Literature DB >> 25272044

Insights into deep-sea sediment fungal communities from the East Indian Ocean using targeted environmental sequencing combined with traditional cultivation.

Xiao-yong Zhang1, Gui-ling Tang1, Xin-ya Xu1, Xu-hua Nong1, Shu-hua Qi1.   

Abstract

The fungal diversity in deep-sea environments has recently gained an increasing amount attention. Our knowledge and understanding of the true fungal diversity and the role it plays in deep-sea environments, however, is still limited. We investigated the fungal community structure in five sediments from a depth of ∼ 4000 m in the East India Ocean using a combination of targeted environmental sequencing and traditional cultivation. This approach resulted in the recovery of a total of 45 fungal operational taxonomic units (OTUs) and 20 culturable fungal phylotypes. This finding indicates that there is a great amount of fungal diversity in the deep-sea sediments collected in the East Indian Ocean. Three fungal OTUs and one culturable phylotype demonstrated high divergence (89%-97%) from the existing sequences in the GenBank. Moreover, 44.4% fungal OTUs and 30% culturable fungal phylotypes are new reports for deep-sea sediments. These results suggest that the deep-sea sediments from the East India Ocean can serve as habitats for new fungal communities compared with other deep-sea environments. In addition, different fungal community could be detected when using targeted environmental sequencing compared with traditional cultivation in this study, which suggests that a combination of targeted environmental sequencing or traditional cultivation alone. This study is the first to report new insights into the fungal communities in deep-sea sediments environmental sequencing and traditional cultivation will generate a more diverse fungal community in deep-sea environments than using either from the East Indian Ocean, which increases our knowledge and understanding of the fungal diversity in deep-sea environments.

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Year:  2014        PMID: 25272044      PMCID: PMC4182876          DOI: 10.1371/journal.pone.0109118

Source DB:  PubMed          Journal:  PLoS One        ISSN: 1932-6203            Impact factor:   3.240


Introduction

Although once thought to be an uninhabitable milieu owing to its extreme conditions, the deep-sea is now recognized as a home to rich and largely microbial communities [1]. Whitman et al. [2] reported that deep-sea-derived microbial communities, mainly composed of bacteria and archaea, accounted for a total cellular carbon content of approximately 3×1017 g. Besides bacteria and archaea [3]–[5], fungi in deep-sea environments have been extensively studied [6]–[8]. The isolation of deep-sea fungi was first reported approximately 50 years ago from the Atlantic Ocean at a depth of 4450 m [9]. Recently, an increasing number of fungal species were found in several deep-sea environments, e.g. sediments from Gulf of Mexico [1] and Mariana Trench at 11500 m depth [10], calcareous sediments [11], the Chagos Trench at a depth of 5500 m [12] and the Central Indian Basin at about 5000 m depth [8]. Orsi et al. [13] revealed that the deep-sea sediments are vast habitats for fungal life where cell may live on geologic timescale and these active fungi have an overlooked role in organic carbon turnover, which provide a direct evidence for active fungal metabolism in the deep-sea environments. Despite recent advances, the distribution and diversity of fungal communities in deep-sea environments are still largely unknown. With the recent development of more advanced instruments designed for sampling and researching life at greater depths, there has been more interest in evaluating the diversity and ecological role of fungi from deep-sea environments [14]–[20]. Traditionally, fungal diversity studies on deep-sea environmental samples have been based on cultivation techniques [21]–[24]. Fungi from deep-sea environments do not necessarily require extreme culture conditions, and many studies on deep-sea fungi describe using cultivation methods under standard laboratory conditions [21], [22]. Currently, more than 120 fungal species have been isolated from deep-sea environments [6], [18], [21]–[24]. Targeted environmental sequencing analyses, however, have indicated that cultivable fungi are only a small fraction of the total number of fungi inhabiting deep-sea environments [7]. The molecular phylogenetic analysis of clone libraries constructed from environmental samples has become the gold-standard in fungal diversity research, and this technique is thought to be able to detect a wider range of fungi that more accurately represent the investigated environment [25]. To date, several unknown novel phylotypes including DSF-group with the phylum Ascomycota [17], [26], KML11 clade and Rozella in the new described Cryptomycota [26], [27] and BCGI clade [17], have been discovered by molecular phylogenetic analysis. This technique of molecular phylogenetic analysis, however, can be easily biased at many steps of the process, such as PCR primer selection and the DNA extraction method used [20]. Previous studies have shown that the 18S rRNA technique is a valuable tool for assessing the global diversity of eukaryotes [28], [29]. This approach, however, is limited because identification is often restricted to the genus or family level [30]. Buchan et al. [31] reported that the internal transcribed spacer (ITS) regions in fungal rDNA exhibit a high degree of polymorphism between species and are thought to be highly conserved within species. ITS regions can provide better taxonomic resolution than 18S rDNA sequences [16]. To identify the maximum amount of fungal species in the five deep-sea sediments collected from the East Indian Ocean and to find new sequences for phylogenetic studies, environmental gene libraries were constructed after amplifying the sediment DNA using an ITS rRNA gene primer set. Furthermore, the culturable fungi in these sediments were also isolated and identified by amplifying and sequencing the ITS rRNA gene.

