11. doi: 10.3934/environsci.2013.1.1

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  • Caffeine is the most abundant and important purine alkaloid derived from several important crop, such as coffee, tea, cocoa, guarana, and other plants. In tea and coffee plants, caffeine is predominantly produced in the young buds of leaves and in immature fruits. The effect of light-stimulating caffeine biosynthesis is uncertain, but our results clearly show that light, independent of N-availability, increases caffeine (26%), allantoin (47%), and theophylline (8%) content in plants compared with those grown in a shaded (50% solar irradiation) environment. Caffeine is the major low-molecular-weight nitrogenous compound in coffee plants, and at times, it functions as a chemical defense for new bud leaves. Therefore, the primary question that remains is whether caffeine can serve as a nitrogen source for other metabolic pathways. If so, plants grown under a low nitrogen concentration should promote caffeine degradation, with the consequent use of nitrogen atoms (e.g., in NH3) for the construction of other nitrogen compounds that are used for the plant's metabolism. Our results provide strong evidence that caffeine is degraded into allantoin at low rates in N-deficient plants but not in N-enriched ones. By contrast, this degradation may represent a significant N-source in N-deficient plants.


    Fungi are eukaryotic microorganisms that serve as a major component of soil biodiversity and play crucial roles in the functioning of soil as decomposers [1]. Fungi are unique in that they are capable of actively attacking lignin in dead plant residues resistant to microbial degradation [2],[3]. The selective decomposition of lignin by fungi results in the white rot of wood and the bleaching of leaf litter [4],[5]. Previous studies on the diversity and ecology of ligninolytic fungi have paid special attention to the Basidiomycota occurring on wood [6], whereas information about the Ascomycota colonizing leaf litter is scarce, even though Xylariaceae and Hypoxylaceae fungi from the Ascomycota group are well-known for their ligninolytic activity [7],[8]. Also, recent studies often encountered ascomycete fungi on bleached portions of leaf litter in subtropical [9] and temperate [10] regions. However, there is a lack of knowledge regarding the diversity patterns of Xylariaceae and Hypoxylaceae fungi on leaf litter from different tree species and between climatic regions.

    The purpose of the present study was to investigate the alpha and beta diversity of Xylariaceae and Hypoxylaceae fungi undertaking lignin decomposition from leaf litter of subtropical and cool temperate tree species in Japan. In this context, we selected nine tree species that are major forest components in these climatic regions and isolated fungi responsible for the bleaching of leaf litter of these tree species. The dataset was then analyzed using rarefaction analysis, nonmetric multidimensional scaling, and one-way permutational multivariate analysis of variance to test the hypothesis that fungal alpha and beta diversity were different among tree species and between subtropical and cool temperate regions.

    Samples were collected from two study sites in Japan—a subtropical forest in Yona, Okinawa (26°44′17″–32″N, 128°13′60″–14′9″E, 250–330 m a.s.l.) and a cool temperate forest in Sanada, Nagano (36°31′5″–36°40′24″N, 138°13′7″–21′11″E, 1280–1340 m a.s.l.) (Figure S1). Mean annual temperature of the subtropical and cool temperate forests was 21.8 °C and 6.9 °C, respectively, and mean annual precipitation was 2680 mm and 1200 mm, respectively. The subtropical forest is located in the northern part of Okinawa Island in southern Japan and is dominated by Castanopsis sieboldii (Makino) Hatusima (Fagaceae) and Schima wallichii (DC.) Korthals (Theaceae) [11]. Seven evergreen broad-leaved tree species from six families were selected (Table 1) as these are major or dominant components of the forest. Sampling was conducted once in September 2020 at four forest stands around the Yona Experimental Forest of the University of the Ryukyus. The cool temperate forest is located in the central part of Honshu Island in central Japan and is dominated by the deciduous broad-leaved tree species Fagus crenata Bl. and Quercus crispula Bl. (Fagaceae). These two dominant tree species were selected (Table 1), and sampling was conducted once in August 2020 at four forest stands in and around the Sugadaira Montane Research Center of University of Tsukuba. The quadrats (5 × 5 m) were arbitrarily selected beneath the tree canopy and at least 30 m from each other. Sampling of 10 bleached leaves was done per quadrat, with 3–9 quadrats per tree species, in a total of 7 and 2 tree species in the subtropical and cool temperate forest for a total of 320 and 160 leaves, respectively (Table 1). Leaf litter with evident bleaching on the leaf surface and in which the original leaf area was preserved were collected from the surface of the forest floor within the quadrats. Leaves were placed in paper bags, preserved at room temperature (approximately 15–20 °C), and taken back to the laboratory.

