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Studies on aquatic fungi in Dikarya: a review of the literature from Southern Cone of South America

Abstract

A bibliographic analysis was carried out to update the state of knowledge about aquatic fungi belonging to the subkingdom Dikarya in the Southern Cone of South America. The exhaustive search resulted in 38 articles reported. These papers correspond to those on taxonomic, ecological and biogeographic topics and include studies from lotic environments of the temperate ecoregions of Chile and Argentina. A total of 325 aquatic fungal taxa were reported, of which 318 belong to the phylum Ascomycota and 7 to the phylum Basidiomycota. According to the subgroups of these aquatic fungi 17 taxa were aero-aquatic, 199 facultative and 109 Ingoldian fungi. Regarding the methodologies, in these studies the information was obtained mainly by using lignocellulosic substrates such as leaf litter and wood as fungal source and wet chamber traditional working technique. However, more studies are still needed using other few-reported perspectives for the region such as ecological and molecular approaches as well as analyses of water environments belonging to unexplored biomes. This information can contribute to a better understanding of aquatic fungal communities and their role in ecosystems of the Southern Cone of South America.

Key words
Biogeography; freshwater environments; fungal source; hyphomycetes; Ingoldian fungi

INTRODUCTION

Aquatic fungi are a group of organisms whose life cycle takes place completely or partly on aquatic habitats (Grossart et al. 2019GROSSART HP, VAN DEN WYNGAERT S, KAGAMI M, WURZBACHER C, CUNLIFFE M & ROJAS-JIMENEZ K. 2019. Fungi in aquatic ecosystems. Nat Rev Microbio 17(6): 339-354.). They participate in different ecological processes and are key elements in the decomposition of organic material, both autochthonous and allochthonous (Goh & Hyde 1996GOH TK & HYDE KD. 1996. Biodiversity of freshwater fungi. J Ind Microbiol 17(5-6): 328-345., Romaní et al. 2009ROMANÍ AM, ARTIGAS J, CAMACHO A, GRAÇA MAS & PASCOAL C. 2009. La biota de los ríos: los microorganismos heterotróficos. In: ELOSEGI A, SABATER S. (Eds), Conceptos y Técnicas en Ecología Fluvial, Fundación BBVA: España, p. 169-218.). Phylogenetically, these fungi are represented by different phyla, mainly the Ascomycota (Webster 1992WEBSTER J. 1992. Anamorph-teleomorph relationships. In The ecology of aquatic hyphomycetes. Springer, Berlin: Heidelberg, p. 99-117.). From an ecological and morphological perspective, they are classified into three categories: Ingoldian (also called aquatic hyphomycetes), aero-aquatic (Beverwijk 1951BEVERWIJK VAN AL. 1951. Zalewski’s ‘Clathrosphaera spirifera’. Trans Brit Mycol Soc 34(3): 280-290.) and facultative (Shearer et al. 2007SHEARER CA ET AL. 2007. Fungal biodiversity in aquatic habitats. Biodivers Conserv 16(1): 49-67., Goh & Hyde 1996GOH TK & HYDE KD. 1996. Biodiversity of freshwater fungi. J Ind Microbiol 17(5-6): 328-345., Tsui et al. 2016TSUI CKM, BASCHIEN C & GOH TK. 2016. Biology and ecology of freshwater fungi. En Biology of Microfungi. In: LI DW (Eds), Springer: Cham, p. 285-313.); each group being characterized mainly by the morphology of its spores (a feature that has a close relationship with the environments where they live) and type of sporulation (Tsui et al. 2016TSUI CKM, BASCHIEN C & GOH TK. 2016. Biology and ecology of freshwater fungi. En Biology of Microfungi. In: LI DW (Eds), Springer: Cham, p. 285-313.).

Several studies indicate that the main factors that modulate fungal diversity in aquatic ecosystems are temperature, turbidity, nutrient concentration, quality of organic matter, spore production, and competition with other fungi in freshwater environments (Bärlocher et al. 2011BÄRLOCHER F, STEWART M & RYDER DS. 2011. Analyzing aquatic fungal communities in Australia: impacts of sample incubation and geographic distance of streams. Czech Mycol 63: 113-132., Graca et al. 2016GRAÇA MAS, HYDE K & CHAUVET E. 2016. Aquatic hyphomycetes and litter decomposition in tropical–subtropical low order streams. Fungal Ecol 19: 182-189., Shearer et al. 2007SHEARER CA ET AL. 2007. Fungal biodiversity in aquatic habitats. Biodivers Conserv 16(1): 49-67., Kominoski et al. 2015KOMINOSKI JS, ROSEMOND AD, BENSTEAD JP, GULIS V, MAERS JC & MANNING DW. 2015. Low-to-moderate nitrogen and phosphorus concentrations accelerate microbially driven litter breakdown rates. Ecol Monogr 25(3): 856-865.).