Materials and Methods

Ethics statement

All the five sampling locations in this study were included in high seas. Permits for sediment sampling were provided by Ministry of Foreign Affairs of the People’s Republic of China. No specific permissions were required for these locations and the field studies did not involve endangered or protected species.

Study site and sample collection

Five deep-sea sediment samples (A–E) were collected using a Remote Operated Vehicle (ROV) during the East Indian Ocean Open Cruise in March 2013 (Fig. S1 in File S1). The coordinates of Sample A–E were shown in Table 1. The collected sediment samples were mostly undisturbed and compact. The average length of the sediment cores collected from these locations was approximately 30 cm. Sub-cores of these samples were collected from a box corer using an alcohol-sterilized PVC cylinder that had a 5 cm inner diameter. Subsections of these samples were cut from the sediment sub-cores and immediately stored in sterile plastic bags to avoid any aerial contamination [18]. The bags were closed with rubber bands and transported to the laminar flow hood in the laboratory on board. A portion of sediment from the middle of each sub-sample that had not been in contact with the PVC cylinder wall was removed using an alcohol-flame-sterilized spatula and placed in a sterile vial for fungal isolation [21]. Fractions of these sediments were immediately stored at −20°C for direct DNA extraction after fungal isolation.
Table 1

The coordinates of Sample A–E.

SamplesLatitudeLongitudeDepth (m)
A−2°57′N95°19′E4810
B00°00′N90°57′E4532
C00°30′N82°03′E4530
D7°57′N89°27′E4614
E10°00′N84°33′E4571

Fungal isolation and identification

The cultivation and isolation methods for fungi from deep-sea environments do not differ fundamentally from the methods used for fungi from shallow marine environments. Physiological analyses have demonstrated that deep-sea-derived fungi are able to grow in deep-sea salinity and at low temperatures [32]. Three different methods were used for fungal isolation in this study, including the particle plating method [33], dilution plating method [21] and low temperature (10°C) incubation method. These fungal isolation methods are described in more detail in a recently published paper by Zhang et al. [18]. Fungal isolates were identified using a combination of morphology characteristics and the internal transcribed spacer (ITS) sequences. Total genomic DNA was extracted from all of the selected fungal strains using a method described by Lai et al. [16]. From the genomic DNA, nearly full-length ITS sequences were amplified by polymerase chain reaction with the primers ITS1 (5′-TCCGTAGGTGAACCTGCGG-3′) and ITS4 (5′-TCCTCCGCTTATTGATATGC-3′) [34]. These fungal ITS gene sequencing and identification methods are described in more detail in a previously published paper by Toledo-Hernandez et al. [35].

DNA extraction, PCR amplification and clone library construction

Environmental DNA was isolated from two grams of sediment sample from each frozen subsection of the sediment cores using a soil DNA extraction kit (Omega Bio-Tek, Inc., Norcross, GA, USA) according to the manufacturer’s instructions and sterile techniques to avoid cross contamination. The DNA samples from the five sediments were amplified using the primers ITS1 and ITS4. The polymerase chain reaction mixture (20 µl) consisted of 2 µl 10× PCR buffer (500 mM KCl, 100 mM Tris-HCl, 15 mM 1% (w/v) MgCl2, and Triton X-100), 1.6 µl of 2.5 mM dNTP, 0.8 µl of each primer, 0.2 µl of 5 U Taq DNA polymerase (Takara Biotechnology Co., Ltd., Dalian, China), 13.6 µl of water, and 1.0 µl of template DNA (10–100 ng). PCR was conducted using an Eppendorf Mastercycler (Eppendorf German Co., Ltd., Hamburger, German) and the following program: denaturation at 95°C for 5 min, 25 cycles of 30 s at 95°C, 30 s at 55°C, and 90 s at 72°C, and a final extension at 72°C for 10 min. Reaction mixtures lacking template DNA were used as negative controls. Amplified products were gel-purified, ligated with pMD18-T easy vector (Takara Biotechnology Co., Ltd., Dalian, China) and transformed into Escherichia coli cells following the manufacturer’s instructions. Transformants were grown overnight at 37°C on Luria-Bertani agar containing 100 µg/ml ampicillin. The presence of insert was confirmed by PCR with M13 forward and reverse primers. One microliter of broth containing the clone was added to 25 µl of PCR reaction mixture. The PCR protocol included an initial hot start incubation (5 min at °C) followed by 34 cycles of denaturation at 94°C for 30 s, annealing at 55°C for 30 s and extension at 72°C for 1 min, and then a final extension at 72°C for 5 min [8]. Clones containing the positive insert were further processed for plasmid isolation and purification using the Millipore plasmid preparation Kit (Millipore, USA). Sequencing of the PCR products from the plasmids was conducted by Invitrogen (China). A total of five environmental gene libraries were constructed from the DNA samples from the five deep-sea sediments. Approximately 100 clones were screened from each library.

