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

Hygrocybe nitrata (Pers.) Wünsche

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Scientific name
Hygrocybe nitrata
Author
(Pers.) Wünsche
Common names
Nitrous Waxcap
lutvokssopp
dušična vlažnica
voskovka ledková
stinkende vokshat
leelis-vesinutt
lipeävahakas
Hygrophore à odeur nitreuse
Nichtrötender Nitratsaftling
Apothekerswasplaat
lutvaxskivling
klorova vlažnica
Nichtrötender Nitrat-Saftling
IUCN Specialist Group
Mushroom, Bracket and Puffball
Kingdom
Fungi
Phylum
Basidiomycota
Class
Agaricomycetes
Order
Agaricales
Family
Hygrophoraceae
Assessment status
Preliminary Assessed
Preliminary Category
VU A2c+3c+4c
Proposed by
John Bjarne Jordal
Assessors
John Bjarne Jordal
Comments etc.
Anders Dahlberg, Irmgard Krisai-Greilhuber

Assessment Notes

Justification

Neohygrocybe nitrata is a species strongly confined to seminatural grassland in Europe, up to alpine areas. The species is not rare everywhere, but the habitat is sharply declining due to changing agricultural practices, development projects and pollution. Over the distribution range we assume a total habitat loss of 30-50% over the last 50 years (approximately three generations: one generation is assumed to be about 17 years). Habitat quality has also become impaired and the decline in population size over this time could be even higher. This decline in habitat is ongoing and expected to continue over the next 50 years. GBIF lists more than 3500 occurrences. The species is assumed to have a population of more than 20000 mature individuals. At a global scale (i.e. Europe) the decline is assumed to be on the average 30-50% in 50 years (past, present and future). The species meets the threshold for VU (A2c+3c+4c).


Taxonomic notes

The species is moved from Hygrocybe s. lat. to Neohygrocybe, as N. nitrata (Pers.) Kovalenko, based on molecular methods (Lodge et al. 2013). The type is from England. The taxonomic status of a few GBIF occurences in N America is uncertain; one sequenced was H. ingrata (Lodge et al. 2013) and these will therefore not be further treated here. One specimen sequenced from Russia was another species (Lodge et al. 2013). Synonymes: Hygrophorus nitratus (Pers.) Fr., Hygrocybe nitrata (Pers.) Wünsche, Hygrocybe murinacea ss. auct.


Why suggested for a Global Red List Assessment?

The species is with certainty only known from Europe. Here, it is a species of old seminatural grasslands, a habitat which is strongly declining due to changing agricultural practices, development projects and pollution. It is redlisted in many countries.


Geographic range

It is known from most countries of western Europe, but seem to lack eastwords.The eastern boundary is unclear due to lack of data. One sequenced specimen from Russia was another species (Lodge et al. 2013). It occurs regularly up to the forest limit and also sometimes up into the alpine zone in mountainous regions (2400 m a.s.l. in the Alps, Boertmann 2010). In Norway the frequency of this species in its habitats increases from sea level up to the forest limit (Jordal 1997).


Population and Trends

GBIF (2019) lists more than 3500 occurrences. Neohygrocybe nitrata is a species strongly confined to seminatural grassland. Griffith et al. (2013) estimated a habitat loss of 90% over the last 75 years for the CHEG-fungi (grassland fungi of Clavariaceae, Hygrocybe s.l., Entoloma and Geoglossaceae) as a whole in Western Europe (i.e. loss in seminatural grasslands, based on available information). According to the Food and Agriculture Organization of the United Nations (FAO), the area of grasslands in the EU declined by 12.8% over 13 years (1990-2003). Also other sources point to a habitat loss of roughly 1% per year in Europe over a longer time, although the data quality is not always very good. We assume a total habitat loss of at least 30% over the last 50 years. As the habitat quality is also declining, population decline should also be more than 30% in the last 50 years. This trend is ongoing and expected to continue in the future.

