Invertebrate Assemblages on Biscogniauxia Sporocarps on Oak Dead Wood: An Observation Aided by Squirrels
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Article Invertebrate Assemblages on Biscogniauxia Sporocarps on Oak Dead Wood: An Observation Aided by Squirrels Yu Fukasawa Graduate School of Agricultural Science, Tohoku University, 232-3 Yomogida, Naruko, Osaki, Miyagi 989-6711, Japan; fukasawayuu@gmail.com; Tel.: +81-229-847-397; Fax: +81-229-846-490 Abstract: Dead wood is an important habitat for both fungi and insects, two enormously diverse groups that contribute to forest biodiversity. Unlike the myriad of studies on fungus–insect rela- tionships, insect communities on ascomycete sporocarps are less explored, particularly for those in hidden habitats such as underneath bark. Here, I present my observations of insect community dynamics on Biscogniauxia spp. on oak dead wood from the early anamorphic stage to matured teleomorph stage, aided by the debarking behaviour of squirrels probably targeting on these fungi. In total, 38 insect taxa were observed on Biscogniauxia spp. from March to November. The com- munity composition was significantly correlated with the presence/absence of Biscogniauxia spp. Additionally, Librodor (Glischrochilus) ipsoides, Laemophloeus submonilis, and Neuroctenus castaneus were frequently recorded and closely associated with Biscogniauxia spp. along its change from anamorph to teleomorph. L. submonilis was positively associated with both the anamorph and teleomorph stages. L. ipsoides and N. castaneus were positively associated with only the teleomorph but not with the anamorph stage. N. castaneus reproduced and was found on Biscogniauxia spp. from June to November. These results suggest that sporocarps of Biscogniauxia spp. are important to these insect taxa, depending on their developmental stage. Citation: Fukasawa, Y. Invertebrate Keywords: fungivory; insect–fungus association; Sciurus lis; Quercus serrata; xylariaceous ascomycetes Assemblages on Biscogniauxia Sporocarps on Oak Dead Wood: An Observation Aided by Squirrels. Forests 2021, 12, 1124. https:// doi.org/10.3390/f12081124 1. Introduction Dead wood is an essential component of biodiversity in forest ecosystems [1,2]. Fungi, Academic Editor: Simon Curling in particular, is a major group of saproxylic communities; they have a large impact on saproxylic communities due to their unique wood decay abilities [3], and their fruit bodies Received: 24 July 2021 and spores are important to the diet of a variety of organisms, including protozoa [4], Accepted: 20 August 2021 invertebrates [5], and vertebrates [6,7]. A better understanding of the relationships between Published: 22 August 2021 fungi and saproxylic communities is critical to clarifying the mechanisms that maintain biodiversity in forest ecosystems. Publisher’s Note: MDPI stays neutral In terms of their diversity and function, insects are another major group present within with regard to jurisdictional claims in saproxylic communities [1]. Insects have intimate relationships with fungi as fungivores, published maps and institutional affil- vectors of fungal propagules, and foragers of wood decomposed by fungi [8]. Numer- iations. ous studies have investigated the insect communities present on fungal fruit bodies, the majority of which are basidiomycetes [5,9,10]. Host specificity [11–14], the evolution of host use [15], and spore dispersal [16–20] have been intensively studied for a variety of fungus–insect relationships. Furthermore, topics in general ecology (e.g., coexisting pat- Copyright: © 2021 by the author. terns on patchy resources [21,22]) and applied ecology (e.g., effects of forest management Licensee MDPI, Basel, Switzerland. on ecological communities [23,24]) have also been investigated using the insect–basidiocarp This article is an open access article system. However, studies on the relationships between insect communities on ascomycete distributed under the terms and fruit bodies, a sister taxon of basidiomycetes which also produces macroscopic fruit bodies, conditions of the Creative Commons are quite limited, with examples of symbiotic associations in ambrosia beetles [25], wood- Attribution (CC BY) license (https:// wasps [26], and fungus-growing termites [27] and insect pathogens, such as in the genera creativecommons.org/licenses/by/ Beauveria [28], Metarhizium [29], and Ophiocordyceps [30]. 4.0/). Forests 2021, 12, 1124. https://doi.org/10.3390/f12081124 https://www.mdpi.com/journal/forests