    Single leaf disks were excised from the bleached portion of individual leaves using a sterile 6 mm diameter cork borer. One leaf disk was excised per leaf, producing a total of 480 leaf disks of bleached portions for the isolation of fungi. Fungi were isolated from the disks using the surface disinfection method [12] using modified lignocellulose agar. Putative Xylariaceae and Hypoxylaceae fungi that produced anamorphic conidia and conidiophores on the plates, such as Xylocoremium, Geniculosporium, and Nodulisporium, and/or dark pseudosclerotinial plates in submerged hyphae were subcultured to establish pure cultures. These isolates were then tested for their potential ability to bleach leaf litter under a pure culture condition, according to the method described previously [9], using sterilized newly shed leaves of C. sieboldii for subtropical isolates and F. crenata for cool temperate ones. Fungal isolates that caused the bleaching of sterilized leaves under the pure culture condition were regarded as ligninolytic fungi and analyzed further.

    The rDNA ITS sequences of the ligninolytic fungal isolates were analyzed, following methods described previously [9] and using primer pairs of ITS1F and LR3. The ITS sequences that originated from isolates were grouped into operational taxonomic units (OTUs) according to the 97% similarity criterion and were then assembled using VSEARCH as implemented in Claident pipeline v0.2.2018.05.29 (Table S1) (software available online: https://www.claident.org/). For each of the OTUs, taxonomic identification was conducted based on the query-centric auto-k-nearest neighbor (QCauto) method [13] with the reference database from International Nucleotide Sequence Database Collaboration (INSDC) and subsequent taxonomic assignment with the lowest common ancestor (LCA) algorithm as implemented in Claident. The ITS sequences were also compared with the rDNA sequences available in the GenBank database by means of BLAST+ [14]. The ITS sequences determined in the present study were deposited in the DNA Data Bank of Japan (DDBJ) (LC821383–LC821630) (Table S2). We retrieved one fungal isolate of each OTU per leaf disk even when two or more isolates of the same OTU appeared.

    Table 1.  Location and climatic region of study sites, tree species examined, and the summarized results of isolation of Xylariaceae and Hypoxylaceae fungi. Values indicate mean ± standard error. The same letters indicate that there is not a significant difference at the 5% level by Tukey's HSD test.
    Location (Climate) Tree species Plant family Code Number of leaves examined Number of leaves isolated Total number of fungal OTUs Mean number of fungal OTUs
    Yona, Okinawa Castanopsis sieboldii Fagaceae Cs 60 41 (68.3%) 9 0.68 ± 0.10 ab
    (Subtropical) Schima wallichii Theaceae Sw 60 29 (48.3%) 9 0.48 ± 0.08 abc
    Neolitsea sericea Lauraceae Ns 50 25 (50.0%) 9 0.50 ± 0.09 abc
    Machilus thunbergii Lauraceae Mt 40 23 (57.5%) 6 0.58 ± 0.11 abc
    Elaeocarpus japonicus Elaeocarpaceae Ej 40 34 (85.0%) 11 0.85 ± 0.12 a
    Distylium racemosum Hamamelidaceae Dr 40 28 (70.0%) 10 0.70 ± 0.13 ab
    Myrica rubra Myricaceae Mr 30 21 (70.0%) 4 0.70 ± 0.12 ab
    Sanada, Nagano Fagus crenata Fagaceae Fc 90 31 (34.4%) 13 0.34 ± 0.06 bc
    (Cool temperate) Quercus crispula Fagaceae Qc 70 16 (22.9%) 11 0.23 ± 0.05 c