Phylogenetic analyses

All of the vector sequences from the sequenced fungal clones were analyzed using the rRNA Database Project CHECK_CHIMERA program to detect and eliminate the potential chimeric sequences. Pairwise alignment of the sequences was conducted using Clustal W in the MEGA software version 5.0. Conserved motifs were identified, and the sequences were trimmed manually. Clones were grouped into operational taxonomic units (OTUs) using a sequence similarity cut-off value of 98% and the Mothur software version 1.32.1 [36]. Rarefaction curves for the number of observed OTUs were calculated with fungal assemblage at each dataset. A representative sequence from each OTU was queried against an NCBI-GenBank BLASTN search.

Nucleotide sequence accession number

The ITS sequences for 20 culturable fungal isolate representatives and 45 uncultured fungal clone representatives obtained in this study were deposited in GenBank under accession numbers KJ173524–KJ17352 and KJ173554–KJ173590.

Results

Phylogeny of environmental fungal ITS-rDNA sequences

A total of 515 clones from five deep-sea sediment samples A–E (Fig. S1 in File S1) from the East Indian Ocean were sequenced. Of the resulting sequences, 445 sequences were found to be fungal, and a total of 45 operational taxonomic units (OTUs) (Table 2) were identified after clustering based on a 98% sequence identity criterion. The other 70 clones (∼13.6%) were eukaryotic or chimeric in nature and were excluded from this study. Rarefaction curves (Fig. S2 in File S1) were constructed for the ITS clone libraries from samples A–E. Rarefaction curves for three samples (B, C and D) demonstrated a plateau, which indicates that the number of sequences analyzed may sufficiently represent the fungal diversity in these samples. While the rarefaction curves of Sample A and E did not reach a plateau. It is likely that the fungal diversity of the two samples is higher than what was detected in this study.
Table 2

Phylogenetic affiliations of uncultured fungi obtained from deep-sea sediment samples A–E.

OTUClosest identified relativeThe number of clones
no.Taxon (Fungal phylum)GenBank accession no.Similarity %ABCDE
OTU-01 Phoma glomerata (Ascomycota)EU27352110025
OTU-02 Cryptococcus curvatus (Basidiomycota)KF4721369957
OTU-03 Phoma herbarum (Ascomycota)KC311476991
OTU-04a Rhizoscyphus ericae (Ascomycota)JQ711893981
OTU-05a Sporobolomyces lactosus (Basidiomycota)HQ914907991
OTU-06a Trichoderma asperellum (Ascomycota)KC4798191001
OTU-07a Trichosporon moniliiforme (Basidiomycota)AF44441510027
OTU-08aUncultured fungus clone (Ascomycota)GU21193810027
OTU-09a Xeromyces bisporus (Ascomycota)GU733338999
OTU-10aUncultured ascomycete (Ascomycota)EU046087991
OTU-11 Uncultured Geomyces (Ascomycota)JQ346989991
OTU-12 Basidiomycete sp. (Basidiomycota)EU871524992
OTU-13Uncultured soil fungus (Basidiomycota)DQ42087710014
OTU-14 Cryptococcus fragicola (Basidiomycota)AB035588995
OTU-15 Cryptococcus podzolicus (Basidiomycota)FN428930991
OTU-16a Guehomyces pullulans (Basidiomycota)AF4444181002
OTU-17 Basidiomycete sp. (Basidiomycota)EU871524992
OTU-18 Rhodotorula slooffiae (Basidiomycota)AB5663289914
OTU-19 Sterigmatomyces halophilus (Basidiomycota)NR07330210037
OTU-20aUncultured compost fungus (Basidiomycota)DQ365334995
OTU-21 Uncultured Mortierella (Zygomycota)JF8315051001
OTU-22 Uncultured Mortierella (Zygomycota)JF8315039925
OTU-23aUncultured soil fungus (Ascomycota)EU826926992
OTU-24a Alternaria alternata (Ascomycota)GQ9165459939
OTU-25a Cladosporium tenuissimum (Ascomycota)AJ3003311003
OTU-26 Alternaria sp. (Ascomycota)KF888649992
OTU-27 Aspergillus penicillioides (Ascomycota)AY373862972
OTU-28 Uncultured fungus clone (Ascomycota)HQ1431179932
OTU-29 Candida etchellsii (Ascomycota)JQ6532719924
OTU-30 Candida inconspicua (Ascomycota)AB179767996
OTU-31 Candida sake (Ascomycota)AJ549822992
OTU-32 Candida xylopsoci (Ascomycota)FM1783391002
OTU-33a Cladophialophora chaetospira (Ascomycota)EU035404932
OTU-34 Cladosporium cladosporioides (Ascomycota)GU932679992
OTU-35a Cladosporium sphaerospermum (Ascomycota)GU0175011002
OTU-36aUncultured soil fungus (Basidiomycota)DQ4208608921
OTU-37a Eurotium rubrum (Ascomycota)AY373891991
OTU-38a Fusarium solani (Ascomycota)JQ9101591005
OTU-39a Galactomyces candidum (Ascomycota)JN974290100221911
OTU-40a Dipodascus australiensis (Ascomycota)HQ115737994
OTU-41 Geomyces pannorum (Ascomycota)DQ189228991
OTU-42 Hortaea werneckii (Ascomycota)GQ334385992
OTU-43a Hypocrea virens (Ascomycota)GU130297100112
OTU-44 Phoma sp. (Ascomycota)HQ6309999811
OTU-45 Leptosphaeria sp. (Ascomycota)AB752252991
Total9279908995