Forests 2021, 12, 1124 2 of 10 Quercus serrata is a deciduous oak that dominates low-elevation rural forests through- out Japan. In recent decades, a serious dieback of Q. serrata (oak wilt disease) resulted in huge amount of dead wood [31,32]. Therefore, evaluations of the biotic communities associated with Q. serrata dead wood is necessary to understand and predict biodiversity in areas affected by oak wilt disease. The symbiotic association between a pathogenic fungus, Raffaerea quercivora, and ambrosia beetles, Platypus querucivorus, which carry the propagules of the fungus in their mycangia, is well studied [33,34]. In addition, since Q. serrata logs are traditionally used for cultivating shiitake mushrooms (Lentinula edodes), several ascomycete species that negatively affect the yield of shiitake mushrooms are known to occur on Q. serrata bed-logs [35]. The most famous ascomycete species is in the genus Trichoderma (including species formerly denoted as Hypocrea), which is an antago- nistic and/or mycoparasitic taxon and causes serious damage to shiitake cultivation [36]. Trichoderma spp. has an intimate relationship with gall midge belonging to the genus Camptomyia on shiitake bed-logs [37]. Despite recent advances in the studies of microscopic and pathogenic ascomycetes associated with insects, relationships between insects and other taxa in macroscopic ascomycetes in genera such as Biscogniauxia, Daldinia, Diatrype, Graphostroma, and Hypoxylon, which fruit on Q. serrata dead wood, are largely unknown. To investigate successive changes of fungal and insect communities and their inter- actions during decomposition of Q. serrata dead wood, I started a multi-year survey of 32 experimentally cut logs of Q. serrata in August 2015. In March 2016, I observed that a squirrel or squirrels frequently visited and intensively debarked the logs, where colonies of anamorphic ascomycetes were found to appear on the sapwood. Subsequently, a variety of insects were found on the ascomycetes throughout their changes from the anamorph to the teleomorph stage. In the present study, I describe the insect assemblages that were observed on the Q. serrata logs and their relationships with the different sexual stages of ascomycetes during a growing season. 2. Materials and Methods 2.1. Experimental Setup The present study was conducted in a secondary forest dominated by Q. serrata and Pinus densiflora in Kami town, Miyagi, Japan (38◦ 37.2 N, 140◦ 48.6 E). In 2016, the mean an- nual temperature at the nearest meteorological station at Kawatabi (38◦ 44.60 N, 140◦ 45.6 E) was 11.6 ◦ C (3.2 ◦ C in February to 28.7 ◦ C in August), and the annual precipitation was 1537.5 mm. Snow covers the ground from November to March (Japan Meteorological Agency, available online: https://www.jma.go.jp/jma/indexe.html (accessed on 21 Au- gust 2021)). In August 2015, two Q. serrata trees were felled and cut into 32 logs with a length of 1 m each (diameter 3.4–24.5 cm). The logs were laid on the ground approximately 1 m from each other. I began observations of the logs’ surfaces (top and bottom) in March 2016, when the ground was still covered with snow, but the tops of the logs were visible. On 10 March 2016, at 6:30 a.m., I observed that a squirrel (Sciurus lis) approached the logs and tore off the bark using its teeth. I found Geniculosporium type anamorph of ascomycete on the sapwood surface where the bark had been removed by the squirrel (Figure 1a). The surface of the anamorph was scratched overall (Figure 1a,b). I found 76 portions of debarking by the squirrel on 15 out of the 32 logs (in 1–10 portions per log). The frequency of the presence of anamorphs on the debarked portion was 100%. The observations continued once per week until the end of November 2016, except for April and May. The frequency of squirrel debarking increased to over 50% (19/32 logs) in July 2016. From March to July, the anamorph layers gradually peeled off and teleomorphs appeared (Figure 1c,d), which were identified as Biscogniauxia maritima and Biscogniauxia plana by Dr. Shuhei Takemoto from the University of Tokyo.
