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Fungal diversity of the hypersaline Inland Sea in Qatar

  • Rashmi Fotedar

    Rashmi Fotedar works as an expert, Department of Genetic Engineering, Ministry of Municipality and Environment, Doha, Qatar. She earned her Master’s in molecular biology from University of Technology, Sydney, Australia and her PhD from All India Institute of Medical Sciences New Delhi, India. Her research interests include marine microbiology and molecular characterization of fungi and bacteria from environment and humans.

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    , Anna Kolecka

    Anna Kolecka is a researcher at Westerdijk Fungal Biodiversity Institute, Utrecht, The Netherlands. From 2010 to 2017 she was working as a postdoc in the Yeast Research Group, led by Teun Boekhout. During those years she extensively studied the implementation of MALDI-TOF mass spectrometry for yeast identification and DNA-based molecular approaches for fungal taxonomy. She further explored the application of proteomics for fungal discrimination, recently by using high resolution accurate mass-mass spectrometry (HRAM-MS). She completed her MSc Eng studies in environmental protection at Gdansk University of Technology, Poland in 2005 and later received her PhD in microbiology at Comenius University, Bratislava, Slovakia in 2011.

    , Teun Boekhout

    Teun Boekhout, works as a principal investigator at Westerdijk Fungal Biodiversity Institute (previously known as CBS Fungal Biodiversity Centre, CBS-KNAW), Utrecht, and Institute of Biodiversity and Ecosystem Dynamics, University of Amsterdam, Amsterdam, The Netherlands. He studied biology in Utrecht where he also graduated. Since 1982 he is working in mycology. In 2018 he was elected Fellow of the American Academy of Microbiology. In 2011 he was editor of The yeasts, a taxonomic study and presently he is editor in chief of The yeasts, an open access platform on yeast diversity.

    , Jack W. Fell

    Jack W. Fell, PhD, Professor Emeritus, University of Miami. Chairman, Science Advisory Board, Bahamas Marine EcoCentre. Dr Fell a marine scientist, with his colleagues and students, studied microbial ecology from the tropics to Antarctic, mangroves to deep sea. His lab research included basidiomycetous yeast mating genetics, he was a pioneer in basidiomycete molecular phylogeny and developed molecular probes for rapid species detection of marine microbes and human pathogens.

    , Ameena Al-Malki

    Ameena Al-Malki works as a specialist in Genetic Engineering Department, Biotechnology Centre, Ministry of Environment, Doha, Qatar. She is involved in studies related to isolation and molecular identification of microorganism from marine environment, detection of GMOs in agricultural and food products. Her fields of interest include the molecular characterization of bacteria and fungi from environmental samples.

    , Aisha Zeyara

    Aisha Zeyara works as an expert in Department of Genetic Resources, Ministry of Municipality and Environment, Doha, Qatar. She has a degree in microbiology and molecular biology from Qatar University, Doha, Qatar. Aisha is a molecular microbiologist and has been involved in research studies including isolation, identification and characterization of microbial pathogens from Qatari marine environment.

    and Masoud Al Marri

    Masoud Al Marri, works as Director, Agricultural Research Department, Ministry of Municipality and Environment, Doha, Qatar. He earned his Master’s degree from University of Florida, USA and has been involved in research projects related to marine environment and environmental monitoring of marine, ground water and air in Qatar.

Published/Copyright: November 17, 2018

Abstract

The hypersaline Inland Sea in Qatar constitutes a unique ecosystem characterized by salinities up to saturation, extreme temperature fluctuations, and limited rainfall. To reveal the fungal diversity of this environment, we isolated fungi from water samples collected at the Inland Sea. Taxonomic identification of the isolates was done via DNA barcoding of the ITS1 and ITS2 ribosomal DNA (rDNA) domains and the D1/D2 domains of the nuclear large subunit rDNA. Additional genes, including glyceraldehyde-3-phosphate dehydrogenase (gapdh) and translation elongation factor 1-alpha (tef1), were included for isolates of Alternaria, actin (Act) for Cladosporium, part of the beta-tubulin (BenA) and calmodulin (CaM) genes for Aspergillus and Penicillium. In total, 159 fungal isolates, including 85 Ascomycota and 74 Basidiomycota, were obtained from the water samples collected during four samplings in the winter and summer seasons. About 14% (22/159) of the strains, presumably novel species, were preliminarily identified to the genus level. This is the first report highlighting the diversity of fungi from the hypersaline Inland Sea in Qatar.

Introduction

Fungi are ubiquitous microorganisms that are part of the microbiota occurring in natural ecosystems, including fresh and marine waters ranging from the ocean surface to the deep sea, eutrophic to ultra-oligotrophic lakes, lagoons, rivers, ground waters, melting water and ice of glaciers (Fell et al. 2011, Turchetti et al. 2013, Gunde-Cimerman and Zalar 2014, Grum-Grzhimaylo et al. 2016, Mokhtarnejad et al. 2016). Fungal diversity in so-called extreme environments may be affected by a variety of abiotic and biotic factors, including temperature, pressure, UV radiation (UVR), salinity, presence of fauna, flora and other microorganisms, run-off from soils and spills, and anthropogenic effluents. In these extreme habitats the interactions between abiotic factors, for instance temperature, salinity, and pH, result in the colonization by microorganisms adapted to these environmental conditions (Gunde-Cimerman et al. 2000, Pedros-Alio et al. 2000, Pedros-Alio 2004).