Recent estimations report more than 3,000 species of aquatic fungi worldwide, taking into account the main fungal groups such as the phyla Ascomycota, Blastocladiomycota and Chytridiomycota (Shearer et al. 2007SHEARER CA ET AL. 2007. Fungal biodiversity in aquatic habitats. Biodivers Conserv 16(1): 49-67., Abdel-Aziz 2008ABDEL-AZIZ FA. 2008. Diversity of aquatic fungi on Phragmites australis at Lake Manzala, Egypt. Sydowia 60(1): 1-14., Tsui et al. 2016TSUI CKM, BASCHIEN C & GOH TK. 2016. Biology and ecology of freshwater fungi. En Biology of Microfungi. In: LI DW (Eds), Springer: Cham, p. 285-313.). However, when the richness of asexual aquatic taxa belonging to the sub-kingdom Dikarya (phyla Ascomycota and Basidiomycota), frequently found in freshwater environments, is quantified, about 335 correspond to Ingoldian forms (Duarte et al. 2016DUARTE S, BÄRLOCHER F, PASCOAL C & CÁSSIO F. 2016. Biogeography of aquatic hyphomycetes: current knowledge and future perspectives. Fungal Ecol 19: 169-181), 90 to aero-aquatic and 405 to facultative ones (Shearer et al. 2007SHEARER CA ET AL. 2007. Fungal biodiversity in aquatic habitats. Biodivers Conserv 16(1): 49-67.). Specifically, current data show that up to 128 of the Ingoldian fungal species have been recognized in South America (Schoenlein-Crusius & Grandi 2003SCHOENLEIN-CRUSIUS IH & GRANDI RAP. 2003. The diversity of aquatic hyphomycetes in South America. Braz J Microbiol 34(3): 183-193., Fiuza et al. 2017FIUZA PO, PÉREZ TC, GULIS V & GUSMAO LF. 2017. Ingoldian fungi of Brazil: some new records and a review including a checklist and a key. Phytotaxa 306(3): 171-200.).

According to Duarte et al. (2016)DUARTE S, BÄRLOCHER F, PASCOAL C & CÁSSIO F. 2016. Biogeography of aquatic hyphomycetes: current knowledge and future perspectives. Fungal Ecol 19: 169-181 the greatest diversity of Ingoldian fungi has been reported for temperate regions. Considering that temperate climate prevails in the Southern Cone of South America, it is important to have an updated review of the reported taxa. This area of the American continent, which extends from the Tropic of Capricornio to Cabo de Hornos (including Argentina, Chile and Uruguay) is potentially favourable to host an important diversity of aquatic fungi, exhibiting a variety of biomes and landscapes. In addition, hydrologically, it a wide range of freshwater habitats, rivers of different orders, lakes, lagoons, peatlands, among other wetlands.

The aim of this review was to explore through information from different bibliographic sources:

I. Biogeographic distribution of taxa in the Southern Cone of South America.

II. Habitats where they were found.

III. Methodology used for their study.

IV. Substrates used.

Despite that reviews on aquatic fungi have been carried out in South America, with emphasis on data from Brazil (Schoenlein-Crusius & Grandi 2003SCHOENLEIN-CRUSIUS IH & GRANDI RAP. 2003. The diversity of aquatic hyphomycetes in South America. Braz J Microbiol 34(3): 183-193., Fiuza et al. 2017FIUZA PO, PÉREZ TC, GULIS V & GUSMAO LF. 2017. Ingoldian fungi of Brazil: some new records and a review including a checklist and a key. Phytotaxa 306(3): 171-200.), the aim of this study was to obtain a current state of knowledge on aquatic fungi in the Southern Cone of South America, which is still little explored in aquatic mycology, to have fundamental information and, therefore, to project future studies that can contribute to expand existing information.