Forests Forests2021, 2021,12, 12,x1124 FOR PEER REVIEW 3 3ofof10 10 Figure 1. (a) Surface of a Quercus serrata log recently debarked by a squirrel. Powdery ascomycete Figure 1. (a) Surface of a Quercus serrata log recently debarked by a squirrel. Powdery ascomycete anamorphappears anamorph appearsatatthethecentre centre of of thethe debarked debarked portion portion where where numerous numerous scratch scratch scarsscars can becanob- be observed, served, MarchMarch 2016.2016. (b) Zoomed (b) Zoomed in picture in picture of the scratched of the scratched anamorph anamorph surface, surface, March March 2016. 2016. (c) Grad- (c) peeling ual Gradualofpeeling of the anamorph the anamorph surfaceportion) surface (brown (brown portion) and appearance and appearance of the teleomorph of the teleomorph surface (grey portion), surface June 2016. (grey portion), (d)2016. June Zoomed in picture (d) Zoomed inof teleomorph, picture which was of teleomorph, identified which as Biscog- was identified as niauxia maritima Biscogniauxia and Biscogniauxia maritima plana by and Biscogniauxia Dr. by plana Shuhei Takemoto Dr. Shuhei from the Takemoto University from of Tokyo, the University July of Tokyo, 2016. Scale Scale July 2016. bars: 5bars: mm.5 mm. 2.2.Data 2.2. DataCollection Collection Debarked,anamorph, Debarked, anamorph,and andteleomorph teleomorphareas areaswere weremeasured measuredevery everymonth month(except (exceptfor for Apriland April andMay) May)by byplacing placing11cmcmgrid gridsquares squareson onthethelog logsurface surfaceandandcounting countingthethenumber number ofgrid of gridsquares squaresthat thathad haddebarkation, debarkation,anamorphs, anamorphs,and andteleomorphs. teleomorphs. Insects that were observed on the log surface Insects that were observed on the log surface were recordedwere recordedevery everyweek week(except (exceptfor for April and May) as binary data (presence/absence on each log). Insects April and May) as binary data (presence/absence on each log). Insects were identified with were identified with reference reference to thetokeys the keys and and nomenclature nomenclature of Kurosawa of Kurosawa et al. et al. [38], [38], Uenoetetal.al.[39], Ueno [39],and and Hayashi et al. [40] for Coleoptera; Ishikawa et al. [41] for Hemiptera; and Terayama et[42] Hayashi et al. [40] for Coleoptera; Ishikawa et al. [41] for Hemiptera; and Terayama et al. al. for Hymenoptera (ants). Identification to the species level was difficult, so [42] for Hymenoptera (ants). Identification to the species level was difficult, so several several species were identified species at genus, were identified family,family, at genus, and orderand level. order Taxa level.that Taxaoccurred on ≥20 that occurred onlogs≥20 were logs recorded as dominant taxa. were recorded as dominant taxa. 2.3. Data Analysis 2.3. Data Analysis All statistical analyses were conducted using R ver. 4.0.5 [43]. A generalised linear All statistical analyses were conducted using R ver. 4.0.5 [43]. A generalised linear model (GLM) was applied to explain the species richness of invertebrates. The diameter of model (GLM) was applied to explain the species richness of invertebrates. The diameter of the logs, position (top/bottom) on the logs, and anamorph and teleomorph areas on the the logs, position (top/bottom) on the logs, and anamorph and teleomorph areas on the log log surface were set as explanatory variables. A binomial distribution error was assumed, surface werelink and a logit set function as explanatory variables. was used. A binomial distribution The log-transformed error surface area ofwas assumed, the logs was setandas aan logit link function offset term. was used. The log-transformed surface area of the logs was set as an offset The term.relationship between invertebrate community composition and environmental The factors wasrelationship visualisedbetween invertebrate using non-metric community composition multi-dimensional scaling (NMDS)and environmental with the vegan factors package was visualised [44]. using Similarities non-metric of the multi-dimensional invertebrate scaling communities across the(NMDS) logs werewith the ve- calculated gan package [44]. Similarities of the invertebrate communities across the using the Raup–Crick similarity index (vegdist command), and this matrix was used logs were calcu- to lated using the Raup–Crick similarity index (vegdist command), and this matrix develop the NMDS ordination plot (metaMDS command). The significance of the difference was used to indevelop community the NMDS ordination composition plotthe between (metaMDS top and command). The significance bottom positions of the logs ofwasthedeter- dif- ference in community composition between the top and bottom positions of mined using permutation multivariate analysis of variance [45] with 10,000 permutations the logs was determined using permutation (adonis command). In addition,multivariate communityanalysis varianceofbetween variancesamples [45] with 10,000 permu- (calculated using tations (adonis command) the betadisper command). wasIn addition, compared community between thevariance between top and bottomsamples positions(calculated using an
were set as environmental variables. A set of GLMs were applied to explain the occurrence o brate species. The environmental variables that were detect Forests 2021, 12, 1124 vfit (diameter, anamorph percentage, and teleomorph percen 4 of 10 variables. Binomial distribution errors were assumed. Logit analysis of variance (anova command). Finally, the significance of the effects of the en- vironmental variables on the invertebrate communities was determined using the envfit 3. Results command; sampling month, diameter, anamorph percentage, and teleomorph percentage were set as environmental variables. The mean percentage of debarked area per log was 10% A set of GLMs were applied to explain the occurrence of the three dominant inverte- brate species. The environmental variables that were detected to be significant using envfit from June to July, and remained constant thereafter (Figure (diameter, anamorph percentage, and teleomorph percentage) were set as explanatory variables. Binomial distribution errors were assumed. Logit link functions were used. debarked more than bottoms of the logs. The anamorph are the3. debarked Results area in March but decreased to zero by the en The mean percentage of debarked area per log was 10% in March, increased slightly trast, from the June toteleomorph area was July, and remained constant seldom thereafter (Figure 2a).observed until The tops of the logs were June debarked more than bottoms of the logs. The anamorph area occupied almost all parts and occupied of the debarked area almost alldecreased in March but parts of theby debarked to zero area 2b). the end of July (Figure until In Nov contrast, the teleomorph area was seldom observed until June but greatly increased in July and occupied almost all parts of the debarked area until November (Figure 2c). Figure 2. Percentage area of debarked (a), anamorph (b), and teleomorph (c) of Bisogniauxia spp. on Figure 2. Percentage area of debarked (a), anamorph (b), and teleom Quercus serrata logs. Grey and white bars show the top and bottom sides of the logs, respectively. Quercus serrata In total, 38 taxalogs. Grey of insects were and white recorded bars (Table S1). show was Coleoptera thethetop and largest bottom group and consisted of 28 taxa, followed by 4 taxa of Hemiptera and 3 taxa of Lepidoptera. Archaeognatha, Hymenoptera, and Psocodea included one taxon each. The GLM indicated In total, 38 taxa of insects were recorded (Table S1). Cole and consisted of 28 taxa, followed by 4 taxa of Hemiptera a chaeognatha, Hymenoptera, and Psocodea included one tax
Forests 2021, 12, 1124 5 of 10 that insect diversity was negatively correlated with log diameter and positively correlated with teleomorph area (Table 1). The bottom sides of the logs had lower insect richness than Forests 2021, 12, x FOR PEER REVIEWthe top sides. 5 of 10 The observed insect communities were significantly correlated with sampling month, log diameter, and anamorph area (Figure 3); however, the position on the logs (top/bottom) was not correlated with the insect communities. Among the recorded insect taxa, Librodor (Glischrochilus) ipsoides, Anamorph Laemophloeus submonilis, and Neuroctenus castaneus– were observed d.f. (null) 444 on ≥20 logs and were thus assigned as dominant taxa; these species were not recorded Null deviance in March but were frequently 814.12 recorded in June and July, particularly on the top sides of the logs (Figure 4). d.f. (residual) Although 441 by August and L. submonilis and L. ipsoides disappeared September, respectively, N. deviance Residual castaneus remained until November. Additionally, 770.35 N. castaneus reproduced on the surfaceAIC of Biscogniauxia teleomorphs (Figure 4c). The GLM based on the 1517.1 data from July suggested that the occurrence of L. submonilis was positively associated with *the p