OTUs marked by a letter (a) are new reports for deep-sea environments. Bolded and italicized OTUs are affiliated with yeasts and filamentous fungi, respectively, and the remaining OTUs are affiliated with unidentified yeasts or filamentous fungi.

OTUs marked by a letter (a) are new reports for deep-sea environments. Bolded and italicized OTUs are affiliated with yeasts and filamentous fungi, respectively, and the remaining OTUs are affiliated with unidentified yeasts or filamentous fungi. Most of the ITS sequences from the 45 OTUs demonstrated ≥98% similarity with sequences from their closest relative taxa in GenBank. Three new sequence types, however, only demonstrated 89%–97% similarity with the existing database. Therefore, these results from the phylogenetic analysis suggest that OTU-27, 33 and 36 are novel fungal taxa that are not closely related to previous identified fungal ITS sequences in public databases (Table 2). The composition indicates that a majority (419/445) of these amplified ITS sequences belong to the phyla Ascomycota (276 clones from 29 OTUs) and Basidomycota (143 clones from 24 OTUs) (Fig. 1 and 2). The other remaining sequences belong to the phylum Zygomycota (26 clones from OUT-21 and 22) (Fig. 2).
Figure 1

Neighbor-joining phylogenetic tree from analysis of ITS rDNA from 29 Ascomycota representative sequences in five libraries.

The numbers at the nodes are the percentages indicating the level of bootstrap support based on a neighbor-joining analysis of 1000 resampled data sets. Only values >50% are shown. The scale bar represents 0.1 substitutions per nucleotide position.

Figure 2

Neighbor-joining phylogenetic tree from analysis of ITS rDNA from 26 Basidomycota and Zygomycota representative sequences (OTU-21 and 22) in five libraries.

The numbers at the nodes are percentages indicating the level of bootstrap support based on a neighbor-joining analysis of 1000 resampled data sets. Only values >50% are shown. The scale bar represents 1 substitution per nucleotide position.

Neighbor-joining phylogenetic tree from analysis of ITS rDNA from 29 Ascomycota representative sequences in five libraries.

The numbers at the nodes are the percentages indicating the level of bootstrap support based on a neighbor-joining analysis of 1000 resampled data sets. Only values >50% are shown. The scale bar represents 0.1 substitutions per nucleotide position.

Neighbor-joining phylogenetic tree from analysis of ITS rDNA from 26 Basidomycota and Zygomycota representative sequences (OTU-21 and 22) in five libraries.

The numbers at the nodes are percentages indicating the level of bootstrap support based on a neighbor-joining analysis of 1000 resampled data sets. Only values >50% are shown. The scale bar represents 1 substitution per nucleotide position. Furthermore, the phylogenetic analyses revealed that 240 clones from 17 OTUs were most closely related to cultivable yeast forms, including three species of genus Cryptococcus (63 clones), Galactomyces candidum (52 clones), Sterigmatomyces halophilus (37 clones), four species of genus Candida (34 clones), Trichosporon moniliiforme (27 clones), Rhodotorula slooffiae (14 clones), Basidiomycete sp. (4 clones), Dipodascus australiensis (2 clones), Guehomyces pullulans (2 clones), Hortaea werneckii (2 clones) and Sporobolomyces lactosus (one clone) (Fig. 1 and Table 2). Another 120 clones from 20 OTUs were closely related to filamentous fungi, including Aspergillus, Alternaria, Cladophialophora, Cladosporium, Eurotium, Fusarium, Geomyces, Hypocrea, Leptosphaeria, Mortierella, Phoma, Rhizoscyphus, Trichoderma and Xeromyces (Fig. 1 and Table 2). The remaining 85 clones from 8 OTUs were closely related to uncultured fungi from soil or plant ecological systems that have been deposited in the NCBI database [37]–[41].

