Microbes and Environments
Online ISSN : 1347-4405
Print ISSN : 1342-6311
ISSN-L : 1342-6311
Regular Papers
Prevalence and Intra-Family Phylogenetic Divergence of Burkholderiaceae-Related Endobacteria Associated with Species of Mortierella
Yusuke TakashimaKensuke SetoYousuke DegawaYong GuoTomoyasu NishizawaHiroyuki OhtaKazuhiko Narisawa
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2018 年 33 巻 4 号 p. 417-427

詳細
Abstract

Endofungal bacteria are widespread within the phylum Mucoromycota, and these include Burkholderiaceae-related endobacteria (BRE). However, the prevalence of BRE in Mortierellomycotinan fungi and their phylogenetic divergence remain unclear. Therefore, we examined the prevalence of BRE in diverse species of Mortierella. We surveyed 238 isolates of Mortierella spp. mainly obtained in Japan that were phylogenetically classified into 59 species. BRE were found in 53 isolates consisting of 22 species of Mortierella. Among them, 20 species of Mortierella were newly reported as the fungal hosts of BRE. BRE in a Glomeribacter-Mycoavidus clade in the family Burkholderiaceae were separated phylogenetically into three groups. These groups consisted of a group containing Mycoavidus cysteinexigens, which is known to be associated with M. elongata, and two other newly distinguishable groups. Our results demonstrated that BRE were harbored by many species of Mortierella and those that associated with isolates of Mortierella spp. were more phylogenetically divergent than previously reported.

Bacterial endosymbionts are widespread within eukaryotic microorganisms such as algae, protists, and fungi (18, 19, 31, 44). Bacterial endosymbionts in fungi are known as endofungal or endohyphal bacteria, and mostly occur in the phylum Mucoromycota (4, 41). Endofungal bacteria associated with Mucoromycota belonging to the class Betaproteobacteria are currently designated as Burkholderia-related endobacteria (4) or Burkholderiaceae-related endobacteria. For example, Burkholderia rhizoxinica, “Candidatus Glomeribacter gigasporarum”, and Mycoavidus cysteinexigens were found inside the fungal cells of Rhizopus microsporus (Mucorales, Mucoromycotina), Gigasporaceae fungi, such as Gigaspora margarita (Diversisporales, Glomeromycotina), and Mortierella elongata (Mortierellales, Mortierellomycotina), respectively (4). These BRE are completely or partly dependent on host nutrients based on a genome analysis (12, 14, 22, 39, 50) and affect gene expression (23, 36, 50), metabolism (23, 26, 35), oxidative stress responses (36, 51), and chemotaxis in their hosts (27).

Mortierella spp. inhabit diverse ecological niches such as various soil types (53) and specific substrates, including the bodies of arthropods (8, 9, 54) and animal dung (7, 10, 11, 13, 20). The genus Mortierella is one of the largest genera in Mucoromycota and contains nearly 100 described species, which are morphologically classified into nine sections (13) and phylogenetically classified into seven phylogenetic groups (53). Therefore, Mortierella spp. have potential as a suitable research material that offers a wider evolutionary perspective on the relationship between BRE and Mucoromycota. Nevertheless, BRE associated with isolates of Mortierella spp. were only reported from limited species such as M. elongata and M. minutissima obtained from soil in Japan and the United States (32, 37, 50).

The objective of the present study was to assess the prevalence of BRE in diverse species of Mortierella possessing different properties. We herein examined the presence/absence of BRE within 238 isolates of Mortierella spp. mainly obtained in the present study, which were phylogenetically identified as 59 fungal species. We identified many species of Mortierella as new fungal hosts of BRE and demonstrated the phylogenetic divergence of BRE associated with isolates of Mortierella spp. by a phylogenetic analysis of the 16S rRNA gene. The localization of BRE in fungal host cells was confirmed in twelve isolates consisting of eight species of Mortierella by fluorescence and transmission electron microscopic observations.

Materials and Methods

Fungal materials

Between 2011 and 2016, we collected five types of substrates, including the dead bodies and dung of animals, fruiting bodies of fungi, fresh and decayed plant materials, and soil from 62 different locations in Japan (Table S1). Estimated temperature data for each geographic coordinate of the collection site were obtained from the WorldClim version 1.4 at 2.5 min of latitude/longitude degree spatial resolution data (15) and putative climates of each collection site were defined by the latitudes and mean temperatures of the warmest and coldest quarters, including 7, 40, and 15 locations in cool, temperate, and subtropical regions, respectively (Table S1). Mortierella spp. were isolated using a moist chamber method and inoculating intact or surface-washed substrates onto artificial media. The sporangia of Mortierella spp. on substrates or substrate-inoculated media were collected using a frame-sterilized fine needle and inoculated onto fresh LCA media (0.2 g yeast extract [Difco, Sparks, MD, USA], 1.0 g glucose [Wako Pure Chemical Industries, Osaka, Japan], 2.0 g NaNO3 [Wako], 1.0 g KH2PO4 [Wako], 0.2 g KCl [Wako], 0.2 g MgSO4·7H2O [Wako], and 15 g Bacto agar [Difco] in 1.0 L distilled water) (28). In addition, eleven and twelve isolates of Mortierella spp. were obtained from the NITE Biological Resource Center (NBRC) and CBS-KNAW culture collection, respectively (Table S1 and S2).