MATERIALS AND METHODS

The search for journal articles dealing with aquatic fungi reported from the Southern Cone of South America was carried out using “Google scholar” (https://scholar.google.com), “Scopus” (https://www.scopus.com), “Scielo” (https://scielo.org/es),“Science direct” (https://www.sciencedirect.com/), and “Dimensions” (https://app.dimensions.ai/) from December 2019 to January 2020. Each database was screened using key words such as “fungi”, “freshwater”, “Ingoldian”, “hyphomycetes”, “aquatic”, “South America” or a combination of these. The bibliographic analysis was carried out taking into account the following information: taxonomic, ecological and biogeographic features, methodologies used for their study, as well as the type of substrate and the aquatic environment where the fungi were found. Nomenclature of fungi was validated through the Mycobank website (http://www.mycobank.org) and for some taxa following recent publications (Johnston et al. 2019JOHNSTON PR ET AL. 2019. A multigene phylogeny toward a new phylogenetic classification of Leotiomycetes. IMA Fungus 10(1): 1-22., Anderson & Marvanová 2020ANDERSON JL & MARVANOVÁ L. 2020. Broad geographical and ecological diversity from similar genomic toolkits in the ascomycete genus Tetracladium. BioRxivin press., Johnston & Baschien 2020JOHNSTON PR & BASCHIEN C. 2020. Tricladiaceae fam. nov. (Helotiales, Leotiomycetes). FUSE 6: 233-242.).

RESULTS AND DISCUSSION

Out of the 38 articles reported, studies about taxonomical features (76 %), followed by those of ecological analysis, which have been considered to be only of local relevance, were found from the database consulted (Supplementary Material-Table SI). The first published paper was carried out in 1970 analyzing freshwater fungi from Chile (Lindquist 1970LINDQUIST JC. 1970. Hughesinia, nuevo género de hifomicetes (Demaciácea). Bol Soc Argent Bot 13: 53.), eight years after the first report for South America by Nilsson 1962NILSSON S. 1962. Some aquatic hyphomycetes from South America. Svensk bot. Tidskr 56: 351-361. on Venezuela. The largest amount of data about freshwater fungi from the Southern Cone of South America were between the 1980s and 1990s, with information corresponding to Argentina and Chile. (Figure 1.)

Figure 1
Timeline of studies published in each decade on the Southern Cone of South America (Table SI).

Regarding the distribution of references, we have observed that there are only reports from five bio-geographic provinces (Figure 2), of the 20 ones recognized in the Southern Cone of South America, of which Pampa and Bosques Valdivianos have 49% and 24%, respectively. Considering that both ecoregions correspond to temperate climate, this information is in agreement with that of the Northern Hemisphere (Europe and east of United States), where the research of these fungi is greater compared to tropical areas (Jabiol et al. 2013JABIOL J, BRUDER A, GESSNER MO, MAKKONEN M, ET AL. 2013. Diversity patterns of leaf-associated aquatic hyphomycetes along a broad latitudinal gradient. Fungal Ecol 6(5): 439-448., Duarte et al. 2016DUARTE S, BÄRLOCHER F, PASCOAL C & CÁSSIO F. 2016. Biogeography of aquatic hyphomycetes: current knowledge and future perspectives. Fungal Ecol 19: 169-181). On the other hand, the analysis of environments in which the studies were conducted reveals that lotic habitats have been more explored (76%) than lentic ones, which have also been less explored worldwide (Descals & Moralejo 2001DESCALS E & MORALEJO E. 2001. Water and asexual reproduction in the ingoldian fungi. Bot Complut 25: 13-71., Wurzbacher et al. 2010WURZBACHER CM, BÄRLOCHER F & GROSSART HP. 2010. Fungi in lake ecosystems. Aquat Microb Ecol 59(2): 125-149.).

Figure 2
Map of the Southern Cone of South America (shaded area), showing the biogeographic provinces (Morrone 2001MORRONE JJ. 2001. Biogeografía de América Latina y el Caribe. M&T-Manuales & Tesis SEA, Sociedad Entomológica Aragonesa. Zaragoza 3: 152.) where studies on aquatic fungi (stars) were recorded. Additionally, the taxa reported in each provinces biogeographic were indicated in Table SII.