High concentrations of salt (hypersalinity) result in an extreme environment with limited fungal and other microbial growth. Due to this strong selection pressure the diversity of halophilic and halotolerant fungi decreases with increasing salt concentrations (Gunde-Cimerman et al. 2000, Butinar et al. 2005a, Gunde-Cimerman and Plemenitaš 2005, Grum-Grzhimaylo et al. 2016). Many genera of fungi such as Aspergillus P. Micheli ex Halle, Alternaria Nees, Aureobasidium Viala et G. Boyer, Cladosporium Link, Penicillium Link and Hortaea Nishim. et Miyaji, have been reported from hypersaline environments (Kis-Papo et al. 2001, Diaz-Munoz and Montalvo-Rodrigue 2004, Gunde-Cimerman et al. 2004, Butinar et al. 2005a, Coelho et al. 2010, Al-Musallam et al. 2011, Nazareth et al. 2012, Jaouani et al. 2014, Mokhtarnejad et al. 2016).

The Inland Sea is a hypersaline lagoon at the inlet of the Arabian Gulf located in southeast Qatar, bordering Saudi Arabia. This lagoon extends 15 km from north to south and 12 km from east to west and is connected to the Arabian Gulf by a 10-km long channel that allows exchange of water mass and subsequent interaction with bottom substrata (Figure 1). The area surrounding the Inland Sea is characterized by the presence of large mobile sand dunes, a tidal embayment system, inland and coastal saltpans, salt hills, stony deserts, elevated areas, and rocky ridges. The Inland Sea is a largely uninhabited area of global importance (Schwarze et al. 2005), which was nominated for the World Natural Heritage List (http://whc.unesco.org/en/tentativelists/5317/). In 1993 Inland Sea was declared a water sanctuary by Ministerial Decree No.78 of the Ministry of Municipal Affairs and Agriculture of Qatar that banned all commercial fishing activities. Because of its connectivity to the Arabian Gulf, Inland Sea is characterized by a pronounced salt gradient with salinities ranging from 57 to 75 in the tidal embayment area with saturated salt conditions in the saltpans near the coastal zones. These characteristics offer a unique opportunity to investigate microbial communities along a natural pronounced salinity gradient, with the original microbiota recruited from the Arabian Gulf.

Figure 1: Map of Inland Sea of Qatar and location of sampling sites. Image Map courtesy: Centre for GIS, Ministry of Municipality and Environment. www.mme.gov.qa.
Figure 1:

Map of Inland Sea of Qatar and location of sampling sites. Image Map courtesy: Centre for GIS, Ministry of Municipality and Environment. www.mme.gov.qa.

The aim of this investigation was to assess the fungal diversity in the hypersaline ecosystem of Inland Sea. Sequencing of different genes was done via DNA barcoding of the ITS1 and ITS2 ribosomal DNA (rDNA) domains and the D1/D2 domains of the nuclear large subunit rDNA. Additional genes, including glyceraldehyde-3-phosphate dehydrogenase (gapdh) and translation elongation factor 1-alpha (tef1), were included for isolates of Alternaria, actin (Act) for Cladosporium, part of the beta-tubulin (BenA) and calmodulin (CaM) genes for Aspergillus and Penicillium.

Materials and methods

Inland Sea sampling sites and collection of water samples

The Inland Sea is located at the inlet of the Arabian Gulf in southeast Qatar (N 24.625308; E051.297259; Figure 1). This area is an arid region characterized by high solar radiation, high salinities ranging from 57 to 75, and limited rainfall (75.2 mm per year). Sampling at eight locations (Figure 1, Table 1) took place during the winter (December 2013) and summer (September 2014) seasons. Seven coastal sites (INS1-INS7) were sampled near the littoral zone in the vicinity of salt pans at a depth of 0.5 m. One site (INS8) was sampled at a depth of 2.5 m in the pelagic zone at approximately 250 m from the coast (Table 1). INS8 was located at the entrance of the 10-km-long channel that allows exchange of water from the Arabian Gulf to the lagoon. Sites INS2, INS6, and INS7 were influenced by human activity due to the proximity of recreational areas and camps, which are allowed in the area from October to April.

Table 1:

Details of sampling sites at the Inland Sea, characteristics of water samples and fungal counts.

Station/depth (m)CoordinatesSampling season/monthSalinitypHTemp. (°C)Yeast count (CFUa/l)Filamentous fungi count (CFUa/l)<<#Hvind>>
INS1/0.5N 24.6706; E 051.2884Winter/Dec 2013738.0624–2570100
INS2/0.5N 24.6171; E 051.3573Winter/Dec 2013758.0624–25140100
INS3/0.5N 24.65787; E 51.28368Summer/Sept 2014728.0730–329015
INS4/0.5N 24.66417;E 51.29282Summer/Sept 2014738.230–32015
INS5/0.5N 24.64786; E51.30041Summer/Sept 2014758.130–32015
INS6/0.5N 24.64357; E 51.33078Summer/Sept 2014748.230–3271010
INS7/0.5N 24.62436; E 51.34179Summer/Sept 2014728.13291010
INS8/2.5N 24.5522; E 051.3325Summer/Sept 201457.37.9932698
  1. aColony forming units (CFU) based on gross morphology of colonies seen on the filter paper. The yeast column included all the yeast isolates and also Aureobasidium spp. and Hortaea werneckii which grew on the medium as yeasts.