     | Show Table
    DownLoad: CSV

    A datasheet was constructed showing the presence/absence of individual fungal OTUs on the 480 leaf disks from the nine tree species. The frequency of occurrence of each OTU was then calculated for individual tree species as a percentage of the number of leaf disks from which that particular OTU was isolated with respect to the total number of leaf disks examined (i.e., 30–90). A generalized linear model (GLM) was used to examine the effects of tree species on the number of fungal OTUs. The glm function of R software was used to perform the analysis, with the glht function of the ‘multcomp’ package for multiple comparisons with Tukey's test. Rarefaction analysis was then conducted to compare the number of fungal OTUs between the tree species by adjusting the difference in the number of fungal isolates across tree species, using the specaccum function with the method ‘coleman’ of the vegan package of R software [15]. Next, nonmetric multidimensional scaling (NMDS) with the Jaccard distance metric was used to analyze the variation of fungal OTU composition between tree species. The NMDS analysis was carried out with the metaNDS function with the default settings of the vegan package. One-way permutational multivariate analysis of variance (PERMANOVA) was then conducted to test the effect of tree species on the dissimilarity of OTU composition. Data of singleton OTUs were excluded from the dataset when performing NMDS and PERMANOVA. Moreover, datasets of subtropical and cool temperate trees were analyzed separately in NMDS and PERMANOVA as there was no overlap of fungal OTUs between these regions. All analyses were performed using RStudio for Macintosh version 1.4.1717.

    A total of 248 fungal isolates were obtained from 202 (42.1%) of the 480 leaf disks examined for nine tree species, with 16–41 isolates per tree species (Table 1). The frequency at which fungi were isolated in leaves was generally higher in subtropical tree species (48.3%–85.0%) than in cool temperate tree species (22.9%–34.4%). The 248 fungal isolates were classified into 43 OTUs at the 97% similarity threshold and were assigned to Xylariaceae (36 OTUs) and Hypoxylaceae (7 OTUs) (Table 2; Figure S2). Claident assigned these OTUs to nine genera, with the most OTU-rich genus being Xylaria (Xylariaceae, 18 OTUs), followed by Nemania (Xylariaceae, 11 OTUs), Hypoxylon (Hypoxylaceae, 5 OTUs), Biscogniauxia (Xylariaceae, 3 OTUs), Annulohypoxylon and Daldinia (Hypoxylaceae, 1 OTU each), and Nodulisporium, Rosellinia, and Whalleya (Xylariaceae, 1 OTU each). The remaining OTU belonged to Xylariaceae but was not assigned to a genus. There was no overlap of fungal OTUs between subtropical (24 OTUs) and cool temperate tree species (19 OTUs), and all seven Hypoxylaceae OTUs were isolated from cool temperate trees (Table 2). The most abundant OTU was Xylaria cubensis OTU_20 isolated from seven subtropical leaves, accounting for 116 (46.8%) of the 248 isolates, followed by Nemania diffusa OTU_03 (14 isolates, 5.6%) from cool temperate leaves and N. diffusa OTU_21, Xylaria sp. OTU_24, and X. cubensis OTU_27 (13 isolates each, 5.2%) from subtropical leaves. Twenty-six (61.0%) of the 43 OTUs were detected only once and were singletons (Table 2), with 12 and 14 being from cool temperate and subtropical trees, respectively.