Analyzing the fungal richness, a total of 325 taxa were reported, being Aegerita candida Pers., Fibulotaeniella sp., Papiliotrema laurentii (Kuff.) Xin Zhan Liu, F.Y. Bai, M. Groenew. & Boekhout, P. pseudoalba (Nakase & M. Suzuki) Xin Zhan Liu, F.Y. Bai, M.Groenew. & Boekhout, Rhodotorula mucilaginosa (A. Jörg.) F.C. Harrison, Tausonia pullulans (Lindner) Xin Zhan Liu, F.Y. Bai, M. Groenew. & Boekhout and Tricladiomyces geniculatus Nawawi & Kuthub. the only representatives of the Basidiomycota and the others belonged to the Ascomycota (Table SII). Only Alatospora acuminata Ingold, Tetracladium marchalianum De Wild., and T. setigerum (Grove) Ingold were reported in all provinces analyzed (Table SII).

Alatospora acuminata was also reported in Duarte et al. (2016)DUARTE S, BÄRLOCHER F, PASCOAL C & CÁSSIO F. 2016. Biogeography of aquatic hyphomycetes: current knowledge and future perspectives. Fungal Ecol 19: 169-181 biogeographic studies in all the regions analyzed worldwide. Of the total species reported for the Southern Cone of South America, 199 corresponded to facultative, followed by 109 Ingoldian and only 17 to aero-aquatic fungi. These Ingoldian fungi represent 32 % of the known species worldwide. This suggests the need of more studies on this aquatic fungal group, since it is known that they play a key role in litter decomposition (Gessner & Chauvet 1994GESSNER MO & CHAUVET E. 1994. Importance of stream microfungi in controlling breakdown rates of leaf litter. Ecology 75(6): 1807-1817., Graça & Ferreira 1995GRAÇA MAS & FERREIRA RCF. 1995. The ability of selected aquatic hyphomycetes and terrestrial fungi to decompose leaves in freshwater. SYDOWIA-HORN 47: 167-222., Gulis & Suberkropp 2003GULIS V & SUBERKROPP K. 2003. Interactions between stream fungi and bacteria associated with decomposing leaf litter at different levels of nutrient availability. Aquat Microb Ecol 3(2): 149-157.) and as pollution bioindicators in freshwater ecosystems (Solé et al. 2008SOLÉ M, FETZER I, WENNRICH R, SRIDHAR KR, HARMS H & KRAUSS G. 2008. Aquatic hyphomycete communities as potential bioindicators for assessing anthropogenic stress. Sci Total Environ 389(2-3): 557-565., Dubey 2016DUBEY A. 2016. Aquatic hyphomycetes communities occur as potential bioindicators of water quality. IJAR 2(8): 778-780., Tarda et al. 2019TARDA AS, SAPARRAT MCN & GÓMEZ N. 2019. Assemblage of dematiaceous and Ingoldian fungi associated with leaf litter of decomposing Typha latifolia L. (Typhaceae) in riverine wetlands of the Pampean plain (Argentina) exposed to different water quality. Environ Manag Today 250: 109409.). In addition, molecular studies have shown that Ingoldian fungi are dominant representatives of the mycobiota associated with leaf litter decomposition in streams (Nikolcheva & Bärlocher 2004NIKOLCHEVA LG & BÄRLOCHER F. 2004. Taxon-specific fungal primers reveal unexpectedly high diversity during leaf decomposition in a stream. Mycol Prog 3(1): 41-49.).