The distances between the sampling sites (INS1-INS7) ranged from approximately 1–3 km, whereas INS8 was further away, approximately 8.2 km from INS2 (Figure 1). Water samples were collected in a 1.7-l Niskin Water Sampler (model 1010) with survey outboard motor boats. The water samples were collected in sterile glass bottles of 1 l that were transferred to the laboratory within 2–3 h after collection, and processed immediately for the isolation of fungi with standard microbiological methods. Marine water parameters, such as temperature, salinity, and pH, were measured in three replicate readings with a 650 MDS Data Logger and 6920 V2 multiparameter, water Quality Sonde (Xylem Analytics, UK) calibrated against standard solutions.

Isolation, identification, and characterization of yeasts and filamentous fungi

Culture methods

For the isolation of fungi, five volumes of 200 ml of water per site were filtered through sterile nitrocellulose membranes (0.45 μm pore size; 47 mm diameter, Merck-Millipore, Ltd., Ireland) with a sterilized filtration device. The process was replicated three times for each sampling site. The filters were placed on modified glucose-yeast extract-peptone agar (GYPA) medium (2% glucose (Conda laboratories, Spain), 1% peptone (Conda laboratories, Spain), 0.5% yeast extract (Conda lab, Spain), 0.05% chloramphenicol (Sigma Aldrich, USA), 1.7% agar, 50% filtered water collected from Inland Sea). The medium was prepared with Inland Sea water obtained from the same sites where the water samples were collected. Initial experiments with the incubation temperatures of >25°C and 30°C for summer and winter seasons, respectively, showed an overgrowth of filamentous fungi, which obscured the yeast colonies. The plates were consequently incubated at 17°C and 25°C for 8–10 weeks for the winter and summer samples, respectively (Fell et al. 2011).

The plates were inspected for fungal growth at intervals of 48–72 h and cell counts (CFU (colony forming unit) l−1) of yeasts and filamentous fungi were made with a stereoscopic microscope (Olympus SZX 16, Japan). The fungal count was scored after 3, 5, 7, 14, 30 and 60 days of incubation and the averages (per site/per sampling) of the total viable yeast and filamentous fungi were calculated. Microscopic and morphological observations were made with an Olympus SZX 16 stereomicroscope (Olympus, Japan). At least one colony of each macro-morphological colony type was picked and subcultured onto a fresh medium for further purification. For yeasts, purification of isolates was performed on modified GYPA plates, whereas potato dextrose agar (PDA, Conda Laboratories, Spain) plates were used for filamentous fungi. The isolates were purified by repeated sub-culturing at least three to five times and stored in 50% glycerol (Avonchem, Cheshire, UK) in sterile distilled water at −20°C.

PCR amplification, sequencing, and phylogenetic analyses

For molecular identification, genomic DNA was extracted in 96-well plates following the PrepMan TM Ultra (Applied Biosystems, UK) protocol (Stielow et al. 2015). The internal transcribed spacer 1 and 2 regions (ITS), including the 5.8S rDNA and the D1/D2 domains of the nuclear large subunit (LSU) rDNA, were used for molecular identification (Fell et al. 2000, Scorzetti et al. 2002, Vu et al. 2016). The primers ITS4 and ITS5 (White et al. 1990) were used to amplify the ITS regions. The LSU region was amplified with the primers LR0R (Rehner and Samuels 1994) and LR5 (Vilgalys and Hester 1990). PCR reactions for amplification were performed in volumes of 12.5 μl containing 2.5 μl of the genomic DNA as reported by Stielow et al. (2015). The PCR product was checked by agarose gel electrophoresis, purified with Fast AP, the alkaline phosphatase (Fermentas, Thermo Fisher Scientific, USA) and cycle-sequenced with the ABI Big Dye™ v3.1 technology (Thermo Fisher Scientific, USA). To increase the taxonomic resolution for some groups of filamentous fungi, additional barcodes were used. For Cladosporium isolates, part of the actin (act) gene was amplified with the primer set ACT-512F and ACT-783R (Carbone and Kohn 1999) as described in Groenewald et al. (2013). For Alternaria species, part of the gapdh and tef1 genes were amplified with the primer sets gpd1 and gpd2 (Berbee et al. 1999) and EF1-728F and EF1-986R (Carbone and Kohn 1999), respectively (Woudenberg et al. 2013). For Aspergillus and Penicillium species, part of the beta-tubulin (BenA) and calmodulin (CaM) genes amplified with the primer sets Bt2a-F and Bt2b-R (Glass and Donaldson 1995) and Cmd5-F and Cmd6-R (Hong et al. 2005), respectively, were sequenced as described in Samson et al. (2014) and Visagie et al. (2014). Forward and reverse sequences were manually corrected with SeqMan software v 8.0.2 (DNA Star Inc., Madison, WI, USA). The resulting consensus sequences were compared by Basic Local Alignment Search Tool (BLASTn) (Altschul et al. 1990) with sequences available in the GenBank database for primary identifications (https://blast. ncbi.nlm.nih.gov/Blast.cgi?PAGE_TYPE=BlastSearch). All sequences from the Qatar isolates were grouped by genus and aligned with Clustal W in MEGA v.6 software (Tamura et al. 2011, 2013) with sequences of relevant type strains. Phylogenetic analysis of the LSU and ITS regions followed the procedures of Fell et al. (2000) and Scorzetti et al. (2002). Phylogenetic trees based on the D1/D2 sequence were constructed by using the program provided within the MEGA6 software package. Phylogenetic placement of the novel species was analyzed with the maximum likelihood method (Tamura et al. 2011, 2013). Based on this analysis and the initial BLAST scores, the identity of the isolates at genus, section or species (-complex) level is listed in Table 2.