Culturable fungal isolates and species richness

A total of 78 fungal isolates belonging to 20 phylotypes (Fig. 3) were recovered using traditional cultivation. The ITS sequencing results showed that most of these fungal sequences demonstrated >97% similarity with sequences from their closet relative species. The one isolate EIODSF013 (accession number KJ173536), however, only demonstrates 95% similarity with the existing sequence (accession number JX981490) in the NCBI database (Table 3). A multigene analysis combined with detailed morphological and ultra structural studies, however, are needed to determine the novelty of this isolate. Most of the 78 fungal isolates belonged to Ascomycota, including two yeast and 16 filamentous fungal species. Among these species, Aspergillus sp., Penicillium sp. and Simplicillium obclavatum were the most diverse and common, while Alternaria alternata, Aureobasidium pullulans, Cryptococcus liquefaciens, Exophiala dermatitidis, Epicoccum nigrum and Neosetophoma samarorum were the rarest fungal species with only single or double isolates. The remaining species occurred as several isolates.
Figure 3

Neighbor-joining phylogenetic tree from analysis of ITS sequences from fungi isolated from five deep-sea sediments from the East Indian Ocean.

The numbers at the nodes are the percentages indicating the level of bootstrap support based on a neighbor-joining analysis of 1000 resampled data sets. Only values >50% are shown. The scale bar represents 0.05 substitutions per nucleotide position.

Table 3

Phylogenetic affiliations of culturable fungi obtained from deep-sea sediment samples A–E.

IsolatesClosest identified relativeThe number of isolates
no.Fungal genera or species (Phylum)GenBank accession no.Similarity %ABCDE
EIODSF 001a Alternaria alternata (Ascomycota)KF29396499%2
EIODSF 002 Aspergillus niger (Ascomycota)JN67612599%4
EIODSF 003a A. ochraceopetaliformis (Ascomycota)KE38418799%1141
EIODSF 004 A. restrictus (Ascomycota)JX15635299%21
EIODSF 005 A. sydowii (Ascomycota)GU32565799%2
EIODSF 006 A. versicolor (Ascomycota)EF65244299%212
EIODSF 007 Aureobasidium pullulans (Ascomycota)AY21363999%2
EIODSF 008 Cladosporium sphaerospermum (Ascomycota)HQ44324199%213
EIODSF 009 Cryptococcus liquefaciens (Basidiomycota)AF14533199%1
EIODSF 010 Epicoccum nigrum (Ascomycota)KC00566298%1
EIODSF 011 Exophiala dermatitidis (Ascomycota)AY66382899%1
EIODSF 012 Leptosphaeria sp. (Ascomycota)AB75225299%6
EIODSF 013a Neosetophoma samarorum (Ascomycota)JX98149095%1
EIODSF 014a Paraphoma fimeti (Ascomycota)KF25117099%21
EIODSF 015 Penicillium chrysogenum (Ascomycota)GU98508699%2
EIODSF 016 P. citrinum (Ascomycota)JN62489799%142
EIODSF 017a P. toxicarium (Ascomycota)FJ55724799%3
EIODSF 018 Phoma sp. (Ascomycota)EF12040499%212
EIODSF 019 Rhodotorula mucilaginosa (Basidiomycota)EF19222399%4
EIODSF 020a Simplicillium obclavatum (Ascomycota)FJ15623599%53221
Total277101420

Species marked by a letter (a) are new reports for deep-sea environments. Bolded and italicized isolates are included in yeasts and filamentous fungi, respectively.

Neighbor-joining phylogenetic tree from analysis of ITS sequences from fungi isolated from five deep-sea sediments from the East Indian Ocean.

The numbers at the nodes are the percentages indicating the level of bootstrap support based on a neighbor-joining analysis of 1000 resampled data sets. Only values >50% are shown. The scale bar represents 0.05 substitutions per nucleotide position. Species marked by a letter (a) are new reports for deep-sea environments. Bolded and italicized isolates are included in yeasts and filamentous fungi, respectively.