The substrates mostly used as fungal source from freshwater environments of the Southern Cone of South America were leaf litter (31 %) and woody substrates (24 %, Figure 3a). The main technique used for detecting fungi was the wet chamber (44 %, Figure 3b). Also different methodological strategies have been employed such as those using leaf litter as source of incubations in chambers assisted with aeration (Chan et al. 2000CHAN SY, GOH TK & HYDE KD. 2000. Ingoldian fungi in Hong Kong. Fungal Divers 5: 89-107.) or by shaking (Bärlocher et al. 2005BÄRLOCHER F. 2005. Sporulation by aquatic hyphomycetes. Methods to study litter decomposition. Springer: Dordrecht, 185-188 p.), while the incubation on solid support under wet chamber, when wood is the inoculum source, is mostly used (Tsui et al. 2000TSUI CKM, HYDE KD & HODGKISS IJ. 2000. Biodiversity of fungi on submerged wood in Hong Kong streams. Aquat Microb Ecol 21(3): 289-298.). The aeration condition in water incubations facilitates mainly the recovery of Ingoldian fungi, while the wet chamber technique does so for obtaining mostly facultative fungi (Roldán et al. 1989ROLDÁN A, PUIG MA & HONRUBIA M. 1989. Comunidades fungicas asociadas a sustratos leñosos en un ríomediterráneo. Annales de limnologie: EDP Sciences, p. 191-195.). Therefore, the methodology conditions the composition of the fungal assemblage obtained from a specific substrate (Sridhar et al. 2010SRIDHAR KR, KARAMCHAND KS & HYDE KD. 2010. Wood-inhabiting filamentous fungi in 12 high-altitude streams of the Western Ghats by damp incubation and bubble chamber incubation. Mycoscience 51(2): 104-115.). Consequently, the dominance of facultative aquatic fungi reported in these studies for freshwater environments of the Southern Cone of South America could be due to technical limitations of the methodology applied for the detection of other categories of aquatic fungi. This is outstanding in articles from the Pampa province, where facultative fungi reached 139 taxa while Ingoldian and aero-aquatic ones, were 32 and 9, respectively.

Figure 3
Percentage of substrates (a) and methodologies (b) reported in each publication.

The procedures used in all the studies of the Southern Cone of South America are traditional ones based on culture and morphology; only a recent article used molecular approach (Seena et al. 2019SEENA S ET AL. 2019. Biodiversity of leaf litter fungi in streams along a latitudinal gradient. Sci Total Environ 661: 306-315.). Therefore, it is imperative that future studies on aquatic fungi from the Southern Cone of South America include methodologies that apply technological advances such as non-culturing techniques and bioinformatic tools as such metagenomic studies. This will contribute to overcome the limitations found by most of the classical mycologists when characterizing the fungal assemblages involved in aquatic environments such as those reported by Panzer et al. (2015)PANZER K ET AL. 2015. Identification of habitat-specific biomes of aquatic fungal communities using a comprehensive nearly full-length 18S rRNA dataset enriched with contextual data. PLoS ONE 10(7): e0134377. and Valderrama et al. (2016)VALDERRAMA B ET AL. 2016. Assessment of non-cultured aquatic fungal diversity from different habitats in Mexico. Rev Mex Biodivers: 87(1): 18-28.. Lepère et al. (2019)LEPÈRE C, DOMAIZON I, HUMBERT JF, JARDILLIER L, HUGONI M & DEBROAS D. 2019. Diversity, spatial distribution and activity of fungi in freshwater ecosystems. PeerJ 7: e6247. reported that still today there are also several limitations in the molecular studies about aquatic fungi since there are not specific molecular markers or well-represented reference databases, which prevent the exploration of the metabolic capacities of aquatic fungi through metagenomic and metatranscriptomic studies and their accurate taxonomic identification.

CONCLUSION

Since the data available about aquatic fungi from freshwater ecosystems reported for the Southern Cone of South America correspond mostly to taxonomical articles, more studies using innovative perspectives such as ecological and molecular ones are still necessary. Therefore, the availability of isolates of these fungi in axenic culture and their housing in culture collections such as in the Instituto Spegazzini (LPSC, Argentina), Facultad de Ciencias Exactas y Naturales, at the University of Buenos Aires (BAFCcult, Argentina), Westerdijk Fungal Biodiversity Institute (CBS, Netherland) or American Type Culture Collection (ATCC, United States of America), where they can be well preserved and used as reference, should be a high priority to decipher the structure and ecology of communities of fungi associated to freshwater ecosystems from the Southern Cone of South America (The cultures were indicated in the Table SII). Finally, our study highlights the need to increase the sampling effort at a regional scale by conducting as many surveys in the most diverse sets of aquatic ecosystems as possible, by exploring different habitats, as well as increasing the resolution of the fungal diversity by performing temporal surveys at the scale of some particular ecosystems. Moreover, it is necessary to emphasize the studies in lentic environments, which have been less explored in the Southern Cone of America so far.