    The total number of fungal OTUs per tree species ranged from 4 to 13, and the mean number of fungal OTUs was significantly higher in Elaeocarpus japonicus and other subtropical tree species than in Quercus crispula and Fagus crenata from the cool temperate region (Table 1). Rarefaction curves depicting the numbers of OTU with respect to the number of leaves from which fungi were isolated indicated that, in the present study, the OTU richness of the nine tree species did not reach asymptotes (Figure 1). This tendency was primarily attributed to the relatively high number of singleton OTUs (Table 2). The rarefaction curve was generally less steep in the seven subtropical trees than in the two cool temperate trees (Figure 1A), due to the dominance (i.e., relatively high frequency of occurrence) of X. cubensis OTU_20 in the subtropical trees and the greater proportions of singleton OTUs in the cool temperate trees. In addition, we combined the data for subtropical and cool temperate tree species to construct two datasets and two rarefaction curves for these climatic regions, because the OTU compositions were not significantly different among leaves of the tree species from the respective climatic regions (see below). The rarefaction curve was again less steep in the subtropical than in the cool temperate dataset (Figure 1B), reflecting the dominance of major OTUs in the subtropical trees and indicating the greater species richness in cool temperate regions.

    Dissimilarity of OTU composition was ordinated using NMDS separately for seven subtropical and two cool temperate trees, resulting in wide variations within single tree species and general overlaps among tree species in the respective climatic regions (Figure 2). In the PERMANOVA, the OTU composition was not significantly different between tree species both for subtropical (F = 1.2918, p = 0.143) and cool temperate datasets (F = 2.1909, p = 0.055).

    Table 2.  Taxon and frequency of occurrence of 43 fungal OTUs.
    OTU Taxon Family Subtropical
    Cool temperate
    Cs Mr Sw Ej Ns Mt Dr Fc Qc
    OTU_20 Xylaria cubensis Xylariaceae 36.7 53.3 26.7 40.0 30.0 40.0 27.5 0.0 0.0
    OTU_21 Nemania diffusa Xylariaceae 10.0 0.0 6.7 5.0 0.0 0.0 0.0 0.0 0.0
    OTU_22 Nemania bipapillata Xylariaceae 8.3 0.0 0.0 5.0 6.0 0.0 0.0 0.0 0.0
    OTU_23 Xylaria sp. Xylariaceae 1.7 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0
    OTU_24 Xylaria sp. Xylariaceae 3.3 10.0 3.3 5.0 2.0 5.0 2.5 0.0 0.0
    OTU_25 Xylaria sp. Xylariaceae 1.7 0.0 0.0 0.0 0.0 0.0 2.5 0.0 0.0
    OTU_26 Xylaria sp. Xylariaceae 3.3 0.0 1.7 2.5 0.0 0.0 0.0 0.0 0.0
    OTU_27 Xylaria cubensis Xylariaceae 1.7 3.3 1.7 10.0 0.0 2.5 12.5 0.0 0.0
    OTU_28 Nodulisporium sp. Xylariaceae 1.7 0.0 1.7 2.5 0.0 0.0 2.5 0.0 0.0
    OTU_29 Xylaria sp. Xylariaceae 0.0 3.3 1.7 5.0 0.0 2.5 2.5 0.0 0.0
    OTU_30 Xylaria cubensis Xylariaceae 0.0 0.0 1.7 5.0 2.0 5.0 0.0 0.0 0.0
    OTU_31 Nemania diffusa Xylariaceae 0.0 0.0 1.7 0.0 0.0 0.0 0.0 0.0 0.0
    OTU_32 Biscogniauxia petrensis Xylariaceae 0.0 0.0 0.0 2.5 0.0 0.0 0.0 0.0 0.0
    OTU_33 Nemania abortiva Xylariaceae 0.0 0.0 0.0 2.5 0.0 0.0 0.0 0.0 0.0
    OTU_34 Xylaria sp. Xylariaceae 0.0 0.0 0.0 0.0 2.0 0.0 0.0 0.0 0.0
    OTU_35 Xylaria cubensis Xylariaceae 0.0 0.0 0.0 0.0 2.0 0.0 0.0 0.0 0.0
    OTU_36 Xylaria cubensis Xylariaceae 0.0 0.0 0.0 0.0 2.0 0.0 0.0 0.0 0.0
    OTU_37 Nemania bipapillata Xylariaceae 0.0 0.0 0.0 0.0 2.0 0.0 0.0 0.0 0.0
    OTU_38 Xylaria sp. Xylariaceae 0.0 0.0 0.0 0.0 2.0 0.0 0.0 0.0 0.0
    OTU_39 Xylaria cubensis Xylariaceae 0.0 0.0 0.0 0.0 0.0 2.5 0.0 0.0 0.0
    OTU_40 Xylariaceae sp. Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 2.5 0.0 0.0
    OTU_41 Xylaria sp. Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 2.5 0.0 0.0
    OTU_42 Xylaria cubensis Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 2.5 0.0 0.0
    OTU_43 Nemania diffusa Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 2.5 0.0 0.0
    OTU_01 Annulohypoxylon sp. Hypoxylaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.0
    OTU_02 Xylaria carpophila Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 5.6 0.0
    OTU_03 Nemania diffusa Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 12.2 4.3
    OTU_04 Hypoxylon cf. rubiginosum Hypoxylaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 1.4
    OTU_05 Whalleya microplaca Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 1.4
    OTU_06 Nemania sp. Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 3.3 1.4
    OTU_07 Hypoxylon perforatum Hypoxylaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 3.3 1.4
    OTU_08 Hypoxylon cercidicola Hypoxylaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.0
    OTU_09 Hypoxylon ferrugineum Hypoxylaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.0
    OTU_10 Nemania sp. Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.0
    OTU_11 Xylaria cubensis Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.0
    OTU_12 Nemania diffusa Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.0
    OTU_13 Hypoxylon sp. Hypoxylaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.0
    OTU_14 Biscogniauxia maritima Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 5.7
    OTU_15 Daldinia childiae Hypoxylaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.4
    OTU_16 Nemania sp. Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.4
    OTU_17 Nemania serpens Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.4
    OTU_18 Rosellinia aquila Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.4
    OTU_19 Biscogniauxia maritima Xylariaceae 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 1.4