Table 2:

Species of fungi isolated from the Inland Sea, Qatar.

GroupSpecies recoveredSite/No. of isolatesStrains sequenced bITS-GenBank accession numbersLSU-GenBank accession numbersGapdh-GenBank accession numbersTef1-GenBank accession numbersActin (A)/β-tubulin (BT) Calmodulin (C) GenBank accession numbersNo. of isolates in WinterNo. of isolates in SummerTotal no. (%)
AscomycotaAlternaria spp.aINS8 (4)2M108AKY387606KY781812KY387604KY387608246 (3.8)
INS1 (2)INM7KY387605KY781811KY387603KY387607
Alternaria sect.

Alternaria

D.P. Lawrence, P.B.

Gannibal, T.L. Peever, B.M. Pryor
INS1 (3)

INS2 (5)

INS3 (1)

INS8 (1)
INM4

INM10
KY744118

KY744136

MF084400

MF084401
MF084404

MF084405


8210 (6.3)
Alternaria sect.

Ulocladioides Woudenberg et Crous
INS1 (1)

INS8 (1)
INM5

2M109




MF084402

MF084403
MF084406



112 (1.2)
Aspergillus citrinoterreusINS8 (1)2M110BKY781744KY781745BT-MF084376

C-MF084381
011 (0.6)
J. Guinea, M. Sandoval-Denis, P. Escribano, E. Bouza et J. Guarro
Aureobasidium iranianumINS1 (1)YINS1KY781746KY781747101 (0.6)
Arzanlou et Khodaei
Aureobasidium

melanogenum (Hermanides-Nijhof) Zalar, Gostincar et Gunde-Cim.
INS8 (2)2Y211

2Y215A
KY781748

KY781750
KY781749

KY781751
022 (1.2)
Aureobasidium pullulansINS8 (1)2Y101KY781752011 (0.6)
(de Bary) G. Arnaud
Zalaria obscura Visagie, Z. Humphries et SeifertINS3 (2)

INS7 (1)

INS8 (1)
INY20

INY28

2Y102
KY781753

KY781755

KY781757
KY781754

KY781756

KY781758












044 (2.5)
Candida metapsilosis Tavanti, A. Davidson, Gow, M. Maiden et OddsINS7 (1)INY21KY695002011 (0.6)
Candida orthopsilosis Tavanti, A. Davidson, Gow, M. Maiden et OddsINS8 (1)2Y191A011 (0.6)
Candida parapsilosis (Ashford) Langeron et TaliceINS8 (1)2Y213KY694996KY695003011 (0.6)
Cladosporium cladosporioides(Fresen.) G.A. de VriesINS2 (2)INM21KY781759KY781760A-MF084386202 (1.3)
INM29
Cladosporium halotoleransZalar, de Hoog et Gunde-Cim.INS1 (3)

INS2 (1)

INS5 (1)
INM1 INM14KY781786

KY781788
KY781787

KY781789




A-MF084398

A-MF084399
415 (3.2)
Cladosporium limoniforme

Bensch, Crous et U. Braun
INS1 (2)

INS2 (1)

INS4 (1)

INS5 (1)

INS6 (1)

INS7 (2)

INS8 (1)
INM3

INM6

2INM1
KY781780

KY781782

KY781784
KY781781

KY781783

KY781785












A-MF084397
369 (5.7)
Cladosporium spp.aINS1 (2)INM18KY781769KY781770A-MF084391617 (4.4)
INM24KY781774KY781775A-MF084394
INS2 (3)INM23KY781773A-MF084393
INM37KY781776KY781777A-MF084395
INS3 (2)INM34KY781771KY781772A-MF084392
2INM9KY781778KY781779A-MF084396
Cladosporium tenuissimum CookeINS1 (5)INM8

INM12
KY781761

KY781763
KY781762

KY781764




A-MF084387

A-MF084388
505 (3.2)
Cladosporium xantochromaticum Sandoval-Denis, Gené et CanoINS1 (2)

INS2 (2)
INM11

INM16
KY781765

KY781767
KY781766

KY781768




A-MF084389

A-MF084390
404 (2.5)
Debaryomyces hansenii

(Zopf) Lodder et Kreger
INS2 (1)YINM36BKY694997KY695004101 (0.6)
Debaryomyces nepalensisINS1 (2)

INS2 (3)
YINS3KY694998KY695005505 (3.2)
Goto et Sugiy
Fusarium chlamydosporum Wollenw. et ReinkingINS3 (1)2INM10BKY781790KY781791011 (0.6)
Hyphozyma spp.aINS6 (2)INY32CKY695000KY695007022 (1.3)
INY36KY695001KY695008
Hortaea werneckii (Horta) Nishim. et MiyajiINS8 (5)2Y193BKY781792KY781793055 (3.2)
2Y210KY781794KY781795
Trichoderma placentula JaklitschINS6 (1)