ACKNOWLEDGMENTS

Financial support for this study was provided by PICT 2015-1342 to NG; PICT 2015-1620 to MCNS Agencia Nacional de Promoción Científica y Tecnológica; and Proyecto de Incentivos a la Investigación (A344) of the Facultad de Ciencias Agrarias y Forestales, UNLP, Argentina. The authors would like to thank Carolina Monti for literature research, Liliana Kuguel for english revision. Also thanks to Andrea López Osornio and Luciana de Tezanos for graphic design assistance on this article, as well as the editor and the anonymous reviewers for improving this manuscript. This paper is the Scientific Contribution No. 1176 of the Institute of Limnology “Dr. Raul Ringuelet” (ILPLA, CCT- La Plata CONICET, UNLP).

REFERENCES

  • ABDEL-AZIZ FA. 2008. Diversity of aquatic fungi on Phragmites australis at Lake Manzala, Egypt. Sydowia 60(1): 1-14.
  • ANDERSON JL & MARVANOVÁ L. 2020. Broad geographical and ecological diversity from similar genomic toolkits in the ascomycete genus Tetracladium. BioRxivin press.
  • BÄRLOCHER F. 2005. Sporulation by aquatic hyphomycetes. Methods to study litter decomposition. Springer: Dordrecht, 185-188 p.
  • BÄRLOCHER F, STEWART M & RYDER DS. 2011. Analyzing aquatic fungal communities in Australia: impacts of sample incubation and geographic distance of streams. Czech Mycol 63: 113-132.
  • BEVERWIJK VAN AL. 1951. Zalewski’s ‘Clathrosphaera spirifera’. Trans Brit Mycol Soc 34(3): 280-290.
  • CHAN SY, GOH TK & HYDE KD. 2000. Ingoldian fungi in Hong Kong. Fungal Divers 5: 89-107.
  • DESCALS E & MORALEJO E. 2001. Water and asexual reproduction in the ingoldian fungi. Bot Complut 25: 13-71.
  • DUARTE S, BÄRLOCHER F, PASCOAL C & CÁSSIO F. 2016. Biogeography of aquatic hyphomycetes: current knowledge and future perspectives. Fungal Ecol 19: 169-181
  • DUBEY A. 2016. Aquatic hyphomycetes communities occur as potential bioindicators of water quality. IJAR 2(8): 778-780.
  • FIUZA PO, PÉREZ TC, GULIS V & GUSMAO LF. 2017. Ingoldian fungi of Brazil: some new records and a review including a checklist and a key. Phytotaxa 306(3): 171-200.
  • GESSNER MO & CHAUVET E. 1994. Importance of stream microfungi in controlling breakdown rates of leaf litter. Ecology 75(6): 1807-1817.
  • GOH TK & HYDE KD. 1996. Biodiversity of freshwater fungi. J Ind Microbiol 17(5-6): 328-345.
  • GRAÇA MAS & FERREIRA RCF. 1995. The ability of selected aquatic hyphomycetes and terrestrial fungi to decompose leaves in freshwater. SYDOWIA-HORN 47: 167-222.
  • GRAÇA MAS, HYDE K & CHAUVET E. 2016. Aquatic hyphomycetes and litter decomposition in tropical–subtropical low order streams. Fungal Ecol 19: 182-189.
  • GROSSART HP, VAN DEN WYNGAERT S, KAGAMI M, WURZBACHER C, CUNLIFFE M & ROJAS-JIMENEZ K. 2019. Fungi in aquatic ecosystems. Nat Rev Microbio 17(6): 339-354.
  • GULIS V & SUBERKROPP K. 2003. Interactions between stream fungi and bacteria associated with decomposing leaf litter at different levels of nutrient availability. Aquat Microb Ecol 3(2): 149-157.
  • JABIOL J, BRUDER A, GESSNER MO, MAKKONEN M, ET AL. 2013. Diversity patterns of leaf-associated aquatic hyphomycetes along a broad latitudinal gradient. Fungal Ecol 6(5): 439-448.
  • JOHNSTON PR ET AL. 2019. A multigene phylogeny toward a new phylogenetic classification of Leotiomycetes. IMA Fungus 10(1): 1-22.
  • JOHNSTON PR & BASCHIEN C. 2020. Tricladiaceae fam. nov. (Helotiales, Leotiomycetes). FUSE 6: 233-242.