Discussion

New insights into the fungal communities in deep-sea environments

The fungal diversity in deep-sea environments has recently gained an increasing amount of attention. Our knowledge and understanding of the true fungal diversity and the roles this diversity plays in deep-sea environments, however, is still limited. The aim of the present study was to obtain the maximum amount of fungal diversity from deep-sea sediments collected in the East Indian Ocean. A total of 45 fungal OTUs and 20 culturable fungal phylotypes were recovered in this study (Table 2 and 3), which revealed that there is a great amount of fungal diversity in the deep-sea sediments collected in the East Indian Ocean. Recently, many studies have shown that there is an increasing number of culturable fungal species and uncultured fungal clones in deep-sea sediments from the Central Indian Basin [8], [21], [42], South China Sea [16], [18] and Eastern Equatorial Pacific [43]. Few studies, however, have specifically focused on the fungal diversity in the deep-sea environments from the East Indian Ocean. This study is the first to report new insight into the fungal communities in deep-sea sediments from the East Indian Ocean using a combination of targeted environmental sequencing and cultivation. These findings increase our knowledge and understanding of the fungal diversity in deep-sea environments. In this study, most of the clones (94.2%) detected by targeted environmental sequencing and all of the culturable fungal isolates recovered using traditional cultivation belonged to the phyla Ascomycota and Basidiomycota (Table 2 and 3). The remaining 5.8% clones (OTU-21 and 22) belonged to the phylum Zygomycota (Table 2). In addition to these three phyla, the phylum Chytridiomycota has also been detected in many deep-sea environments, e.g. Izu-Ogasawara Trench [6]. In this study, however, no putative Chytridiomycota sequences were detected in any of the five sediment samples collected from the East Indian Ocean. We do not believe that our methods were incapable of detecting these higher taxonomic groups because the same primer set has been shown to be able to detect a diverse range of these taxa from deep-sea environments [16], [44], [45]. Therefore, these results suggest that the fungal communities in the deep-sea sediments from the East Indian Ocean tend to be dominated by Ascomycota and Basidomycota, while other fungal taxonomic groups are rare or absent. Notably, 44.4% (20 out of 45 OTUs, Table 2) fungal OTUs and 30% (6/20) culturable fungal phylotypes (Table 3) identified in this study are new reports for deep-sea sediments (Table 2 and 3). Some of these species demonstrated phylogenetic similarity to fungal species and genera known to be found in shallow-sea environments. For examples, A. alternata was found in tropic sea grass Enhalus acoroides [45]; E. rubrum, H. virens and Leptosphaeria sp. were found in marine mangroves [46]; A. ochraceopetaliformis and C. tenuissimum were found in marine corals and sponges [36], [47]; C. inconspicua may be found in crabs [48]. Other species were affiliated with culturable or uncultured fungi from soil or plant ecological systems. For examples, R. ericae was isolated from lodgepole pine in central British Columbia [49]; and D. australiensis was recovered from agricultural soil [50]; uncultured soil fungus (OTU-13) was detected in a genetically modified rice ecosystem [41]. These results may appear to be inconsistent, but previous studies have shown that while a majority of the fungal isolates from deep-sea environments were psychrotolerant, they grew more rapidly at 30°C than 5°C [42], [51]. Moreover, most of the fungi isolated from deep-sea environments are halotolerant and do not absolutely require seawater for growth [24], [32]. It is possible that there are no true indigenous fungi in deep-sea environments and that species from terrestrial environments have gradually adapted to deep-sea extreme conditions [6].

Yeast fungi detected by targeted environmental sequencing

Our targeted environmental sequencing results showed 53.9% fungal clones were closely related to yeast fungi. Among the yeast forms in this study, most of the clones represented phylotypes relevant to the genera Cryptococcus and Galactomyces. Some of Cryptococcus-related phylotypes are psychrotolerant and have been found in the majority of deep subseafloor samples from North Pond, Hydrate Ridge, Peru Margin and Eastern Equatorial Pacific [43], but Galactomyces-related phylotypes are rarely recovered from deep-sea environments. Four OTUs were closely related to Candida sp., which are considered to be associated with ecosystems in anaerobic environments [26]. In addition to the previously mentioned yeast phylotypes, Rhodotorula, Sterigmatomyces and Trichosporon yeasts were also found to be abundant in this study. Previous studies have shown that Rhodotorula spp. demonstrate remarkable ubiquity based on their presence in several different habitats, such as deep-sea sediments [52]. Phylotypes related to the genera Trichosporon and Sterigmatomyces are known pathogens or parasites of marine animals, which suggests that they may also be opportunistic pathogens or parasites of deep-sea animals [47], [53]. Furthermore, OUT-12 and 17 are related to unidentified Basidiomycetious yeasts (EU871524) and were detected in a water column from the Equatorial Indian Ocean (unpublished). The remaining yeast forms were singletons or doubletons, indicating the low abundance of these clones.

Filamentous fungi dominated the fungal community based on traditional cultivation