     | Show Table
    DownLoad: CSV
    Figure 1.  Rarefaction curve depicting the effect of the number of leaves examined on the number of fungal OTUs. Solid line, subtropical tree species; dotted line, cool temperate tree species. (A) Data for nine tree species. Abbreviated codes of tree species are as in Table 1. Standard deviations are not shown for the sake of visibility. (B) Combined data for all subtropical species and combined data for all cool temperate tree species are shown. Shaded areas indicate standard deviations of the means.
    Figure 2.  Multivariate ordination of fungal OTU composition in leaf litter of subtropical (A) and cool temperate tree species (B), using nonmetric multidimensional scaling (NMDS, stress value = 0.016 in subtropical dataset and 0.000 in cool temperate dataset). Abbreviated codes of tree species are as in Table 1. Bars indicate standard errors.

    The present study estimated the alpha diversity (i.e., OTU richness) and beta diversity (OTU composition) of ligninolytic fungi from Xylariaceae and Hypoxylaceae associated with bleached leaf litter from subtropical and temperate forest soils. The eight fungal genera found (Xylaria, Nemania, Hypoxylon, Biscogniauxia, Annulohypoxylon, Daldinia, Nodulisporium, and Rosellinia) have been isolated previously from bleached leaf litter in both subtropical and temperate forests [9],[10]. Xylariaceae and Hypoxylaceae are closely related taxa of the Xylariales and are well-known for their ability to decompose lignin in plant residues [16][18]. Wendt et al. [19] recently re-established Hypoxylaceae (formerly classified as subfamily Hypoxyloideae in Xylariaceae) based on morphology, phylogeny, and secondary metabolite analyses. According to the survey carried out by the authors in main databases such as PubMed, Scopus, and Web of Science, this is the first report of Whalleya microplaca OTU_05 as ligninolytic fungi isolated from cool temperate leaves (Table 2). This species was previously known as wood-inhabiting fungi fruiting on dead wood [20] and as endophytes of live leaves [21].