  • KOMINOSKI JS, ROSEMOND AD, BENSTEAD JP, GULIS V, MAERS JC & MANNING DW. 2015. Low-to-moderate nitrogen and phosphorus concentrations accelerate microbially driven litter breakdown rates. Ecol Monogr 25(3): 856-865.
  • LEPÈRE C, DOMAIZON I, HUMBERT JF, JARDILLIER L, HUGONI M & DEBROAS D. 2019. Diversity, spatial distribution and activity of fungi in freshwater ecosystems. PeerJ 7: e6247.
  • LINDQUIST JC. 1970. Hughesinia, nuevo género de hifomicetes (Demaciácea). Bol Soc Argent Bot 13: 53.
  • MORRONE JJ. 2001. Biogeografía de América Latina y el Caribe. M&T-Manuales & Tesis SEA, Sociedad Entomológica Aragonesa. Zaragoza 3: 152.
  • NIKOLCHEVA LG & BÄRLOCHER F. 2004. Taxon-specific fungal primers reveal unexpectedly high diversity during leaf decomposition in a stream. Mycol Prog 3(1): 41-49.
  • NILSSON S. 1962. Some aquatic hyphomycetes from South America. Svensk bot. Tidskr 56: 351-361.
  • PANZER K ET AL. 2015. Identification of habitat-specific biomes of aquatic fungal communities using a comprehensive nearly full-length 18S rRNA dataset enriched with contextual data. PLoS ONE 10(7): e0134377.
  • ROLDÁN A, PUIG MA & HONRUBIA M. 1989. Comunidades fungicas asociadas a sustratos leñosos en un ríomediterráneo. Annales de limnologie: EDP Sciences, p. 191-195.
  • ROMANÍ AM, ARTIGAS J, CAMACHO A, GRAÇA MAS & PASCOAL C. 2009. La biota de los ríos: los microorganismos heterotróficos. In: ELOSEGI A, SABATER S. (Eds), Conceptos y Técnicas en Ecología Fluvial, Fundación BBVA: España, p. 169-218.
  • SCHOENLEIN-CRUSIUS IH & GRANDI RAP. 2003. The diversity of aquatic hyphomycetes in South America. Braz J Microbiol 34(3): 183-193.
  • SEENA S ET AL. 2019. Biodiversity of leaf litter fungi in streams along a latitudinal gradient. Sci Total Environ 661: 306-315.
  • SHEARER CA ET AL. 2007. Fungal biodiversity in aquatic habitats. Biodivers Conserv 16(1): 49-67.
  • SOLÉ M, FETZER I, WENNRICH R, SRIDHAR KR, HARMS H & KRAUSS G. 2008. Aquatic hyphomycete communities as potential bioindicators for assessing anthropogenic stress. Sci Total Environ 389(2-3): 557-565.
  • SRIDHAR KR, KARAMCHAND KS & HYDE KD. 2010. Wood-inhabiting filamentous fungi in 12 high-altitude streams of the Western Ghats by damp incubation and bubble chamber incubation. Mycoscience 51(2): 104-115.
  • TARDA AS, SAPARRAT MCN & GÓMEZ N. 2019. Assemblage of dematiaceous and Ingoldian fungi associated with leaf litter of decomposing Typha latifolia L. (Typhaceae) in riverine wetlands of the Pampean plain (Argentina) exposed to different water quality. Environ Manag Today 250: 109409.
  • TSUI CKM, BASCHIEN C & GOH TK. 2016. Biology and ecology of freshwater fungi. En Biology of Microfungi. In: LI DW (Eds), Springer: Cham, p. 285-313.
  • TSUI CKM, HYDE KD & HODGKISS IJ. 2000. Biodiversity of fungi on submerged wood in Hong Kong streams. Aquat Microb Ecol 21(3): 289-298.
  • VALDERRAMA B ET AL. 2016. Assessment of non-cultured aquatic fungal diversity from different habitats in Mexico. Rev Mex Biodivers: 87(1): 18-28.
  • WEBSTER J. 1992. Anamorph-teleomorph relationships. In The ecology of aquatic hyphomycetes. Springer, Berlin: Heidelberg, p. 99-117.
  • WURZBACHER CM, BÄRLOCHER F & GROSSART HP. 2010. Fungi in lake ecosystems. Aquat Microb Ecol 59(2): 125-149.

SUPPLEMENTARY MATERIAL

Tables SI-SII

Publication Dates

  • Publication in this collection
    02 May 2022
  • Date of issue
    2022

History

  • Received
    29 July 2020
  • Accepted
    16 Dec 2020
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