Population Trend: Decreasing


Habitat and Ecology

Neohygrocybe nitrata is an indicator of mycologically rich but nutrient-poor, semi-natural grassland (a member of the waxcap grassland assemblage). This habitat, which may be of low conservation concern for its plant and animal diversity, is rapidly disappearing due to changes in land use (see Threats). It is found from the sea up to alpine grasslands and snowbeds in low alpine zone, like in Scandinavia and in the Alps. In Norway, most localities of the species are in seminatural grasslands (N=905; 92,6% in seminatural grasslands, only 3,5% in forests; Jordal et al. 2016), and similar patterns are found in other countries. Halbwachs et al. (2018) suggested that waxcaps are biotrophic endophytes or possibly mycorrhizal, but the details remain unclear. The fruit bodies are short-lived (weeks), but the mycel is suspected to be longlived; >50-100 years.

Subarctic GrasslandTemperate Grassland

Threats

Habitat destruction and abandoning are the main threats to seminatural grasslands. The most important process is probably withgrowing due to ceased grazing/mowing of old seminatural grasslands as part of intensification of agriculture. Further modern cultivation methods like use of fertilizers, pesticides and plowing. Also some places changed land use with the construction of roads, industrial areas, settlements etc. Decline is expected to continue, as the areas of seminatural grasslands are of little economic importance in modern agriculture. Most waxcap grasslands are among types redlisted as VU, EN or CR in the EU red list of habitats (Jansen et al. 2016)

Housing & urban areasCommercial & industrial areasShifting agricultureAgro-industry farmingRoads & railroadsAcid rain

Conservation Actions

The habitats should be protected against destruction due to intensification of agriculture or development plans. The maintaining of seminatural grasslands demands yearly grazing or mowing. If grazing by heavy animals destroys part of the soil, light animals like sheep should be recommended. Habitat conservation by governmental support to traditional agricultural practices is most important, this exists in many countries to maintain extensive areas of agricultural areas, and should be extended to larger areas than today.

Site/area protectionAwareness & communicationsConservation payments

Research needed

Further ecological research is needed to clarify the nutrient strategy of waxcaps. Management plans are needed. Habitat trends should be monitored.

Population size, distribution & trendsLife history & ecologyArea-based Management PlanHabitat trends

Use and Trade

The species is not known to be used.