INS7 (2)
INY33, INY10BKY781797033 (1.9)
KY781796
Knufia petricolaINS8 (1)2Y215BKY781798KY781799011 (0.6)
(Wollenz. et de Hoog) Gorbushina et Gueidan
Penicillium oxalicumINS5 (1)2INM6AKY781804KY781805C-MF084384022 (1.3)
Currie et ThomBT-MF084379
INS8 (1)2M110AKY781806KY781807C-MF084385
BT-MF084380
Penicillium chrysogenumThomINS3 (1)

INS4 (1)
2INM8KY781802KY781803C-MF084383022 (1.3)
2INM4KY781800KY781801BT-MF084378

C-MF084382

BT-MF084377
Sarocladium bacillisporumINS1 (1)YINS5KY781808101 (0.6)
(Onions et G.L. Barron) Summerb.
BasidiomycetesKondoa spp.aINS8 (4)2Y188

2Y189

2Y209

2Y214
KY744105



KY744106

KY744107
KY744120044 (2.5)
KY744121
KY744122
KY744123
Naganishia albida (Saito) X.Z. Liu, F.Y. Bai, M. Groenew. et BoekhoutINS7 (1)INY12KY744108KY744124011 (0.6)
Naganishia albidosimilis (Vishniac et Kurtzman) X.Z. Liu, F.Y. Bai, M. Groenew. et BoekhoutINS3 (1)

INS6 (2)

INS7 (1)
INY14

INY25
KY744109

KY744110
KY744125

KY744126






044 (2.5)
Naganishia qatarensisa R. Fotedar, A. Kolecka, T. Boekhout, J.W. Fell A. Anand, A. Al Malaki, A. Zeyara, M. Al Marri.INS6 (1)

INS7 (1)
INY13

INY29
KY744111

MG852088
KY744127

KY744128






022 (1.3)
Papiliotrema laurentiiINS6 (1)INY35KY744112KY744129011 (0.6)
(Kuff.) X.Z. Liu, F.Y. Bai, M. Groenew. et Boekhout
Rhodotorula diobovata (S.Y. Newell et I.L. Hunter) Q.M. Wang, F.Y. Bai, M. Groenew. et T. Boekhout.INS6 (1)INY34KY744130011 (0.6)
Rhodotorula mucilaginosa(A. Jörg.) F.C. HarrisonINS3 (6)

INS6 (18)

INS7(23)
INY2

INY6

KY744113

KY744114

KY744131

KY744132













04747 (29.6)
Symmetrospora marina (Phaff, Mrak et O.B. Williams) Q.M. Wang, F.Y. Bai, M. Groenew. et BoekhoutINS8 (12)2Y186 2Y190AKY744115

KY744116
KY744133

KY744134






01212 (7.6)
Symmetrospora spp.aINS8 (1)2Y207KY744117KY744135011 (0.6)
Tremellales sp.INS2 (1)INM28KY781809KY781810101 (0.6)
Total isolates (number)44115159 (100)
  1. aStrains preliminarily identified at the genus level on the basis of the LSU, ITS, TEf1, Gapdh 1 and 2 sequence analyses.

  2. bStrains sequenced and sequences deposited in GenBank.

Results

The physicochemical characteristics of the water samples are summarized in Table 1. The range of pH and salinity for the coastal sites, i.e. INS1-INS7, was similar, whereas INS8 showed a lower pH and salinity. During the winter and summer seasons the seawater temperatures varied between 24–25°C and 30–32°C, respectively (Table 1).

The total average yeast and filamentous fungus counts for each sampling site are shown in Table 1. The average number of isolates (including both yeasts and filamentous fungi) ranged from 15 to 920 CFU l−1 (Table 1), with the highest values corresponding to the sites INS7, INS6 and INS2 that were coastal zones in the vicinity of salt pans.

One hundred and fifty-nine isolates (yeasts and filamentous fungi) were obtained from the water samples (Table 2). Seventy-two percent of the isolates (115/159) were recovered during the summer season and 28% (44/159) during the winter season. Selected sequences of the fungal isolates were deposited in the GenBank database (www.ncbi.nlm.nih.gov.), and their GenBank accession numbers are listed in Table 2. Taxonomic assignments of yeasts were done according to the published literature (Kurtzman et al. 2011, Liu et al. 2015a,b, Wang et al. 2015a,b). Twenty-two strains (22/159; 13.8%) in six genera [Alternaria spp. (6 isolates), Cladosporium spp. (7 isolates), Hyphozyma spp. (2 isolates), Kondoa spp. (4 isolates), Naganishia qatarensis (2 isolates), Symmetrospora sp. (1 isolate)] could not be identified to the species level on the basis of the D1/D2 domains of the LSU and ITS rDNA. These strains may represent novel species (Table 2, Figures 24). The novel species of Naganishia Goto has been described as N. qatarensis by Fotedar et al. (2018). Formal taxonomic descriptions of the remaining novel species are in progress.

Figure 2: Maximum likelihood multi-gene tree based on ITS, gapdh and tef1 sequences of Alternaria sp. nov. (marked in bold), including all reference isolates from Alternaria sect. Chalastospora and the closest relatives from Alternaria sect. Infectoriae with Alternaria penicillata CBS 116607 (Alternaria sect. Crivellia) as outgroup.The RAx ML bootstrap support values ≥75% (BS) and Bayesian posterior probabilities ≥0.95 (PP) are given at the nodes. Thickened lines indicate a BS of 100% and a PP of 1.0. The GenBank accession numbers of the studied sequences are given in brackets [ITS; gapdh; tef1] after the species names.
Figure 2:

Maximum likelihood multi-gene tree based on ITS, gapdh and tef1 sequences of Alternaria sp. nov. (marked in bold), including all reference isolates from Alternaria sect. Chalastospora and the closest relatives from Alternaria sect. Infectoriae with Alternaria penicillata CBS 116607 (Alternaria sect. Crivellia) as outgroup.