DNA extraction, PCR, and sequencing of internal transcribed spacer (ITS) regions of Mortierella isolates

The nucleotide sequences of the ITS1-5.8S-ITS2 region of each isolate were determined for molecular identification. Template DNA was extracted from mycelia using PrepmanTM Ultra sample reagent (Applied Biosystems, Foster City, CA, USA) in accordance with Sato et al. (37). Fifty microliters of a PCR mixture containing 1.0 μL of template DNA, 2.5 μL of each forward and reverse fungal universal primer solution (10 pmol μL−1 each), 4.0 μL of the dNTP mixture (2.5 mM each), 0.15 μL of 5 U μL−1 Ex Taq HS polymerase (Takara Bio, Otsu, Japan), 5.0 μL of 20 mM 10×Taq Buffer, and 34.85 μL of sterilized deionized water was prepared. PCR amplification was performed as follows: initially 5 min for 95°C, followed by 30 cycles of 95°C for 30 s, 54°C for 30 s, and 72°C for 1.5 min, and a final extension step at 72°C for 10 min using a thermal cycler. Forward and reverse primer combinations, such as ITS5-ITS4, ITS1F-ITS4, and ITS5-LR5, were used for PCR (Table S3). PCR products were purified using polyethylene glycol and ethanol precipitation, and a cycle sequence reaction was then performed with a BigDye Terminator Cycle Sequencing Ready Reaction Kit (Applied Biosystems) in accordance with the manufacturers’ instructions with the forward primer used for PCR. Additionally, cycle sequence reactions were also conducted using the reverse primer if needed, and ITS3 and LR0R were used as additional sequencing primers for PCR products using ITS5-LR5 primer combinations (Table S3). Cycle sequencing products were purified by ethanol precipitation, and electrophoresis was performed using an Applied Biosystems 3130xl genetic analyzer (Applied Biosystems) to determine nucleotide sequences. The sequences obtained from each primer were assembled to a single sequence using GeneStudio Professional software version 2.2.0.0 (www.genestudio.com).

Trimming of large and small subunit coding regions

The sequences obtained from each isolate varied in length because of the different primer combinations and included unnecessary regions for the blastn search at both ends, namely, the large subunit (LSU) and small subunit (SSU) regions. In order to trim off these regions, the start and end positions of the ITS1-5.8S-ITS2 region were detected using ITSx version: 1.0.11 (3). The LSU and/or SSU regions were trimmed off manually from each sequence if present.

Blastn searches using the ITS1-5.8S-ITS2 region

The genus Mortierella is known as one of the most frequently recovered fungal genera in environmental sequencing studies of soil, and there are a large number of environmental and unidentified ITS1-5.8S-ITS2 sequences deposited in GenBank (30). These “unidentifiable” ITS1-5.8S-ITS2 sequences of Mortierella often complicate the identification of Mortierella spp. using web-based blastn searches. In order to facilitate the identification of the closest species by a blastn search, we constructed a nucleotide sequence database (hereinafter referred to as the custom database) by collecting ITS1-5.8S-ITS2 sequences of Mortierellomycotinan fungi determined using living cultures deposited in culture collections and specimens deposited in herbaria. The custom database consisted of 307 sequences from different phylotypes of 90 Mortierellomycotinan species. Most sequences (299 sequences) were used in a comprehensive phylogenetic analysis of the genus Mortierella by Wagner et al. (53), and the others were one sequence of M. elasson that was obtained from the type strain CBS 220.29, six sequences deposited along with new species descriptions, such as M. calciphila (25), M. fluviae (16), M. signyensis (5), and M. thereuopodae (11), and two sequences obtained from Modicella spp., from a different genus but phylogenetically included within the genus Mortierella (40). The blastn searches with our trimmed ITS1-5.8S-ITS2 sequences using the custom database were conducted to identify the closest species using BLAST+ version 2.5.0 (6). In these blastn searches, the ITS1-5.8S-ITS2 sequences obtained from four BRE-detected isolates of M. elongata (FMR13-2, FMR23-1, FMR23-6, and FMR23-9) described in the previous study were included (37). On the other hand, twelve isolates (CBS 122.71, CBS 130.66, CBS 131.66, CBS 222.35, CBS 277.71, CBS 315.61, CBS 316.61, CBS 443.68, CBS 857.70, CBS 858.70, NBRC 109920, and NBRC 109921) obtained from culture collections were excluded and regarded as having 100% similarity because the ITS1-5.8S-ITS2 sequences of these isolates were contained in the custom database.

Phylogenetic analyses of Mortierella spp

Based on blastn searches, untrimmed ITS sequences were separately clustered in different alignment blocks for each phylogenetic group of Mortierella spp. defined by Wagner et al. (53). The ITS sequences of the custom database were subsequently clustered and combined with the alignment blocks separately. We then conducted phylogenetic analyses using the alignment blocks to clarify the species-level phylogenetic relationship of isolates within each phylogenetic group. Each alignment block was separately aligned, poorly aligned positions were removed, and they were then used for a phylogenetic analysis by the maximum likelihood (ML) method with RA×ML version 8.1.5 software (43) as previously described by Takashima et al. (45).

