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  • Under Assessment
  • Preliminary Assessed
  • Assessed
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Cortinarius citrino-olivaceus M.M. Moser

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Scientific name
Cortinarius citrino-olivaceus
Author
M.M. Moser
Common names
 
IUCN Specialist Group
Mushroom, Bracket and Puffball
Kingdom
Fungi
Phylum
Basidiomycota
Class
Agaricomycetes
Order
Agaricales
Family
Cortinariaceae
Assessment status
Published
IUCN Red List Category
VU C2a(i)
Proposed by
Tor Erik Brandrud
Assessors
Tor Erik Brandrud
Contributors
Tor Erik Brandrud

Assessment Status Notes

Taxonomic notes


Why suggested for a Global Red List Assessment?

Cortinarius citrinoolivaceus is a mycorrhizal species associated with Abies alba and rarely with Pinus sylvestris. It belongs to the rich fungus element of the (mixed) calcareous Abies alba forests of C Europe.  Many of the species occurring here has a limited host range, edaphic requirements and distribution. Some occurs both in calcareous fir- and calcareous oak-beech forests, some occur both in calcareous fir- and calcareous spruce-pine forests, but some occurs only/mainly in Abies alba forests, such as the present one, Cortinarius atrovirens, C. haasii, C. subgracilis and Hygrophorus pudorinus. These species, is suffering from decline in the small and fragmented calcareous fir forests of e.g. Black Forest, the Jura, Prealps and the Carpaths, due to e.g. areal loss in more heavy populated areas and loss/fragmentation of older coniferous forest stands from modern (clear-cut) forestry.
Global and European Red List assessment;
VU (C2a(i)), with a continuous decline of the species and its habitat, and a small, restricted population, with an estimated size of less than 5000 sites and less than 10.000 individuals, and very small subpopulations.

Cause:
The decline is due to a long-term and persistent decline in mature/old-growth silver fir forests, due to forestry. The montane forests in Tyrol, where the species has its major area, has had an increased forestry activity, with a doubling of annual felling the last 40 years, according to forestry statistics (Austria). Furthermore, a habitat-loss is probably seen in many silver fir regions due to settlement/tourist resort expansion, road construction, ski tracks, etc. The narrow bands of Abies forests in the Alp valleys may also be vulnerable to climate change. The mature, calcareous pine forests at Gotland (Sweden) is also declining, due to forestry and areal loss due to expansion of limestone quarries, as well as altered management practices (incl. loss of cattle grazing).


Geographic range

Cortinarius citrinoolivaceus has a limited, disjunct/fragmented European distribution, with a core area in certain Abies districts of the Prealps and some outposts in Pinus forests at Gotland and in the Pyrenees. Recorded from E France, N Italy, Austria, NE Spain and SE Sweden (Gotland). So far no certain records are known from the northern flank of calcareous Abies alba forests in Germany, the eastern-southeastern flanks in the Carpaths, nor the southern flank of the Apennines, C Italy. Among the better investigated calcareous Abies forest areas, the species is completely lacking from the Black Forest area, and appears very rare in the Jura, whereas the species is more distributed in Tyrol. This pattern may indicate that the species has a slightly eastern-continental distribution within the calcareous Abies alba forest range, and the species might be occurring also farther east-south east, e.g. in the limestone-dolomite areas of SE Prealps of Slovenia and the W Carpaths, in districts which are up to now little surveyed for Cortinarius species.
Cortinarius citrinoolivaceus, as well as the other, more or less strict members of this calcareous Abies alba element (such as Cortinarius atrovirens), are not reported from outside Europe.


Population and Trends

The species is among the rarest within the calcareous Abies alba forest element. It has a core area in montane, dolomite areas in Tyrol in the eastern Prealps. Collections from approx 10 localities in Austria and 2 from adjacent N Italy are available. The species is furthermore found in the French Jura (E France; on limestone plateaus), but must be very rare here, since lacking in the extensive publications on Cortinarius from the area. Finally, the species is recorded from Pyrenees (NE Spain) and from three, possibly four sites at the limestone island of Gotland, S Sweden. Known, verified records are summing up to approx. 20, and the real number of sites/localities is estimated to be approx.. 200-300, corresponding with a total of 4000-6000 individuals.