Forests 2021, 12, x FOR PEER REVIEW 6 of 10 Forests 2021, 12, 1124 6 of 10 Figure 4. Frequencies of Laemophloeus submonilis (a), Librodor ipsoides (b), and Neuroctenus castaneus (c) Figure 4. Frequencies of Laemophloeus submonilis (a), Librodor ipsoides (b), and Neuroctenus castaneus on Quercus serrata logs. Grey and white bars show the top and bottom sides of the logs, respectively. (c) on Quercus serrata logs. Grey and white bars show the top and bottom sides of the logs, respec- tively. Table 2. GLM results showing estimated coefficients between occurrences of the three dominant insect 2. Table species GLM and log showing results variables.estimated coefficients between occurrences of the three dominant insect species and log variables. Variable Laemophloeus Librodor Neuroctenus Variable Diameter Laemophloeus 0.18 Librodor 0.32 * Neuroctenus 0.20 ** Anamorph Diameter area 0.97 0.18* 0.321.17* 0.20–** Teleomorph Anamorph area area 0.08 0.97** 1.17 * 0.24 0.51 – ** d.f. (null) 63 63 63 Teleomorph Null deviance area 0.08 51.98* 0.24 71.98* 0.51 ** 86.46 d.f. (null) d.f. (residual) 63 60 6360 6361 Residual deviance Null deviance 24.47 51.98 22.51 71.98 41.33 86.46 AIC d.f. (residual) 32.47 60 30.51 60 47.33 61 * p < 0.05; ** p < 0.01. Residual deviance 24.47 22.51 41.33 AIC 32.47 30.51 47.33 4. Discussion * p < 0.05; ** p < 0.01. In the present study, the debarking behaviour of squirrels improved the visibility of in- 4.sect communities on Biscogniauxia sporocarps, as their initial anamorphic stages are usually Discussion hidden under the bark. Fungivorous saproxylic insects with flat morphology often inhabit In the present study, the debarking behaviour of squirrels improved the visibility of invisible microhabitats, such as the space between bark and wood, which reduces their insect communities on Biscogniauxia sporocarps, as their initial anamorphic stages are usu- visibility considerably [1,46]. Debarking by squirrels targeting Biscogniauxia sporocarps ally hidden under the bark. Fungivorous saproxylic insects with flat morphology often enabled the author to observe the sporocarps starting from the very early stages of their inhabit invisible microhabitats, such as the space between bark and wood, which reduces development. Squirrels very accurately found Biscogniauxia sporocarps hidden under the their visibility considerably [1,46]. Debarking by squirrels targeting Biscogniauxia sporo- bark. It is well-known that squirrels can detect hypogeous sporocarps by smell [47,48]. Xy- carps enabled the author to observe the sporocarps starting from the very early stages of lariaceous ascomycetes effuse a variety of volatiles, depending on the developmental stage their development. of their sporocarps Squirrels very [49], which may accurately found be detected Biscogniauxia by squirrels. sporocarps McKeever hidden [47] also un- reported der the bark. It is well-known that squirrels can detect hypogeous sporocarps that fungi constitute the largest portion of squirrel diets, particularly in the summer and by smell [47,48]. Xylariaceous early autumn, ascomycetes and represent effuse alargest the second varietyportion of volatiles, depending of their on the diets in the develop- early spring; mental however, the majority of the fungi eaten by squirrels may be basidiomycetes [48]. I [47] stage of their sporocarps [49], which may be detected by squirrels. McKeever also also reported observed that fungi a squirrel constitute eating the largest old (fruiting portion from the of squirrel previous diets, particularly year) Sarcomyxa in the serotina (basid-
Forests 2021, 12, 1124 7 of 10 iomycetes) sporocarps on 18 April 2021 in Japan (the personal observation of Yu Fukasawa). Although it is unclear whether squirrel fungivore of xylariaceous ascomycetes is common, I found the same type of debarking on freshly felled oak logs approximately 8 km away from the study site in 2018 and again at the study site in February 2021 (Figure S1, the personal observation of Yu Fukasawa). Currah et al. [6] investigated the stomach contents of squirrels and flying squirrels in North America and found fragments of Xylariaceae and Diatripaceae ascocarps. However, again, basidiomycetes sporcarps constituted the majority of their gut contents. Xylariaceous ascomycetes may constitute a supplemental diet during the early spring when other fresh