Diagnostic PCR to detect endofungal bacteria

Diagnostic PCR targeting the bacterial 16S rRNA gene was conducted to detect the presence/absence of endofungal bacteria. Template DNA samples extracted previously for the molecular identification of Mortierella spp. were used. Regarding the PCR amplification of the 16S rRNA gene, 50 μL of a PCR mixture containing 1.0 μL of template DNA, 1.5 μL of each primer solution of the bacterial universal primers 10F and 926R (10 pmol μL−1 each) (Table S3), 10 μL of 2 mM dNTPs, 1.0 μL of 1.0 U μL−1 KOD FX Neo DNA polymerase (Toyobo, Osaka, Japan), 25 μL of 2×PCR Buffer for KOD FX Neo DNA polymerase, and 10 μL of sterilized deionized water was prepared. PCR amplification was performed as follows: initially 2 min for 94°C, followed by 30 cycles of 98°C for 10 s, 58°C for 30 s, and 68°C for 1 min using a thermal cycler, and PCR amplification was checked by agarose gel electrophoresis.

DNA sequencing of the 16S rRNA gene of Burkholderiaceae-related endobacteria

PCR products of the 16S rRNA gene obtained using 10F-926R primers were purified and initially sequenced using the 10F forward primer as a sequencing primer. If the partial sequences obtained with the 10F primer were close to the sequences of known BRE in Mucoromycota using blastn searches in NCBI (https://www.ncbi.nlm.nih.gov/), additional PCR to determine longer sequences suited for the phylogenetic analysis was conducted. The 10F-1541R or 27F-1492R primer combinations were used in additional PCR (Table S3), which was performed using the same conditions as that with the 10F-926R primer set described above. The PCR products of the 16S rRNA sequences of BRE obtained were purified and used for cycle sequencing with the forward and reverse primers used in PCR and additional sequencing primers, such as 786R, 800F, and 926R (Table S3). The sequences obtained from each primer were assembled to a single sequence using GeneStudio Professional software version 2.2.0.0 (www.genestudio.com).

Phylogenetic analysis of Burkholderiaceae-related endobacteria

In the phylogenetic analysis of BRE, the 16S rRNA gene sequences obtained were aligned with the retrieved 16S rRNA gene sequences from GenBank using MAFFT v7.212 (17). The alignment block obtained was viewed using MEGA 6.06 software (46), and poorly aligned positions at both ends were removed manually. Model selection for maximum likelihood phylogeny was performed in MEGA 6.06. The alignment block was used for the phylogenetic analysis with the maximum likelihood (ML) method using RAxML version 8.1.5 software (43) under the GTRGAMMAI model selected by MEGA 6.06 and bootstrapping (1,000 replicates) with the rapid bootstrap analysis option. The alignment block was also used to cluster 16S rRNA gene sequences into operational taxonomic units (OTUs) using mothur v.1.36.1 (method=average) (38). The threshold was set as 97%, which is a common threshold for 16S rRNA gene sequence similarity and has been widely used for the delineation of species in bacterial classification (42).

Fluorescence microscopy

In order to observe endofungal bacteria inside fungal cells, fluorescence microscopic observations by nucleic staining using a LIVE/DEAD® BacLightTM Bacterial Viability Kit (Molecular Probes, Eugene, OR, USA) and fluorescence in situ hybridization (FISH) were performed. Regarding LIVE/DEAD staining, six BRE-harbored isolates (M. basiparvispora E1425, M. humilis YTM36, and M. verticillata CBS130.66 harbored MorBRE group A; M. alpina YTM25 harbored MorBRE group B; M. elongata FMR13-2 and YTM18 harbored MorBRE group C) and a non-BRE-harbored isolate M. basiparvispora E1439 were used. A staining solution containing 1.5 μL each of SYTO9 and propidium iodide fluorescent nucleic acid stains in 1 mL distilled water was freshly prepared and used for staining by adding approximately 100–200 μL of the staining solution onto fungal mycelia placed on a slide. After waiting a few min for staining, the staining solution was removed using a pipette and mycelia were rinsed with adequate amounts of distilled water. A cover slip was then mounted on stained fungal mycelia and excess water was removed using filter paper. Five BRE-harboring isolates and the non-BRE-harboring isolate M. sugadairana YTM39s9 were used for FISH. The BRE-harboring isolates were as follows: M. elongata FMR23-6 with MorBRE group A; Mortierella sp. “zonata” YTM23 with MorBRE group B; M. parvispora E2010s1, M. sugadairana YTM39, and Mortierella sp. 5 YTM49 with MorBRE group C. Fungal mycelia or germinated sporangiospores were fixed in 400 μL of a 3:1 (v/v) mixture of 10% formalin and phosphate-buffered saline (PBS) at 4°C for 6 h in a 1.5-mL tube following two washing steps with 500 μL of PBS and used for hybridization steps. In each case, after removing PBS, the fixed samples were treated using the following steps if needed. Dehydration was performed by adding 200 μL of 50, 75, and 100% ethanol in this order. After ethanol had evaporated, a proteinase K treatment step was performed by adding 200 μL of 10 μg mL−1 proteinase K solution at room temperature (RT) for 10 min. After discarding the solution, the following washing steps were performed by adding 200 μL of PBS for 5 min, 200 μL of 1% Tween20 in PBS for 5 min, and rinsing twice with 200 μL of PBS for 5 min again. Treated and untreated samples were then subjected to a hybridization step with an oligonucleotide probe solution containing the universal bacterial 16S rRNA gene probe EUB338 (5′-GCTGCCTCCCGTAGGAGT-3′) (2), which was labeled at the 5′-end with Cy3 (red) or fluorescein isothiocyanate (FITC, green). The oligonucleotide probe solution was a 1:49 mixture of 50 ng μL−1 of the oligonucleotide probe and hybridization buffer (34) with a stringency of 35% formamide. In the hybridization step, 100 μL of hybridization solution was added to samples and the probe was hybridized at 46°C for 1.5 h. After hybridization, samples were carefully washed twice with washing buffer (34). After the washing step, samples were placed on a slide and mounted in Slow Fade Diamond Antifade Mountant with DAPI (Molecular Probes). All fluorescence images were obtained using a fluorescence microscope (BX51, Olympus Corp., Tokyo, Japan) equipped with a digital camera DP25 (Olympus Corp.) or EOS kiss X7i (Canon, Tokyo, Japan).