The RAx ML bootstrap support values ≥75% (BS) and Bayesian posterior probabilities ≥0.95 (PP) are given at the nodes. Thickened lines indicate a BS of 100% and a PP of 1.0. The GenBank accession numbers of the studied sequences are given in brackets [ITS; gapdh; tef1] after the species names.

Figure 3: Phylogenetic tree showing the placement of Kondoa sp. nov. (marked in bold) and some closely related species based on the analysis of the combined ITS region and D1/D2 domains of LSU rDNA.Type strains indicated by superscript T. Sequences not generated during this study were obtained from GenBank (accession numbers are shown in parentheses). The tree was constructed by maximum-likelihood method based on the Kimura 2-parameter model using MEGA6 software. Numbers on branches represent bootstrap values from 1000 replicates. Scale bar represents 0.05 substitutions per nucleotide position.
Figure 3:

Phylogenetic tree showing the placement of Kondoa sp. nov. (marked in bold) and some closely related species based on the analysis of the combined ITS region and D1/D2 domains of LSU rDNA.

Type strains indicated by superscript T. Sequences not generated during this study were obtained from GenBank (accession numbers are shown in parentheses). The tree was constructed by maximum-likelihood method based on the Kimura 2-parameter model using MEGA6 software. Numbers on branches represent bootstrap values from 1000 replicates. Scale bar represents 0.05 substitutions per nucleotide position.

Figure 4: Phylogenetic tree showing the placement of Naganishia qatarensis (marked in bold) and some closely related species based on the analysis of the combined ITS region and D1/D2 domains of LSU rDNA.Type strains indicated by superscript T. Sequences not generated during this study were obtained from GenBank (accession numbers are shown in parentheses). The tree was constructed by maximum-likelihood method based on the Kimura 2-parameter model using MEGA6 software. Numbers on branches represent bootstrap values from 1000 replicates. Scale bar represents 0.02 substitutions per nucleotide position (Fotedar et al. 2018).
Figure 4:

Phylogenetic tree showing the placement of Naganishia qatarensis (marked in bold) and some closely related species based on the analysis of the combined ITS region and D1/D2 domains of LSU rDNA.

Type strains indicated by superscript T. Sequences not generated during this study were obtained from GenBank (accession numbers are shown in parentheses). The tree was constructed by maximum-likelihood method based on the Kimura 2-parameter model using MEGA6 software. Numbers on branches represent bootstrap values from 1000 replicates. Scale bar represents 0.02 substitutions per nucleotide position (Fotedar et al. 2018).

Rhodotorula mucilaginosa, a halo- and psychrotolerant red-pigmented yeast species, represented almost 30% (47/159 isolates) of all fungal isolates and was obtained at a sampling depth of 0.5 m from three sites (INS3, INS6, INS7) with a salinity of 72–74 and temperatures ranging from 30 to 32°C.

The majority (40.2%; 64/159 isolates) of the fungal isolates consisted of melanized fungi belonging to the genera Alternaria, Aureobasidium, Cladosporium, Hortaea, Knufia L.J. Hutchison et Unter. and Zalaria Visagie, Z. Humphries et Seifert. These melanized fungi were isolated from all sites sampled. Among the melanized fungi, Cladosporium species (20%; 32/159 isolates) were most commonly isolated, followed by Alternaria species (11.3%; 18/159 isolates).

Discussion

The Inland Sea of Qatar is a unique ecosystem with extreme environmental conditions. During sampling we encountered temperatures of 24–32°C, below average rainfall (winter, 0.1 mm; summer, 0 mm) and high salinities (57–75). For sites INS1-7, no trend was observed between the fungal isolates obtained and the environmental factors measured, such as temperature, pH, salinity, and season of isolation. Sites INS7, INS6 and INS2 (approx. 2–3 km apart from each other) located at the east side had the highest fungal counts, and this could be related to the proximity of these sites to the coastal zone, and the recreational area and camps. Sites INS4, INS5, and INS3 showed low fungal counts that could be due to the pristine nature of these sites with absence of human activity. INS8 (salinity 57, pH 7.9, depth 2.5 m) showed a higher species diversity (Table 2), when compared to the other sites (salinity >70, pH 8.02–8.35 and 0.5 m depth).

The yeast communities in Inland Sea were similar to those reported from other hypersaline environments (Coelho et al. 2010, Yurkov et al. 2011, 2012, França et al. 2016, Mokhtarnejad et al. 2016). Several studies reported a predominance of basidiomycetous fungi in hypersaline aquatic environments (Libkind et al. 2003, Butinar et al. 2005a, de Garcia et al. 2007, Brandao et al. 2011, Mokhtarnejad et al. 2016), but in our study ascomycetous and basidiomycetous yeasts occurred almost with equal abundance (Ascomycota 52.8%; Basidiomycota 47.2%). Some psychrotolerant yeasts, such as species of Naganishia, Rhodotorula F.C. Harrison and Debaryomyces Lodder et Kreger-van Rij ex Kreger-van Rij, were isolated in this study. These yeast species have also been reported from cold ecosystems, e.g. the Calderone glacier, Alpine glaciers and high Arctic glaciers (Butinar et al. 2007, Turchetti et al. 2008, 2013, Branda et al. 2010, Zalar and Gunde-Cimerman 2014).