Bibliography

Adamčik, S. & Kautmanova, I. 2005. Hygrocybe species as indicators of natural value of grasslands in Slovakia. Catathelasma 6:25-34.
Artdatabanken Sweden 2019. Artfakta Hygrocybe nitrata. http://artfakta.artdatabanken.se/taxon/803
Artsdatabanken Norway 2019. https://www.artsdatabanken.no/Rodliste
Atlas grzybów Polski 2019. Mushrooms and Fungi of Poland: Hygrocybe nitrata. https://www.grzyby.pl/gatunki/Hygrocybe_nitrata.htm
Boertmann, D. (2010). The genus Hygrocybe. Fungi of Northern Europe 1. 2nd revised edition. Danish Mycological Society, Copenhagen.
Finnish Biodiversity Information Facility 2019. Suomen lajitietokeskus. https://laji.fi/en
Food and Agricultural Organisation of the United Nations 2006. FAO Statistical Yearbook. – FAOSTAT.
Foreningen til svampekundskabens fremme 2019. Danmarks svampeatlas. https://svampe.databasen.org/
GBIF 2019. Hygrocybe nitrata/Neohygrocybe nitrata. https://www.gbif.org/species/2538440 + https://www.gbif.org/species/2538438
German Mycological Society 2019. Pilzen Deutschlands: Neohygrocybe nitrata. http://www.pilze-deutschland.de/organismen/neohygrocybe-nitrata-pers-kovalenko-1989
Gozdarski Institut Slovenije 2019. Varstvo gozdov Slovenije: Hygrocybe nitrata. https://www.zdravgozd.si/bi_karta_sre.aspx?idorg=539fed53-9a62-40bb-b380-15409355dbdc
Griffith, G. W., Gamarra, J. P., Holden, E. M., Mitchel, D., Graham, A., Evans, D. A., et al. (2013) The international conservation importance of welsh ’waxcap’ grasslands. Mycosphere 4: 969–984. http://mycosphere.org/pdf/MC4_5_No10.pdf
Halbwachs H, Easton GL, Bol R, Hobbie EA, Garnett MH, Peršoh D, Dixon L, Ostle N, Karasch P & Griffith GW, 2018. Isotopic evidence of biotrophy and unusual nitrogen nutrition in soil-dwelling Hygrophoraceae. Environmental Microbiology 20 (10), 3573–3588 doi:10.1111/1462-2920.14327
Janssen, JAM, J.S. Rodwell, M. García Criado, S. Gubbay, T. Haynes, A. Nieto, N. Sanders, F. Lan-ducci, J. Loidi, A. Ssymank, T. Tahvanainen, M. Valderrabano, A. Acosta, M. Aronsson, G. Arts, F. Attorre, E. Bergmeier, R.-J. Bijlsma, F. Bioret, C. Biţă-Nicolae, I. Biurrun, M. Calix, J. Capelo, A. Čar-ni, M. Chytrý, J. Dengler, P. Dimopoulos, F. Essl, H. Gardfjell, D. Gigante, G. Giusso del Galdo, M. Hájek, F. Jansen, J. Jansen, J. Kapfer, A. Mickolajczak, J.A. Molina, Z. Molnár, D. Paternoster, A. Piernik, B. Poulin, B. Renaux, J.H.J. Schaminée, K. Šumberová, H. Toivonen, T. Tonteri, I. Tsiripidis, R. Tzonev and M. Valachovič, (2016). European Red List of habitats. Part 2, terrestrial and freshwater habitats. European Union, Luxembourg. http://ec.europa.eu/environment/nature/knowledge/pdf/terrestrial_EU_red_list_report.pdf
Jordal JB, 1997. Sopp i naturbeitemarker i Norge. En kunnskapsstatus over utbredelse, økologi, indikatorverdi og trusler i et europeisk perspektiv. Direktoratet for Naturforvaltning, Utredning for DN nr. 6 - 1997. 112 pp. [Fungi of seminatural grasslands in Norway. Status of knowledge about distribution, ecology, indicator value and threats in a european perspective]
Jordal, J.B., Evju, M., Gaarder, G., 2016. Habitat specificity of selected grassland fungi in Norway. Agarica 37: 5-32. http://www.jbjordal.no/publikasjoner/Habitat_specificity_Jordal_et_al2016.pdf
Lodge D.J., Padamsee M., Matheny P.B., Aime M.C., Cantrell S.A., Boertmann D., Kovalenko A., Vizzini A., Dentinger B.T.M., Kirk P.M., Ainsworth A.M., Moncalvo J.-M., Vilgalys R., Larsson E., Lücking R., Griffith G.W., Smith M.E., Norvell L.L., Desjardin D.E., Redhead S.A., Ovrebo C.L., Lickey E.B., Ercole E., Hughes K.W., Courtecuisse R., Young, A., Binder M., Minnis A.M., Lindner D.L., Ortiz-Santana B., Haight J., Læssøe T., Baroni T.J., Geml J., Hattori T. (2014). Molecular phylogeny, morphology, pigment chemistry and ecology in Hygrophoraceae (Agaricales). Fungal Diversity 64:1-99. https://www.researchgate.net/publication/258508783_Molecular_phylogeny_morphology_pigment_chemistry_and_ecology_in_Hygrophoraceae_Agaricales
Newton, A.C., Davy, L.M., Holden, E., Silverside, A., Watling, R. & Ward, S.D. 2003. Status, distribution and definition of mycologically important grasslands in Scotland. Biological Conservation 111:11-23.
Österreichische Mykologische Gesellschaft 2019. Datenbank der Pilze Österreichs. http://austria.mykodata.net/Taxa_0.aspx
NBN Atlas 2019. Hygrocybe nitrata. https://species.nbnatlas.org/species/NHMSYS0001484498
Nederlandse Mykologische Vereniging 2019. Verspreidingsatlas Paddenstoelen: Hygrocybe nitrata. https://www.verspreidingsatlas.nl/0059220
Swiss Federal Institute for Forest, Snow and Landscape Research 2019. Swiss fungi. Distribution atlas. https://swissfungi.wsl.ch/en/distribution-data/distribution-atlas.html
Tkalčec Z., Mešić A., Matočec N, Kušan I., 2008. Crvena Knjiga Gljiva Hrvatske/Red Book Of Croatian Fungi. Ministarstvo Kulture. Državni zavod za zaštitu prirode Republika Hrvatska. Zagreb. 430 pp.


Known distribution - countries

Regional Population and Trends

Country Trend Redlisted