Transmission electron microscopy

Transmission electron microscopy (TEM) was performed to confirm the endohyphal features of newly distinguishable BRE groups, such as MorBRE groups B and C. Four BRE-harboring isolates were used: M. elongata YTM18 and YTM19 with MorBRE group B; Mortierella sp. “zonata” YTM23 and M. alpina YTM25 with MorBRE group C. Seven-day-old mycelia incubated on a sterilized cellophane sheet placed onto 1/2 CMMY media (10 g malt extract [Difco], 1.0 g yeast extract [Difco], 8.5 g corn meal agar [Difco], and 7.5 g Bacto agar [Difco] in 1.0 L distilled water) at RT were obtained and embedded in a drop of water agar. Regarding fixation, the agar piece was placed in a 1.5-mL tube containing 2.5% glutaraldehyde in 0.05 M cacodylate buffer (CB), pH 7.2 at RT for 2 h. The fixed agar piece was washed in ca. 1 mL of 0.05 M CB three times. The fixed agar piece was then postfixed by adding 750 μL of 1% osmium tetroxide in 0.05 M CB at RT in the dark for 2 h. After removing the solution, the fixed agar piece was washed with ca. 1 mL distilled water twice. Following a dehydration step using ca. 1 mL of 30, 50, 70, 90, and 95% ethanol once, and 100% ethanol twice for 15 min per step, the agar piece was immersed twice in ca. 1 mL of a mixed solution of 100% ethanol and acetone (1:1, v/v) twice, and 1 mL of 100% acetone twice for 15 min per step before being infiltrated once in ca. 1 mL of agar low viscosity resin (Agar Scientific, Stansted, Essex, UK) in 100% acetone (1:1, v/v) for 1 h and then infiltrated with ca. 1 mL of pure resin for 4 h (resin was replaced once at 2 h). The agar piece infiltrated in resin was polymerized at 60°C for 18 h. Ultrathin sections were prepared with a Leica EM UC7 Ultramicrotome (Leica Microsystems GmbH, Wetzlar, Germany). Sections were picked up on grids and stained with 10-fold diluted TI-Blue solution (Nisshin EM, Tokyo, Japan) for 20 min and 0.4% lead citrate solution (52) for 7 min following rinsing three times with distilled water for each staining step. Sections were observed with a Hitachi H-7700 transmission electron microscope (Hitachi, Tokyo, Japan) at an acceleration voltage of 80 kV.

Statistical analysis

In order to statistically evaluate whether the properties of isolates of Mortierella spp., such as climatic zones, phylogenetic groups, and substrates, affected the prevalence of BRE, a generalized linear model (GLM) was examined in the presence/absence of BRE as a binary response variable (binomial family, logit link function, n=238). The GLM of the prevalence of BRE incorporated the effects of climatic zones (cool, temperate, subtropical, and unknown), phylogenetic groups (seven groups), and substrates (animal, dung, fungi, plant, soil, and unknown) as categorical explanatory variables, which were the properties of the isolates listed in Table S1, S2, and S4. Using the GLM, odds ratios (OR) with a 95% confidential interval (CI) of the prevalence of BRE in each climatic zone, phylogenetic group, and substrate were calculated by the function “logistic.display()” in the R package “epiDisplay” (https://CRAN.R-project.org/package=epiDisplay) with comparisons to that in the temperate zone, phylogenetic group 7, and soil as reference levels of each explanatory variable, respectively. The combination of properties of reference levels was the most typical in the isolates examined (35 out of 238 isolates). All statistical analyses were performed using R version 3.3.1 (https://www.r-project.org/).

Primer information and sequence data

All the details of primer information used in the present study are listed in Table S3. Sequences containing the ITS1-5.8S-ITS2 region were deposited under accession no. MF403050–MF403052, MF510830, and MH802517–MH802523 for the eleven isolates obtained from culture collections, and MF423485–MF423695 for the 211 isolates newly obtained in this study. 16S rRNA gene sequences of BRE were deposited under accession no. MF383419–MF383462 and MH760809–MH760813 for the 49 sequences used in the phylogenetic analysis.

Results and Discussion

Relaxed intraspecific host range by Burkholderiaceae-related endobacteria associated with Mortierella spp

Approximately 89% (211 out of 238 isolates) of fungal isolates were newly obtained in the present study. Most of the ITS sequences associated with these isolates (189 out of 226) showed high similarities of more than 97%, which was the threshold in Mortierella spp. representing an almost linear relationship between the number of type materials currently sequenced and the number of identifiable molecular OTUs (30). The other ITS sequences showed similarities of less than 97% (Table S4). These 238 isolates were phylogenetically clustered in 59 species, including the 38 described species (Fig. S1 and Table S4), which represent all seven phylogenetic groups of Mortierella spp. (Fig. 1A) defined by Wagner et al. (53). The number of identified fungal species corresponded to approximately half of the fungal species contained in the custom database.