food sources are unavailable. Fungal spores contain a high percentage of nitrogen, but their digestibility is very low in squirrels [50]. Among the recorded insect taxa, almost all taxa except for Niponius osorioceps and Pheidole fervida belonged to families that include species reported to be fungivores [1,51,52]. More specifically, species belonging to Aradidae, Cucujidae, Nitidulidae, Anthribidae, Monotomidae, Silvanidae, Corylophidae, and Biphyllidae are known as ascomycete eaters [51,53]. I even observed Lepidopteran larvae of unknown identity grazing the surface of Biscogniauxia stromata. Tineoidea moths are known to have fungivorous habits, although they feed on basidiomycotan wood decay fungi [22,54]. Powell [55] reported that Lepidopteran species belonging to Pyralidae feed on the stromata of Hypoxylon occidentale (Xylariaceae, Ascomycota). As shown through NMDS (Figure 3), the presence of Biscogni- auxia spp. may strongly attract fungivorous insects and affect their community structure. Lee et al. [56] reported that stem canker caused by Annulohypoxylon truncatum (Xylariaceae) on oak stem significantly increases invertebrate diversity in Korea, irrespective of the presence or absence of sap flow. In the present study, I identified three dominant insect species: Librodor ipsoides (Ni- tidulidae, Coleoptera); L. submonilis (Cucujidae, Coleoptera); and N. castaneus (Aradidae, Hemiptera)—they each had significant relationships with the occurrence of Bisocogni- auxia spp. (Table 2). Although the gut contents of these species were not surveyed in the present study, it is highly likely that these three species were all fungivores and had intimate associations with Biscogniauxia spp. during their life cycle. Nitidulidae is a well- known fungivorous Coleoptera occurring in not only fungal fruit bodies but also in the sap flows of damaged trees, fermenting fruits, and pathological plant tissues—-such species probably have yeasts or pathogenic fungi as a normal and essential part of their diet [51]. Specifically, species in the genus Librodor are known as ‘sap beetles’ that forage and breed in fermented sap flow [57](referred as a genus Glischrochilus). L. ipsoides has also been found in the sap on Quercus acutissima trees in Japan, although its abundance is quite low compared with that of other sap beetles [58]. On the other hand, L. ipsoides has been found in the fruit bodies of a basidiomycete Cryptoporus volvatus on Pinus densiflora in Korea [59], but it was not found in C. volvatus in Japan [22]. In the present study, I newly found L. ipsoides on Biscogniauxia spp. fruit bodies at a relatively high frequency (>30%; Figure 4), indicating that the stromata and/or conidia of Biscogniauxia spp. are an important habitat of this species. Lawrence [60] reported observations of Prometopia sexmaculata (Nitidulidae) breeding in the stromata of Hypoxylon (Xylariaceae) on oak. Cucujidae are also known as Coleopteran ascomycete eaters. Species in the genus Laemophloeus have been frequently reported in association with ascomata, such as Daldinia, Tubercularia, Hypoxylon, and Biscog- niauxia (=Nummularia) [51]. Therefore, it is not surprising that I found L. submonilis on Biscogniauxia spp. (B. maritima and B. plana) in the present study, even though it is a newly found association in Japanese species. In Aradidae (Hemiptera), most species are fungivores [53,61] that feed on fungal hyphae, using their piercing-sucking mouthparts to suck the cell contents, and have adapted gut systems [62], but little is known about the fungal host association of most species, particularly for ascomycetes [53]. Most of the Aradidae species occur preferentially on dead wood during the early stages of decay, probably due to the presence of their dietary fungal species [53]. As such, outbreaks of some Aradidae species are closely associated with large dieback events, such as forest fires and pests. Aradus lugubris can appear immediately
