• Proposed
  • Under Assessment
  • DDPreliminary Assessed
  • 4Assessed
  • 5Published

Psathyrella atlantica V. Coimbra & Wartchow

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Scientific name
Psathyrella atlantica
V. Coimbra & Wartchow
Common names
IUCN Specialist Group
Mushroom, Bracket and Puffball
Assessment status
Preliminary Assessed
Preliminary Category
Proposed by
Francisco Calaça
Diogo H. Costa-Rezende, Francisco Calaça, Genivaldo Alves-Silva, Juliano M. Baltazar, Luciana da Canêz, Marcela Monteiro
Gregory Mueller, E. Ricardo Drechsler-Santos, Kelmer Martins da Cunha

Assessment Notes


This is a rare species, known only from one collection found in Pernambuco State, Brazil in 2020. It is likely to become even rarer with the continued loss and degradation of the habitat in the Atlantic Forest due to human activity and climate change. Nevertheless, the habitat preferences of the species and its distribution are unclear, making it difficult to estimate its population size and trend

Taxonomic notes

Psathyrella atlantica V. Coimbra & Wartchow, Acta Botanica Brasilica 34 (2): 395 (2020). Psathyrella atlantica was described by Coimbra et al. (2020), based on both morphological and molecular evidence. Currently, there are no synonyms to this species, and based on morphological and phylogenetic analysis, the authors assume that this species is a genuine member of Psathyrella stricto sensu.

Why suggested for a Global Red List Assessment?

Geographic range

This species is found in the Atlantic Forest, and it was described as occurring at the lowland ombrophilous dense forest with a regeneration process (Coimbra et al. 2020). The species is currently known from one site, in the municipality of Tamandaré, found growing on litter deposited on the soil at ‘Reserva Biológica de Saltinho’, a biological reserve with Atlantic Forest remnants located in the municipalities of Tamandaré and Rio Formoso, Pernambuco State, Northeast Brazil. Nonetheless, the species is expected to be distributed along the Atlantic Forest in the dense ombrophilous forest areas/remnants. Considering the vegetation structure of the ombrophilous dense forest found in the ‘Reserva Biológica de Saltinho’ in Pernambuco with those ombrophilous forests that occur in the Amazon region (Condé et al. 2013), it is important to consider that P. atlantica can reach these areas, where vegetational cover is more conserved than that found in Atlantic Forest biome.

Population and Trends

  Psathyrella atlantica is a recently described species, currently known from only one site, with one collection (Coimbra et al. 2020). This site is located in a lowland ombrophilous dense forest inside the Atlantic Forest, which is a highly fragmented biodiversity hotspot reduced to only 28% of its original area (Myers et al. 2000, Rezende et al. 2018). It is expected that the species can also reach other ombrophilous dense forest areas in the Atlantic Forest. Psathyrella atlantica is likely rare, as Northeastern Brazil has been intensively studied in Brazil (see Maia et al. 2015 and their cited references), and even with intense efforts to sample the Funga in the region, it was recorded only at one site. Nevertheless, the habitat preferences of the species and its distribution are unclear, making it difficult to estimate its population size and trend.

Population Trend: Uncertain

Habitat and Ecology

Psathyrella atlantica is a saprophytic species, growing in the litter deposited on the soil. This species forms caespitose basidiomata composed by some slender, whitish, and with a small orange floccose-squamulose veil remnants pileus clustered mushrooms (Coimbra et al. 2020).

Subtropical/Tropical Moist Lowland Forest


The Atlantic Forest is considered a hotspot for biodiversity conservation due to various anthropogenic pressures, vegetation cover conversion, and the high rate of endemism observed in the biome (Myers et al. 2000). Because the remnant of the biome is highly fragmented, the annual rate of deforestation is still high and the consequences of the effects of environmental changes due to climate change, the areas where the species can occur are highly threatened (Salazar et al. 2007, Tabarelli et al. 2010, Rezende et al. 2018). Furthermore, an emerging threat is flexibility observed in public policies for the conservation of the Atlantic Forest. Recent deregulating acts from the current Brazilian government reduced protection and provided amnesty for deforestation in the Atlantic Forest (Vale et al. 2021). Psathyrella atlantica was observed in one site that is a kind of protected area by Brazilian law (Law nº 9.995/2000), close to urban centers, sites that may be heavily threatened, even under legal protection. In addition, the areas with the occurrence of ombrophilous dense forests are located in flat coastal areas. These coastal forest formations have been fragmented, converted, and occupied since the beginning of colonization, and overall, 65% of the biome surface is covered by anthropic areas. The few remnants are under intense anthropogenic pressure due to the expansion of coastal cities, illegal hunting, and excessive exploitation of natural resources (Joly et al. 2014, Schneider et al. 2018).