Fig. 1

The number of isolates of Mortierella examined in the present study (A) and harboring different OTUs of Burkholderiaceae-related endobacteria with different properties, such as phylogenetic groups of the fungal host, climatic zones, and substrates (B), and odds ratios showing the effects of the different properties of isolates of Mortierella on the prevalence of BRE (C). In graph B, Each OTU was defined by the threshold with 97% similarity to the 16S rRNA gene using mothur v.1.36.1. “MorBRE_OTU1”, “MorBRE_OTU2”, and “MorBRE_OTU3”, and other OTUs (MorBRE_OTU4, 5, 6, 7 and 8) were located in the clades MorBRE groups A, B, and C, respectively, shown in the ML phylogenetic tree. In graph C, the odds ratio (OR) with a 95% confidential interval (CI) was estimated using a generalized linear model (GLM) on the presence/absence of BRE (a binary response variable) incorporating the effects of climatic zones, phylogenetic groups, and substrates as categorical explanatory variables, which were the properties of Mortierella isolates (binomial family, logit link function, n=238). The prevalence of BRE in each climatic zone, phylogenetic group, and substrate of Mortierella isolates was compared to that in the temperate zone, phylogenetic group 7, and soil as a reference level, respectively. “NA” indicates that the odds ratio is not available because the prevalence of BRE was not identified in this study.

In the present study, 234 isolates of Mortierella spp. were examined for the presence/absence of BRE. Diagnostic PCR targeted to the bacterial 16S rRNA gene revealed that BRE were detected in approximately 22% (53 out of 238) isolates and 37% (22 out of 59) species of Mortierella (Table 1). The 22 species of Mortierella harboring BRE were classified into five phylogenetic groups defined by Wagner et al. (53): Group 1 (six species), Group 2 (four species), Group 5 (five species), Group 6 (one species), and Group 7 (six species) (Table 1). Mortierella spp. are traditionally classified into nine sections based on their asexual morphologies, i.e., Actinomortierella, Alpina, Haplosporangium, Hygrophila, Mortierella, Schmuckeri, Simplex, Spinosa, and Stylospora (13). Even though this classification was not supported by the phylogenetic classification (53), similarities in asexual morphologies may represent its reproductive strategies, such as dispersion. Among these nine morphology-based sections, 13 species included in the 22 BRE-harboring species were classified into six sections (Actinomortierella [one species], Alpina [one species], Hygrophila [two species], Simplex [one species], Spinosa [five species], and Stylospora [three species]) (Table 1). Previous studies showed that BRE were associated with only two species, M. elongata (phylogenetic group 7, section Hygrophila) and M. minutissima (phylogenetic group 2, section Hygrophila), in Mortierella spp. (32, 37, 50). Therefore, these results suggested that BRE associated with phylogenetically and morphologically broad host species in Mortierella spp.

Table 1 Presence/absence of Burkholderiaceae-related endobacteria (BRE) in isolates of Mortierella obtained from different climatic zones.
Species identified by integrating blastn searches and phylogenetic analyses* No. of isolates harbored BRE/total no. of isolates Presence of BRE Prevalence of BRE in each phylogenetic group of hosts No. of isolates harboring BRE/total no. of isolates obtained from different climates

Cool Temperate Subtropical Unknown
M. alliaceab 0/1 Group 1, 15% (6/41 isolates) 0/1
M. chieniih 1/12 + 1/11 0/1
M. cystojenkiniih 0/1 0/1
M. pulchellah 0/2 0/2
M. selenosporad 0/2 0/2
M. sossauensish 1/2 + 1/2
M. basiparvisporad 1/3 + 0/1 1/2
M. jenkiniih 0/1 0/1
M. parvisporah 1/10 + 0/5 1/5
M. sugadairanah 1/3 + 1/3
Mortierella sp. 1 0/2 0/2
Mortierella sp. 2 1/1 + 1/1
Mortierella sp. 3 0/1 0/1

M. clonocystisd 0/3 Group 2, 24% (9/37 isolates) 0/3
M. epicladiah 0/1 0/1
M. humilisi 3/10 + 1/3 2/6 0/1
M. verticillatai 3/7 + 0/2 3/5
M. horticolai 1/10 + 1/10
M. minutissimad 0/4 0/4
Mortierella sp. “zonata” 2/2 + 2/2

M. calciphilad 0/3 Group 3, 0% (0/11 isolates) 0/3
M. gemmiferad 0/5 0/5
M. kuhlmaniid 0/3 0/3

Dissophora decumbens 0/1 Group 4, 0% (0/9 isolates) 0/1
Gamsiella multidivaricata 0/1 0/1
M. globuliferag 0/7 0/1 0/4 0/2

M. ambiguaa 1/1 + Group 5, 25% (7/28 isolates) 1/1
M. capitataa 0/10 0/10
M. oedorhizag 1/1 + 1/1
M. wolfiih 0/2 0/2
Mortierella sp. 4 2/4 + 2/4
Mortierella sp. 5 2/3 + 2/3
Mortierella sp. 6 1/1 + 1/1
Mortierella sp. 7 0/1 0/1
Mortierella sp. 8 0/4 0/1 0/3
Mortierella sp. 9 0/1 0/1