In this study, filamentous fungi dominated the fungal community using traditional cultivation. The five genera Aspergillus, Penicillium, Simplicillium, Cladosporium and Phoma were distributed in more than three sediments from the East Indian Ocean (Table 2). Members of the mycelia genera Aspergillus and Penicillium are known to be globally distributed fungal taxa. It seems doubtful that these fungal species are indigenous to deep-sea environments, and evidence of physiological adaption of these species to deep-sea environments had been reported by Raghukumar et al. [54]. Moreover, Aspergillus spp. were frequently detected in anaerobic marine sediments and were shown to play an important role in the denitrification process [20]. These findings suggest that these Aspergillus species may play a potentially versatile role for fungi in major ecological processes in the deep-sea environments. The genus Simplicillium was segregated from Verticillium and contains 10 species [55], [56]. These Simplicillium species occur in a broad range of ecological niches, such diseased plant tissue, soil, human nails, dog tissue and mushrooms [55], [57]. In this study, we report for the first time the presence of Simplicillium sp. in deep-sea sediments. Phoma species are known to be associated with not only land plants but also with marine plants. Previous studies have demonstrated that many terrestrial microorganisms could accumulate in deep-sea sediments [58], [59]. One terrestrial fungal genus, Cladosporium was isolated from three deep-sea sediments below 3000 m in this study, which indicates that sedimentation may be an important factor responsible for the accumulation of facultative marine fungi in deep-sea sediments. In addition, only two isolates belonging to A. alternate were recovered using traditional cultivation, but this species was also detected by targeted environmental sequencing in this study. Therefore, A. alternata should be abundant in these deep-sea sediments from the East Indian Ocean. Previous studies have shown that the genera Alternaria was found in nearly every survey of free-living fungal communities associated with biological soil crusts [60], [61]. Few Alternaria sp., however, were detected in deep-sea environments.

Comparison of fungal community by targeted environmental sequencing and traditional cultivation

A distinct difference in the fungal community based on targeted environmental sequencing compared with traditional cultivation was that the Zygomycota spp. was not recovered by traditional cultivation but was detected by targeted environmental sequencing. Previous studies have also shown that Zygomycota spp. could be found in different deep-sea environments using targeted environmental sequencing [17], [24]. Currently, however, there are no reports of isolating Zygomycota species from deep-sea environment cultures. After a further comparison of the fungal phylotypes recovered using these two methods, it was found that the majority of the fungal phylotypes recovered using targeted environmental sequencing could not be recovered using a traditional cultivation method. This finding is consistent with the findings published by Le Calvez et al. [24], who reported that there are striking differences in the deep-sea fungal diversity results when using targeted environmental sequencing compared with traditional cultivation. These findings suggest that a combination of targeted environmental sequencing and traditional cultivation will generate a more accurate assessment of the fungal diversity in deep-sea environments compared with using targeted environmental sequencing or traditional cultivation alone. Furthermore, to obtain an even greater abundance of deep-sea fungi, it is necessary to combine the methods used in this study with other methods, such as the microscopic observation of samples appropriately staining, FISH, measuring ergosterol, metagenomic methods, and other new powerful tools expected to be developed in the future [62]. Contains Fig. S1 Map of the East Indian Ocean, location and depth of the sampling site and Fig. S2 Rarefaction curves constructed for ITS clone libraries from each of the five sampling sites. ITS, internal transcribed spacer. (DOCX) Click here for additional data file.
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1.  Microbial diversity in the deep sea and the underexplored "rare biosphere".

Authors:  Mitchell L Sogin; Hilary G Morrison; Julie A Huber; David Mark Welch; Susan M Huse; Phillip R Neal; Jesus M Arrieta; Gerhard J Herndl
Journal:  Proc Natl Acad Sci U S A       Date:  2006-07-31       Impact factor: 11.205

2.  Resource availability controls fungal diversity across a plant diversity gradient.

Authors:  Mark P Waldrop; Donald R Zak; Christopher B Blackwood; Casey D Curtis; David Tilman
Journal:  Ecol Lett       Date:  2006-10       Impact factor: 9.492

3.  Occurrence and diversity of yeasts in the mid-atlantic ridge hydrothermal fields near the Azores Archipelago.

Authors:  Mário Gadanho; José Paulo Sampaio
Journal:  Microb Ecol       Date:  2005-11-24       Impact factor: 4.552

4.  Molecular evidence demonstrating the basidiomycetous fungus Cryptococcus curvatus is the dominant microbial eukaryote in sediment at the Kuroshima Knoll methane seep.

Authors:  Kiyotaka Takishita; Masashi Tsuchiya; James D Reimer; Tadashi Maruyama
Journal:  Extremophiles       Date:  2005-12-10       Impact factor: 2.395

5.  A new alkaloid from the marine-derived fungus Hypocrea virens.

Authors:  Tao Liu; Zhan-Lin Li; Yu Wang; Li Tian; Yue-Hu Pei; Hui-Ming Hua
Journal:  Nat Prod Res       Date:  2011-06-03       Impact factor: 2.861

6.  Microbial flora in the deepest sea mud of the Mariana Trench.

Authors:  H Takami; A Inoue; F Fuji; K Horikoshi
Journal:  FEMS Microbiol Lett       Date:  1997-07-15       Impact factor: 2.742

Review 7.  Prokaryotes: the unseen majority.