Rhodotorula mucilaginosa was the most frequently isolated yeast species (29.5% of the total isolates) from the sites adjacent to the salt pans (INS6 and INS7), which were impacted by human activity, due to their proximity to the recreational camps. Our results are in accordance with other reports highlighting R. mucilaginosa as the dominant yeast in hypersaline environments with a wide range of salinities and pH (Lahav et al. 2002, Burgard et al. 2010). Symmetrospora marina was the second most dominant yeast species with 12 isolates and was isolated from the pelagic site INS8 (salinity 57, 32°C). This species was reported from an aquatic environment in Japan (Urano et al. 2001), from the surface washing of shrimp (Sampaio 2011), and the Florida Everglades (Fell et al. 2011). This is the first report of S. marina from a hypersaline environment.

Naganishia albidosimilis (formerly Cryptococcus albidosimilis Vishniac et Kurtzman), Naganishia albida and Naganishia qatarensis (Fotedar et al. 2018) were isolated from three sites with temperatures ranging from 30 to 32°C. Naganishia albidosimilis was reported from hypersaline lakes in Iran (Mokhtarnejad et al. 2016). Strains of Kondoa species that belong to the Agaricostilbum clade of Pucciniomycotina (Fonseca et al. 2000, Sampaio 2011, Wang et al. 2015a) were isolated in low frequencies from INS8 only. The Qatari isolates are related to other marine Kondoa species, such as K. aeria Á. Fonseca, J.P. Samp. et Fell, and K. malvinella (Fell et I. L. Hunter) Y. Yamada, Nakagawa et I. Banno, on the basis of the phylogenetic analyses, but may present an undescribed species (Figure 3). Kondoa aeria is known from terrestrial habitats (Fonseca et al. 2000), waters of the North Island of New Zealand (Francis et al. 2016), and deep sea sediments of Sagami Bay, Japan (Minegishi et al. 2006). To our knowledge, this is the first report of the isolation of Kondoa spp. from a hypersaline lagoon.

Species of the genus Debaryomyces, i.e. D. hansenii and D. nepalensi, were recovered during the winter seasons from two sites with a salinity range of 73–75, a depth of 0.5 m and a temperature of 24–25°C. Debaryomyces hansenii has a broad salinity tolerance (Yadav and Loper 1999) and the isolation of this halotolerant species has been documented from oceanic and aquatic environments (Hagler and Ahearn 1987, Nagahama 2006, Coelho et al. 2010), high salinity coastal and oceanic environments (Almeida 2005), and natural hypersaline lakes that are exposed to seasonal low temperatures (Butinar et al. 2005a).

Candida metapsilosis and C. orthoparapsilosis were isolated in low numbers (2/159 isolates). A single isolate of Candida parapsilosis was cultured from INS8. This species was previously reported from aquatic and hypersaline environments (Soares et al. 1997, Butinar et al. 2005a, Hagler 2006, Nagahama 2006).

The largest group (40.2%; 64/159 isolates) of the filamentous fungal isolates belonged to the melanized fungal genera Alternaria, Aureobasidium, Cladosporium, Hortaea, Knufia and Zalaria. Cladosporium species (20%; 32/159 isolates) were the most dominant, followed by Alternaria species (11.3%; 18/159 isolates). These melanized isolates were recovered from different sampling sites (with varying salinities and temperatures) across the Inland Sea suggesting a wide adaptability and ability to survive in various environments of high salinities and high temperatures. The majority of these black fungi (75%; 48/64 isolates) were isolated from the coastal sites (INS1-7) near the vicinity of salt pans, indicating that they are able to grow in hypersaline waters and this observation is in agreement with those made elsewhere (Gunde-Cimerman et al. 2000, Nazareth et al. 2012).

Cladosporium was the most species-rich genus and was present in almost all sampling sites with high salinity of 72–75, and this observation is in accordance with reports of Cladosporium occurring in salterns in Slovenia and Puerto Rico (Gunde-Cimerman et al. 2000, Cantrell et al. 2006), Great Salt Lake, Utah (Cronin and Post 1977), sabkhas (coastal salt flats) and salterns (Gunde-Cimerman et al. 1997, Butinar et al. 2005b, Cantrell et al. 2006, Al-Musallam et al. 2011), deserts, and salty environments (Kis-Papo et al. 2001, Grishkan et al. 2003, Conley et al. 2006, Smolyanyuk and Bilanenko 2011). Several studies have shown that species of Alternaria are predominant in deserts and salty environments (Gunde-Cimerman et al. 2000, Kis-Papo et al. 2001, Conley et al. 2006, Smolyanyuk and Bilanenko 2011). These fungi produce thick-walled and strongly melanized spores, which are important to protect against UVR and increase desiccation tolerance (Sterflinger et al. 2012).

Hortaea werneckii, another melanized fungus, was recovered from the water samples collected from the deep water site INS8 (2.5 m depth; salinity 57.3). This yeast-like fungus was previously reported from drying salty pools (de Hoog and van den Ende 1992), hypersaline waters in Europe (Gunde-Cimerman et al. 2000, Plemenitas et al. 2008), saline water of crystallization ponds (Gunde-Cimerman et al. 2003) and solar salterns in Puerto Rico (Diaz-Munoz and Montalvo-Rodriguez 2004), suggesting that hypersaline water is an ecological habitat of this species (Gunde-Cimerman et al. 2000, Kogej et al. 2005). Hortaea werneckii thrives in extreme environments characterized by scarce nutrients, low oxygen tension, high temperature, high UVR, high osmotic stress, as well as a mixture of these conditions (Sterflinger 2006). In our study we did not isolate this species from sites near the salt pans, but in contrast H. werneckii was isolated from the deeper water samples of INS8.