M. alpinab 3/21 + Group 6, 9% (3/35 isolates) 0/1 2/14 1/6
M. hypsicladiah 0/1 0/1
M. oligosporae 0/1 0/1
M. polycephalae 0/2 0/1 0/1
Mortierella sp. 10 0/7 0/7
Mortierella sp. 11 0/3 0/3

M. biramosae 0/2 Group 7, 36% (28/77 isolates) 0/2
M. elongatad 14/34 + 2/3 6/25 6/6
M. exiguah 0/1 0/1
M. fatshederaed 0/1 0/1
M. gamsiih 4/4 + 4/4
M. thereuopodaeh 0/2 0/2
M. zonatai 0/1 0/1
M. zychaed 0/4 0/4
Mortierella sp. CBS 118520 0/1 0/1
Mortierella sp. 12 1/3 + 1/2 0/1
Mortierella sp. 13 0/4 0/4
Mortierella sp. 14 0/1 0/1
Mortierella sp. 15 1/6 + 0/1 1/5
Mortierella sp. 16 6/7 + 3/4 3/3
Mortierella sp. 17 2/3 + 2/3
Mortierella sp. 18 0/1 0/1
Mortierella sp. 19 0/2 0/2

Prevalence of BRE 22% (53/238 isolates) 37% (22/59 species) 26% (12/47 isolates) 19% (27/141 isolates) 30% (14/46 isolates) 0% (0/4 isolates)
*  Sections based on asexual morphologies were indicated for each name as follows:

a  Actinomortierella,

b  Alpina,

c  Haplosporangium,

d  Hygrophila,

e  Mortierella,

f  Schmuckeri,

g  Simplex,

h  Spinosa,

i  Stylospora,

†  Not designated.

Polyphyly of Burkholderiaceae-related endobacteria associated with Mortierella spp

A ML phylogenetic tree with 1334 positions showed that all BRE were located in the family Burkholderiaceae (Fig. 2). Furthermore, BRE detected from the Mortierella spp., “Ca. Glomeribacter gigasporarum”, and bacterial endosymbionts associated with the root parasitic nematodes, Xiphinema spp. (33), were clustered together in a single clade corresponding to a Glomeribacter-Mycoavidus clade (50). This clade was sister to another clade containing BRE in Rhizopus spp., such as B. rhizoxinica and B. endofungorum, and “Ca. Vallotia” spp. (47) (Fig. 2). Within the former clade, we found that BRE detected from Mortierella spp. were divided into three well-supported clades, identified as MorBRE groups A, B, and C (Fig. 2). By clustering OTUs at a 97% similarity using mothur, 16S rRNA gene sequences located within the MorBRE groups A, B and C were divided into one, two, and five OTUs, respectively (Table 2). A subclade consisting only of “Ca. Glomeribacter gigasporarum” and a subclade containing M. cysteinexigens (named MorBRE group A in the present study) were previously reported within the Glomeribacter- Mycoavidus clade (32, 37, 50); however, the present study found two additional groups within the clade that only consisted of BRE associated with Mortierella spp., named MorBRE groups B and C, respectively (Fig. 2). Our microscopic observations showed that these additional BRE groups were harbored in the host cells (MorBRE group B: Fig. 3B, 4A, 4B, and S2C; MorBRE group C: Fig. 3C, 3D, 3E, 4C, 4D, S2A, and S2B) as well as MorBRE group A (Fig. 3A, S2D, S2E, and S2F). In contrast, bacterial cells were not observed in two non-BRE harbored isolates in which endofungal bacteria were not detected by diagnostic PCR (Fig. 3F and S2G). TEM observation clarified that these phylogenetically new BRE were observed as rod-shape cells in a longitudinal section possessing a double-layered cell envelope and cytoplasm rich in ribosomes within the host hypha (MorBRE group B: Fig. 4A and B; MorBRE group C: Fig. 4C and D) similar to those of M. cysteinexigens (37, 50) and were frequently observed in vacuoles in the host hypha (Fig. 4). Therefore, these results indicated that phylogenetically different BRE were harbored within the hyphae of Mortierella spp. In addition, according to the phylogenetic analysis, the phylogenetic positions of BRE associated with Mortierella spp. were not related to the phylogenetic groups of the fungal hosts (Fig. 2). Evidence for phylogenetic co-divergence between BRE and fungal hosts was previously obtained for both associations, Rhizopus-Burkholderia (21) and Gigasporaceae-“Ca. Glomeribacter” (29). On the other hand, it currently remains unclear whether BRE associated with isolates of Mortierella spp. and its fungal hosts were co-divergent or not. However, according to the ML phylogenetic tree, the transmission of these BRE was not circumscribed only by vertical or horizontal transmission because BRE classified in the same OTUs were sometimes found in several different species of Mortierella (Fig. 2 and Table 2). Furthermore, Lastovetsky et al. (24) newly detected BRE in Acaulospora sp. (Acaulosporaceae, Diversisporales, and Glomeromycotina) as a new fungal host group of BRE. It was phylogenetically close to M. cysteinexigens detected in M. elongata FMR23-6. Therefore, the potential for the horizontal transmission of BRE among Mortierella spp. and other fungal hosts within subphyla Glomeromycotina exists. In the future, the fungal resources obtained in the present study will contribute to the construction of more robust phylogenies of BRE and its hosts using multi-locus genes and a co-phylogenetic analysis of BRE and its hosts in order to estimate whether BRE is transmitted horizontally among different Mortierella spp. and/or among fungal hosts within different subphyla.