Authors:  W B Whitman; D C Coleman; W J Wiebe
Journal:  Proc Natl Acad Sci U S A       Date:  1998-06-09       Impact factor: 11.205

8.  Yeast forms dominate fungal diversity in the deep oceans.

Authors:  David Bass; Alexis Howe; Nick Brown; Hannah Barton; Maria Demidova; Harlan Michelle; Lily Li; Holly Sanders; Sarah C Watkinson; Simon Willcock; Thomas A Richards
Journal:  Proc Biol Sci       Date:  2007-12-22       Impact factor: 5.349

9.  Tasting soil fungal diversity with earth tongues: phylogenetic test of SATé alignments for environmental ITS data.

Authors:  Zheng Wang; R Henrik Nilsson; Francesc Lopez-Giraldez; Wen-ying Zhuang; Yu-cheng Dai; Peter R Johnston; Jeffrey P Townsend
Journal:  PLoS One       Date:  2011-04-21       Impact factor: 3.240

10.  Community profiling and gene expression of fungal assimilatory nitrate reductases in agricultural soil.

Authors:  Markus Gorfer; Marzena Blumhoff; Sylvia Klaubauf; Alexander Urban; Erich Inselsbacher; Dragana Bandian; Birgit Mitter; Angela Sessitsch; Wolfgang Wanek; Joseph Strauss
Journal:  ISME J       Date:  2011-05-12       Impact factor: 10.302

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  22 in total

1.  What lies beneath? Fungal diversity at the bottom of Lake Michigan and Lake Superior.

Authors:  Hannah E Wahl; Daniel B Raudabaugh; Elizabeth M Bach; Tiffany S Bone; Mark R Luttenton; Robert H Cichewicz; Andrew N Miller
Journal:  J Great Lakes Res       Date:  2018-01-10       Impact factor: 2.480

2.  Fungi Present in Antarctic Deep-Sea Sediments Assessed Using DNA Metabarcoding.

Authors:  Mayara Baptistucci Ogaki; Otávio Henrique Bezerra Pinto; Rosemary Vieira; Arthur Ayres Neto; Peter Convey; Micheline Carvalho-Silva; Carlos Augusto Rosa; Paulo E A S Câmara; Luiz Henrique Rosa
Journal:  Microb Ecol       Date:  2021-01-06       Impact factor: 4.552

3.  Fungal communities from the calcareous deep-sea sediments in the Southwest India Ridge revealed by Illumina sequencing technology.

Authors:  Likui Zhang; Manyu Kang; Yangchao Huang; Lixiang Yang
Journal:  World J Microbiol Biotechnol       Date:  2016-04-02       Impact factor: 3.312

4.  Fungal diversity in the coastal waters of King George Island (maritime Antarctica).

Authors:  Gabriela Garmendia; Angie Alvarez; Romina Villarreal; Adalgisa Martínez-Silveira; Michael Wisniewski; Silvana Vero
Journal:  World J Microbiol Biotechnol       Date:  2021-07-29       Impact factor: 3.312

5.  Cultivable yeasts associated with marine sponges in the Gulf of Thailand, South China Sea.

Authors:  Chutima Kaewkrajay; Sumaitt Putchakarn; Savitree Limtong
Journal:  Antonie Van Leeuwenhoek       Date:  2021-02-11       Impact factor: 2.271

6.  The phoma-like dilemma.

Authors:  L W Hou; J Z Groenewald; L H Pfenning; O Yarden; P W Crous; L Cai
Journal:  Stud Mycol       Date:  2020-05-21       Impact factor: 16.097

7.  Cultivable fungi present in deep-sea sediments of Antarctica: taxonomy, diversity, and bioprospecting of bioactive compounds.

Authors:  Mayara B Ogaki; Lívia C Coelho; Rosemary Vieira; Arthur A Neto; Carlos L Zani; Tânia M A Alves; Policarpo A S Junior; Silvane M F Murta; Emerson C Barbosa; Jaquelline G Oliveira; Isabela P Ceravolo; Patrícia O Pereira; Betania B Cota; Roberta O Viana; Viviane S Alves; Luiz H Rosa
Journal:  Extremophiles       Date:  2019-11-22       Impact factor: 2.395

8.  Aspergillus sydowii and Other Potential Fungal Pathogens in Gorgonian Octocorals of the Ecuadorian Pacific.

Authors:  M Mar Soler-Hurtado; José Vladimir Sandoval-Sierra; Annie Machordom; Javier Diéguez-Uribeondo
Journal:  PLoS One       Date:  2016-11-30       Impact factor: 3.240

Review 9.  A Brief Review of Bioactive Metabolites Derived from Deep-Sea Fungi.

Authors:  Yan-Ting Wang; Ya-Rong Xue; Chang-Hong Liu
Journal:  Mar Drugs       Date:  2015-07-23       Impact factor: 5.118

10.  Diversity and distribution of fungal communities in the marine sediments of Kongsfjorden, Svalbard (High Arctic).

Authors:  Tao Zhang; Neng Fei Wang; Yu Qin Zhang; Hong Yu Liu; Li Yan Yu
Journal:  Sci Rep       Date:  2015-10-23       Impact factor: 4.379

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