    The rarefaction curves (Figure 2) did not reach asymptotes due to the relatively high number of singleton OTUs but suggested a lower alpha diversity of ligninolytic ascomycete fungi in the subtropical than in the cool temperate region. However, caution must be taken to ecologically interpret this climatic difference in fungal diversity because the numbers of sites and tree species examined were low, especially in the cool temperate region. Few comparative data have been available regarding climatic patterns of ligninolytic ascomycete fungi in leaf litter, but a similar study was conducted to compare the diversity of endophytic fungi in Xylariaceae and Hypoxylaceae (as Xylarioideae and Hypoxyloideae of Xylariaceae) in live leaves [22]. Interestingly, Ikeda et al. [22] found an opposite pattern to that found in the present study; namely, they found that the rarefaction curve of endophytic fungi was steeper in the subtropical than in the cool temperate forest, i.e., there was greater diversity of endophytic fungi in the subtropical forest. This discrepancy may be attributable to the difference in substrata (dead vs. live leaves), but more investigations are needed to further consider the climatic pattern of diversity of Xylariaceae and Hypoxylaceae fungi.

    Segregation of the OTU composition among tree species was not obvious for either subtropical or cool temperate tree leaves (Figure 2). This is primarily attributable to the dominance of particular fungal OTUs on leaf litter across different tree species, i.e., X. cubensis OTU_20 in subtropical trees and N. diffusa OTU_03 in cool temperate trees, leading to relatively similar OTU compositions among tree species examined. This result in the present study is consistent with the previous finding [9] that the isolates of Xylariaceae obtained from leaf litter had low host recurrence. Zhou and Hyde [23] defined host recurrence of fungi as the frequent or predominant occurrence of a fungus on a particular host or range of hosts, but the fungus can also occur infrequently on other host plants in the same habitat. Indeed, fungi in Xylariaceae and Hypoxylaceae are generally considered to have a wide host range [24][26]. In contrast, we found no overlap of fungal OTUs between subtropical and cool temperate tree species (Table 2). Such low similarity in the OTU composition of Xylarioideae and Hypoxyloideae between these climatic regions was previously reported for endophytic fungi [22] and suggests geographic and climatic structures of fungal distribution, at least in Japan. It should be noted, however, that some OTUs from different climatic regions were assigned to the same species, namely X. cubensis and N. diffusa (Table 2). Such results imply high degrees of intraspecific variability (i.e., more than 3% dissimilarity) in their ITS sequences and/or insufficient taxonomic information in the database record that the bioinformatic tool referred to. In fact, by quantifying the intraspecific ITS variability in all fungi for which sequence data were available through the International Nucleotide Sequence Database (INSD), the intraspecific sequence variability of X. hypoxylon was found to reach 24.2% [27].

    The present study demonstrated the patterns of alpha and beta diversity of Xylariaceae and Hypoxylaceae fungi associated with lignin decomposition of leaf litter from subtropical and temperate trees. These fungi are well-known for their ability to metabolize not only lignin but also other diverse compounds [28],[29] and are diverse phylogenetically as well as taxonomically [19],[20]. Future study directions include the evaluation of functional and phylogenetic diversity of Xylariaceae and Hypoxylaceae fungi, in addition to their taxonomic diversity and the climatic patterns of these diversity measures to get further insights into climatic effects on the roles of fungal diversity in forests.

    The supporting information can be downloaded at the website.

    The authors declare they have not used Artificial Intelligence (AI) tools in the creation of this article.

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