Fig. 2

Maximum likelihood (ML) phylogenetic tree of BRE in the family Burkholderiaceae based on partial 16S rRNA gene sequences (1334 positions) using RAxML version 8.1.5 software with the GTRGAMMAI model and bootstrapping (1,000 replicates) with the rapid bootstrap analysis option. Bootstrap values >70% are shown at nodes. The value of the log likelihood was −12105.124158. Wolbachia pipientis was used as an outgroup. Backgrounds show bacterial clades consisting of BRE. BRE clades associated with Mortierella spp. were classified into MorBRE groups A, B, and C. Some subclades including BRE associated with Mortierella spp. obtained from plant materials are indicated by boxes with dashed lines. Taxa names of BRE-detected isolates of Mortierella are shown with different colored backgrounds corresponding to the phylogenetic groups of Mortierella: groups 1 (yellow), 2 (orange), 5 (green), 6 (blue), and 7 (purple) as defined by Wagner et al. (53). Isolates of Mortierella spp. obtained from plant or fungal materials are indicated with “P” and “F”, respectively, according to the name of the isolate; the absence of these marks indicates that the isolates were obtained from soil. BRE-detected isolates of Mortierella spp. used for microscopic observations (LIVE/DEAD staining, FISH, or TEM) are shown in red letters. Diamonds, circles, and triangles at the end of the taxa name indicate the climate at which the hosts were obtained as cool, temperate, and subtropical regions, respectively.

Table 2 Phylogenetic positions of Burkholderiaceae-related endobacteria (BRE) associated with isolates of Mortierella.
Fungal host Burkholderiaceae-related endobacteria


Host species identified by integrating blastn searches and phylogenetic analyses Isolate no. of fungal hosts Placement of phylogenetic clades of detected BRE OTUs of BRE classified by mothur Accession no. of 16S rRNA genes of detected BRE
M. basiparvispora E1425 A OTU1 MF383420
M. elongata FMR23-1 A OTU1 AB558491
M. elongata FMR23-6 A OTU1 AB558492
M. gamsii YTM123 A OTU1 MF383440
M. gamsii YTM124 A OTU1 MF383441
M. gamsii YTM127 A OTU1 MF383442
M. humilis YTM36 A OTU1 MF383428
M. humilis YTM187 A OTU1 MH760813
M. humilis YTM225 A OTU1 MF383462
M. verticillata YTM35 A OTU1 MF383427
M. verticillata CBS 130.66 A OTU1 MF383419
Mortierella sp. 15 YTM171 A OTU1 MH760811
Mortierella sp. 16 YTM110 A OTU1 MF383437
Mortierella sp. 16 YTM112 A OTU1 MF383438
Mortierella sp. 16 YTM113 A OTU1 MF383439
M. alpina YTM25 B OTU2 MF383426
M. alpina YTM40 B OTU2 MF383430
M. elongata FMR23-9 B OTU2 AB558493
M. elongata YTM190 B OTU2 MF383457
M. horticola YTM78 B OTU2 MF383434
M. sossauensis YTM223 B OTU2 MF383461
Mortierella sp. “zonata” YTM23 B OTU2 MF383425
Mortierella sp. 16 YTM179 B OTU2 MF383454
Mortierella sp. 16 YTM184 B OTU2 MF383456
Mortierella sp. 16 YTM185 B OTU2 MH760812
M. ambigua YTM115 B OTU3 MH760809
M. alpina YTM173 C OTU4 MF383452
M. elongata YTM18 C OTU4 MF383423
M. elongata YTM19 C OTU4 MF383424
M. gamsii YTM131 C OTU4 MF383443
M. verticillata YTM181 C OTU4 MF383455
Mortierella sp. 4 YTM104 C OTU4 MF383435
Mortierella sp. 4 YTM108 C OTU4 MF383436
Mortierella sp. 5 YTM49 C OTU4 MF383431
Mortierella sp. 5 YTM50 C OTU4 MF383432
Mortierella sp. 6 YTM53 C OTU4 MF383433
Mortierella sp. 17 YTM212 C OTU4 MF383459
Mortierella sp. 17 YTM214 C OTU4 MF383460
M. elongata FMR13-2 C OTU5 AB558494
M. elongata YTM164 C OTU5 MF383450
M. elongata YTM165 C OTU5 MH760810
M. elongata YTM170 C OTU5 MF383451
M. elongata YTM174 C OTU5 MF383453
M. elongata YTM210 C OTU5 MF383458
M. sugadairana YTM39 C OTU5 MF383429
Mortierella sp. 2 YTM133 C OTU5 MF383444
Mortierella sp. 12 YTM134 C OTU5 MF383445
Mortierella sp. “zonata” YTM160 C OTU5 MF383449
M. elongata YTM138 C OTU6 MF383447
M. elongata YTM139 C OTU6 MF383448
M. parvispora E2010s1 C OTU6 MF383422
M. chienii E1931 C OTU7 MF383421
M. oedorhiza YTM135 C OTU8 MF383446
Fig. 3