Based on the D1/D2 LSU and ITS rDNA sequence analyses, 13.8% (22/159) of the isolates, presumably novel species, were preliminarily identified to the genus level. These species include Alternaria spp., Cladosporium spp., Hyphozyma spp., Kondoa spp., Naganishia qatarensis (Fotedar et al. 2018) and Symmetrospora sp. (Table 2; Figures 24). Taxonomically undefined yeast and filamentous fungi have been isolated in various extreme environments, including glaciers (Butinar et al. 2007, Turchetti et al. 2013), alkaline soils (Grum-Grzhimaylo et al. 2013, 2016), and saline as well as hypersaline environments (Buchalo et al. 1998, Jones and Abdel-Wahab 2005, Zalar et al. 2007, Al-Musallam et al. 2011).

This is the first report highlighting the isolation of halotolerant fungi from hypersaline waters of the Inland Sea in Qatar. Due to the rising sea levels this study will be useful as a reference for future monitoring studies in Qatar.

About the authors

Rashmi Fotedar

Rashmi Fotedar works as an expert, Department of Genetic Engineering, Ministry of Municipality and Environment, Doha, Qatar. She earned her Master’s in molecular biology from University of Technology, Sydney, Australia and her PhD from All India Institute of Medical Sciences New Delhi, India. Her research interests include marine microbiology and molecular characterization of fungi and bacteria from environment and humans.

Anna Kolecka

Anna Kolecka is a researcher at Westerdijk Fungal Biodiversity Institute, Utrecht, The Netherlands. From 2010 to 2017 she was working as a postdoc in the Yeast Research Group, led by Teun Boekhout. During those years she extensively studied the implementation of MALDI-TOF mass spectrometry for yeast identification and DNA-based molecular approaches for fungal taxonomy. She further explored the application of proteomics for fungal discrimination, recently by using high resolution accurate mass-mass spectrometry (HRAM-MS). She completed her MSc Eng studies in environmental protection at Gdansk University of Technology, Poland in 2005 and later received her PhD in microbiology at Comenius University, Bratislava, Slovakia in 2011.

Teun Boekhout

Teun Boekhout, works as a principal investigator at Westerdijk Fungal Biodiversity Institute (previously known as CBS Fungal Biodiversity Centre, CBS-KNAW), Utrecht, and Institute of Biodiversity and Ecosystem Dynamics, University of Amsterdam, Amsterdam, The Netherlands. He studied biology in Utrecht where he also graduated. Since 1982 he is working in mycology. In 2018 he was elected Fellow of the American Academy of Microbiology. In 2011 he was editor of The yeasts, a taxonomic study and presently he is editor in chief of The yeasts, an open access platform on yeast diversity.

Jack W. Fell

Jack W. Fell, PhD, Professor Emeritus, University of Miami. Chairman, Science Advisory Board, Bahamas Marine EcoCentre. Dr Fell a marine scientist, with his colleagues and students, studied microbial ecology from the tropics to Antarctic, mangroves to deep sea. His lab research included basidiomycetous yeast mating genetics, he was a pioneer in basidiomycete molecular phylogeny and developed molecular probes for rapid species detection of marine microbes and human pathogens.

Ameena Al-Malki

Ameena Al-Malki works as a specialist in Genetic Engineering Department, Biotechnology Centre, Ministry of Environment, Doha, Qatar. She is involved in studies related to isolation and molecular identification of microorganism from marine environment, detection of GMOs in agricultural and food products. Her fields of interest include the molecular characterization of bacteria and fungi from environmental samples.

Aisha Zeyara

Aisha Zeyara works as an expert in Department of Genetic Resources, Ministry of Municipality and Environment, Doha, Qatar. She has a degree in microbiology and molecular biology from Qatar University, Doha, Qatar. Aisha is a molecular microbiologist and has been involved in research studies including isolation, identification and characterization of microbial pathogens from Qatari marine environment.

Masoud Al Marri

Masoud Al Marri, works as Director, Agricultural Research Department, Ministry of Municipality and Environment, Doha, Qatar. He earned his Master’s degree from University of Florida, USA and has been involved in research projects related to marine environment and environmental monitoring of marine, ground water and air in Qatar.

Acknowledgments

This research was supported by research grant NPRP 6-647-1-127 from the Qatar National Research Fund, a member of Qatar Foundation to R. Fotedar, (Ministry of Environment, Qatar), T. Boekhout (Westerdijk Fungal Biodiversity Institute Uppsalalaan, Utrecht, Netherlands) and J.W. Fell (Rosenstiel School of Marine and Atmospheric Sciences, University of Miami, Key Biscayne, FL, USA). The authors are solely responsible for the content of the manuscript.

The publication of this article was funded by the Qatar National Library.

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Received: 2018-05-01
Accepted: 2018-10-09
Published Online: 2018-11-17
Published in Print: 2018-12-19

©2019 Rashmi Fotedar et al., published by De Gruyter, Berlin/Boston

This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 License.

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