Housing & urban areasAgro-industry plantationsUnintentional effects: large scale (species being assessed is not the target) [harvest]Increase in fire frequency/intensityUnspecified speciesHabitat shifting & alteration

Conservation Actions

Ensuring the conservation of Atlantic Forest, under the Brazilian Native Vegetation Protection Law (Law No. 12.651/2012), known the Brazilian Forest Code, and mainly under the most specific law of protection for the biome (Law No. 11.428/2006) is the most efficient short-term measure. Forest restoration actions, the creation of new preservation areas, management, maintenance, and protection of existing preservation areas are also strategies that should be adopted for the conservation of habitats where the species can potentially occur (IIS 2021).

Site/area protectionSite/area managementAwareness & communicationsNational levelPolicies and regulations

Research needed

More surveys in suitable areas for the occurrence of the species should be explored, to determine the extent of its geographic distribution along the Atlantic Forest and even in other biomes in the country, such as the ombrophilous dense forests regions. Additionally, new collections may help to specify any variability of its morphological characters or ecological/microbiome interactions (Coimbra et al. 2020).

Population size, distribution & trendsLife history & ecologyThreats

Use and Trade

No use/trade known.



Berglund, H., Jonsson, B.G. 2005. Verifying an extinction debt among lichens and fungi in northern Swedish boreal forests. Conservation Biology19(2): 338-348. https://doi.org/10.1111/j.1523-1739.2005.00550.x

Coimbra, V.R.M., Mendes-Alvarenga, R.L., Lima-Junior, N.C., Gibertoni, T.B., Wartchow, F. 2020. Psathyrella atlantica (Agaricales: Basidiomycota), a new species from Brazil. Acta Botanica Brasilica 34(2): 394-400. https://doi.org/10.1590/0102-33062019abb0406

Condé, T.M., Tonini, H. 2013. Fitossociologia de uma Floresta Ombrófila Densa na Amazônia Setentrional, Roraima, Brasil. Acta Amazonica 43(3): 247-259. https://doi.org/10.1590/S0044-59672013000300002
Dahlberg, A. and Mueller, G. 2011. Applying IUCN red-listing criteria for assessing and reporting on the conservation status of fungal species. Fungal Ecology 4: 1-16. https://doi.org/10.1016/j.funeco.2010.11.001

Haddad, N.M., Brudvig, L.A., Clobert, J. et al. 2015. Habitat fragmentation and its lasting impact on Earth’s ecosystems. Science Advances 1: e1500052. https://doi.org/10.1126/sciadv.1500052

Joly, C.A., Metzger, J.P., Tabarelli, M. 2014. Experiences from the Brazilian Atlantic Forest: ecological findings and conservation initiatives. New Phytologist 204(3): 459-473. https://doi.org/10.1111/nph.12989

Maia, L.C., Carvalho-Junior, A.A., Cavalcanti, L.H. et al. 2015. Diversity of Brazilian Fungi. Rodriguésia 66(4): 1033-1045. https://doi.org/10.1590/2175-7860201566407
Myers, N., Mittermeier, R.A., Mittermeier, C.G., da Fonseca, G.A.B. and Kent, J. 2000. Biodiversity hotspots for conservation priorities. Nature 403: 853-858. https://doi.org/10.1038/35002501
Rezende, C.L., Scarano, F.R., Assad, E.D., Joly, C.A., Metzger, J.P., Strassburg, B.B.N., Tabarelli, M., Fonseca, G.A., Mittermeier, R.A. 2018. From hotspot to hopespot: An opportunity for the Brazilian Atlantic Forest. Perspectives in Ecology and Conservation 16(4): 208-214. https://doi.org/10.1016/j.pecon.2018.10.00
Salazar, L. F., Nobre, C. A., and Oyama, M. D. 2007. Climate change consequences on the biome distribution in tropical South America. Geophysical Research Letters 34(9): 2-7. https://doi.org/10.1029/2007GL029695

Schneider, L.C.A., Silva, M.T., Agostinetto, L., Siegloch, A.E. 2018. Deforestation in mixed ombrophilous forest in the Serrana Region of Santa Catarina. Revista Árvore 42(2): e420206. https://doi.org/10.1590/1806-90882018000200006
Tabarelli, M., Aguiar, A. V., Ribeiro, M. C., Metzger, J. P., and Peres, C. A. 2010. Prospects for biodiversity conservation in the Atlantic Forest: Lessons from aging human-modified landscapes. Biological Conservation 143(10): 2328-2340.

Country occurrence

Regional Population and Trends

Country Trend Redlisted