FISH images of BRE-harbored isolates (A–E) and BRE-cured isolate of Mortierella (F). Bright field images are shown beside each FISH image. FISH was performed using Cy3-labeled (Red, A–C) or FITC-labeled (Green, D–F) EUB338 probes. Bacterial cells within hyphae and sporangiospores are indicated by arrowheads and arrows, respectively. Rod-shaped endofungal bacterial cells were detected within the hypha of M. elongata FMR23-6 (A), Mortierella sp. “zonata” YTM23 (B), and M. sugadairana YTM39 (E). Rod-shaped endofungal bacterial cells were detected within sporangiospores of M. parvispora E2010s1 (C) and Mortierella sp. 5 YTM49 (D). No bacterial cells were detected within M. sugadairana YTM39s9 (F), which is a BRE-cured isolate of M. sugadairana YTM39 (E). Scale bars: 10 μm.

Fig. 4

TEM images of BRE-harbored isolates of Mortierella (A–D). Bacterial cells were detected within hypha of Mortierella sp. “zonata” YTM23 (A), M. alpina YTM25 (B), M. elongata YTM18 (C), and M. elongata YTM19 (D). b, bacterium; fw, fungal cell wall; ld, lipid droplet; v, vacuole; m, mitochondrion; arrowhead, endofungal bacterium showing binary fission; *, bacterial double-layered cell envelope. Scale bars: 1 μm.

Relationship between abiotic factors and the prevalence of Burkholderiaceae-related endobacteria associated with Mortierella spp

In the present study, BRE were detected in fungal isolates obtained from soil at 29% (44 out of 154 isolates), plant materials at 17% (8 out of 48 isolates), and fungal materials at 11% (1 out of 9 isolates), but was not detected in fungal isolates originating from animal materials, such as bodies and dung (Fig. 1B). BRE were detected in fungal isolates obtained from various locations in different climates in Japan (Table S1 and S2). The prevalence rates of BRE were 30% (14 out of 46 isolates), 26% (12 out of 47 isolates), and 19% (27 out of 141 isolates) in subtropical, cool, and temperate climatic zones, respectively (Fig. 1B and Table 1). Differences in the prevalence of bacterial endosymbionts with a focus on geographical, climatic, and ecological factors are often suggested in arthropod hosts (e.g. 1, 48, 49); however, this has not been attempted for the bacterial endosymbionts of fungi. Based on the results of our examination of BRE, we initially attempted to evaluate whether abiotic factors (the properties of isolates of Mortierella spp.) affected the prevalence of BRE in hosts by calculating OR with a 95% CI using a GLM incorporating the effects of abiotic factors, such as climatic zones, phylogenetic groups, and substrates for categorical explanatory variables. The results obtained showed that most of the differences in the properties of isolates of Mortierella spp. did not appear to affect the prevalence of BRE because most of the ORs of each variable included OR=1 (Fig. 1C). However, CI values were wide because the number of isolates harboring BRE was small (Fig. 1C). Therefore, extensive examinations on the selected Mortierella spp., such as M. elongata, obtained from BRE-harbored isolates from different climatic zones will contribute to more accurate investigations on the effects of environmental factors on the presence/absence of BRE.

An evolutionary perspective on Burkholderiaceae-related endobacteria associated with Mortierella spp

The phylogenetic positions of BRE associated with Mortierella spp. did not appear to be circumscribed by the species of fungal hosts or climatic zones of the fungal hosts isolated (Fig. 2). On the other hand, we found that the phylogenetic positions of some BRE taxa detected in isolates obtained from plant materials mainly clustered into two different clades located in MorBRE groups A and B, respectively (boxes with a dashed line in Fig. 2). Since the number of BRE detected in isolates obtained from plant materials was limited, this result implies that the phylogenetic positions of BRE associated with isolates of Mortierella spp. are circumscribed by the isolation substrates of the hosts. Palomares-Rius et al. (33) previously reported a phylogenetic relationship between BRE and bacterial endosymbionts associated with the plant root parasitic nematodes, Xiphinema spp. Our phylogenetic tree emphasized that the clade containing the bacterial endosymbionts of nematodes was related to the Glomeribacter-Mycoavidus clade and showed that the clade was a sister to clades of BRE associated with Mortierella spp.

Acknowledgements

We thank Dr. Y. Sato for guidance on molecular techniques and LIVE/DEAD staining, and Dr. K. Kai for advice on the FISH method for Mortierella spp. We also thank Dr. E. Usui, Dr. K. Yamamoto, Ms. F. Nakanishi, Ms. H. Nabatame, and Ms. Y. Inose for providing isolates of Mortierella spp., and Dr. T. Masaki and Dr. K. Yamamoto for providing soil samples. This research was supported by a Grant-in-Aid from the Japan Society for the Promotion of Science (JSPS) Fellows (No. 16J08716), a JSPS Grant-in-Aid for Challenging Exploratory Research (No. 15K14902), and a Grant-in-Aid for Scientific Research (C) (No. 17K07695). This research was also supported by a grant from the Institute for Fermentation, Osaka (IFO).

References
 
© 2018 by Japanese Society of Microbial Ecology / Japanese Society of Soil Microbiology / Taiwan Society of Microbial Ecology / Japanese Society of Plant Microbe Interactions.
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