According to the sites seen, the species is mainly associated with older coniferous forest stands, without influence of modern forestry with clear-cuts. These habitats are declining in the core area of Tyrol, due to increased forestry (see under threats. The three, known localities from Gotland, Sweden are from extremely calcareous, formerly grazed pine forests, being hotspots for threatened coniferous forests species in general, but more specificially, also housing several outpost localities for typical Abies alba species such as Cortinarius atrovirens, C. haasii, and C. subgracilis. These forests are now declining on Gotland (see under threats). 

The C European silver fir forests have also regionally been seriously declining during the latest 50 years due to long transboundary air pollution leading to forest die-back. However, the pollution and its effects are now decreased, and is furthermore effecting mainly less calcareous forest stand.

The decline in old-growth, calcareous Abies forests due to forestry and habitat-loss is estimated to approx. 15-20% during the evaluation period. Based on this the species becomes red-listed as NT according to the A criterion (A2c + 3c + 4 c). It is, however redlisted as VU according to the C criterion, since associated with declining habitats (calcareous Abies forests in C Europe, and calcareous pine forests at Gotland), and having small to very small, quite local populations.
We evaluate the species to VU after C2 a(i) based on a continuously decline, population size <10 000 individuals, and very small subpopulations.

Population Trend:


Habitat and Ecology

The species is a mycorrhizal associate mainly with Abies alba, but in outposts outside the natural distribution area of Abies also with Pinus sylvestris (Spain, Sweden). The species was initially described from Picea abies forests of N Tyrol, Austria, but on examination of collected material from N Tyrol, needles from both Abies alba and Picea abies were found on the fruitbodies, indicating that this actually occurs in mixed Abies-Picea forests. All C European finds are from Abies forests or from mixed Abies-Picea forests, where the species is found together with other Abies specialists such as C. atrovirens. The species is never found in pure Picea forests, and never in Picea-dominated regions outside the Abies alba range. It is therefore concluded that this is an Abies forest associate in C Europe. The species occur in mossy, calcareous forests, in Tyrol mainly on dolomite ground, elsewhere on limestone. The sites at Gotland as strictly calcareous, and the species occurs with other strictly calciphilous fungi.


Threats

The species is threatened by loss, depauperation and fragmentation of intact, calcareous fir and pine forest habitats, due mainly to intensive forestry. The montane forests in Tyrol, where the species has its major area, has had an increased forestry activity, with a doubling of annual felling the last 40 years, according to forestry statistics (Austria). Furthermore, a habitat-loss is probably seen in many silver fir regions due to settlement expansion, road construction, ski tracks, etc. The narrow bands of Abies forests in the Alp valleys may also be vulnerable to climate change. The mature, calcareous pine forests at Gotland (Sweden) is also declining, due to forestry and areal loss due to expansion of limestone quarries, as well as altered management practices (incl. loss of cattle grazing), leading to depauperated habitat qualities for the strictly calciphilous pine forests species.


Conservation Actions

To prevent decline and fragmentation of calcareous fir(-pine) forests with good habitat quality, it is important to set aside reserves on calcareous hotspots, housing many rare/redlisted species such as Cortinarius citrinoolivaceus and C. atrovirens. It is furthermore important to establish woodland key biotopes and similar kinds of forest stand where a non-intensive, closed cutting is performed, leaving much of the stand qualities intact, including a continuity in the fir/pine roots and their mycorrhizae.


Research needed

There is a need for further mapping/surveying of the species, especially in more eastern regions of calcareous silver fir forest habitats, such as the SE Prealps of Slovenia and the W Carpaths of Slovakia.


Use and Trade


Bibliography

Brandrud, T.E., Lindström, H., Marklund, H., Melot, J. & Muskos, S. 2012. Cortinarius, Flora Photographica. Vol. 5 (Swedish version; French version 2013; English 2015). Härnösand.
Brandrud, T. E., Frøslev, T. G. & Jeppesen, T. S. 2015.The taxonomy of Cortinarius subgenus Phlegmacium section Percomes in Europe. In prep. for Mycological Progress.
Moser, M. 1961 (“1960”). Die gattung Phlegmacium. Verlag Julius Klinkhardt. Bad Heilbrunn Obb.


Known distribution - countries

Regional Population and Trends

Country Trend Redlisted