Forests 2021, 12, 1124 8 of 10 after forest fires, when they feed on Daldinia loculata (Lév.) Sacc. (Xylariaceae), a known fire-related ascomycete in boreal forests [63]. Similarly, large-scale wind throws and bark beetle outbreaks in a Norway spruce forest in the Bavarian Forest in Germany, where dead spruce snags were intensively colonised by a basidiomycete Fomitopsis pinicola [64], provided a suitable habitat for Aradus obtectus [53]. In Japan, Q. serrata trees have recently suffered from oak wilt disease [65]. However, relationships between oak wilt disease and the occurrence of Biscogniauxia spp. are unclear. Fukasawa et al. [66] compared latent fungal communities within Q. serrata trunks in stands with or without the prevalence of oak wilt disease and did not detect Biscogniauxia spp. Parental care has been observed in Aradidae, during which the male safeguards the egg mass for several weeks, and parental care may be extended to the nymphal stage [53]. In the present study, I also observed that adults appeared to guard the mass of nymphs (Figure 4). In addition, I observed many nymphs spraying (probably some chemicals) simultaneously from their tail when they were shaded by my hands. To summarise, I observed the insect communities on saproxylic Biscogniauxia spp. on oak dead wood during the transition from the anamorphic to teleomorphic stages; this was aided by debarking by squirrels. The presence of Biscogniauxia spp. significantly affected the insect communities. More specifically, the population dynamics of two Coleoptera and one Hemiptera dominant species revealed that Biscogniauxia spp. represents an important habitat in their life cycles. Supplementary Materials: The following are available online at https://www.mdpi.com/article/ 10.3390/f12081124/s1. Figure S1: Another evidence of debarking of Quercus serrata log by squirrel targeting on ascomycete anamorph, Table S1: Insect taxa recorded in the present study. Funding: This research received no external funding. Acknowledgments: The author is grateful to Shuhei Takemoto for identification of Biscogniauxia spp. I also thank Chisato Kobayashi for letting me use our garden for my experiment. Conflicts of Interest: The author declares that they have no conflict of interest. References 1. Stokland, J.N.; Siitonen, J.; Jonsson, B.G. Biodiversity in Dead Wood; Cambridge University Press: Cambridge, UK, 2012. 2. Seibold, S.; Bässler, C.; Brandl, R.; Gossner, M.M.; Thorn, S.; Ulyshen, M.D.; Müller, J. Experimental studies of dead-wood biodiversity—A review identifying global gaps in knowledge. Biol. Conserv. 2015, 191, 139–149. [CrossRef] 3. Rayner, A.D.M.; Boddy, L. Fungal Decomposition of Wood: Its Biology and Ecology; John Wiley & Sons: Chichester, UK, 1988. 4. Fukasawa, Y.; Hyodo, F.; Kawakami, S. Foraging association between myxomycetes and fungal communities on coarse woody debris. Soil Biol. Biochem. 2018, 121, 95–102. [CrossRef] 5. Hanski, I. Fungivory: Fungi, insects and Ecology. In Insect–Fungus Interactions; Wilding, N., Collins, N.M., Hammond, P.M., Webber, J.F., Eds.; Academic Press: London, UK, 1989. 6. Currah, R.S.; Smreciu, E.A.; Lehesvirta, T.; Niemi, M.; Larsen, K.W. Fungi in the winter diets of northern flying squirrels and red squirrels in the boreal mixedwood forest of northern Alberta. Can. J. Bot. 2000, 78, 1514–1520. 7. Elliott, T.F.; Elliott, K. Vertebrate consumption and dispersal of the Nothofagaceae associated ascomycete Cyttaria. Austral. Ecol. 2019, 44, 747–751. [CrossRef] 8. Schigel, D.S. Fungivory and host associations of Coleoptera: A bibliography and review of research approaches. Mycology 2012, 3, 258–272. [CrossRef] 9. Buxton, C.M.G. British Diptera associated with fungi. III. Flies of all families reared from about 150 species of fungi. Entomol. Mon. Mag. 1960, 96, 61–94. 10. Elton, C.S. The Pattern of Animal Communities; Methuen and Co.: Slingsby, UK, 1966. 11. Jonsell, M.; Nordlander, G. Host selection patterns in insects breeding in bracket fungi. Ecol. Entomol. 2004, 29, 697–705. [CrossRef] 12. Yamashita, S.; Hijii, N. The role of fungal taxa and developmental stage of mushrooms in determining the composition of the mycophagous insect community in a Japanese forest. Eur. J. Entomol. 2007, 104, 225–233. [CrossRef] 13. Nakamori, T.; Suzuki, A. Surface properties of the mushroom Strobilurus ohshimae result in food differentiation by collembolan species. Eur. J. Soil Biol 2008, 44, 478–482. [CrossRef] 14. Yamashita, S.; Ando, K.; Hoshina, H.; Ito, N.; Katayama, Y.; Kawanabe, M.; Maruyama, M.; Itioka, T. Food web structure of the fungivorous insect community on bracket fungi in a Bornean tropical rain forest. Ecol. Entomol. 2015, 40, 390–400. [CrossRef] 15. Kobayashi, T.; Sota, T. Evolution of host use in fungivorous ciid beetles (Coleoptera: Ciidae): Molecular phylogeny focusing on Japanese taxa. Mol. Phylogen Evol. 2021, 162, 107197. [CrossRef] [PubMed]
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