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Basidiomycete diversity within Calabrian pine (Pinus brutia) ecosystems on the island of Cyprus

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  • Cyprus Mycological Association

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Extended areas on the island of Cyprus including the vast majority of forested land, are occupied by Pinus brutia, an ecologically important tree forming ectomycorrhizal associations with a wide array of fungi. In this third installment of macromycete inventories from selected ecosystems in Cyprus, the basidiomycete diversity within P. brutia communities is reported following a 12-y-inventory. Two hundred and thirty-one taxa are compiled in an annotated checklist, 95 of which constitute new records for the country. Most notable of these are Clitopilus daamsii, Hygrophorocybe nivea, Lepiota lepida, Leucoagaricus georginae, Rhodocybe matesina, Russula werneri, Tephrocybe striaepilea, Tephroderma fuscopallens, and Tricholoma chrysophyllum, which are rarely reported in published literature. Notes on the altitude, phenology and estimated abundance are provided, accompanied by selected imagery and a review of previously published records.
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Basidiomycete diversity within Calabrian pine (Pinus brutia)
ecosystems on the island of Cyprus
ΜICHAEL LOIZIDES
P.O. BOX 58499, 3734 LIMASSOL, CYPRUS
CORRESPONDENCE: michael.loizides@yahoo.com
ABSTRACTExtended areas on the island of Cyprus including the vast majority of forested land, are occupied by Pinus brutia, an
ecologically important tree forming ectomycorrhizal associations with a wide array of fungi. In this third installment of macromycete
inventories from selected ecosystems in Cyprus, the basidiomycete diversity within P. brutia communities is reported following a 12-y-
inventory. Two hundred and thirty-one taxa are compiled in an annotated checklist, 95 of which constitute new records for the country.
Most notable of these are Clitopilus daamsii, Hygrophorocybe nivea, Lepiota lepida, Leucoagaricus georginae, Rhodocybe matesina,
Russula werneri, Tephrocybe striaepilea, Tephroderma fuscopallens, and Tricholoma chrysophyllum, which are rarely reported in
published literature. Notes on the altitude, phenology and estimated abundance are provided, accompanied by selected imagery and a
review of previously published records.
KEY WORDSbiogeographical distribution, checklist, East-Mediterranean pine, fungi, inventory, island biogeography, Turkish pine
Introduction
Pinus brutia Ten., the Calabrian or East-Mediterranean pine, along with its sister-species the Aleppo pine (P.
halepensis Mill.), are ecologically important constituents of the Mediterranean flora jointly occupying some 7
million hectares (Quézel 2000). Both species have developed efficient regeneration mechanisms to deal with
wildfires in the region, and grow prolifically on dry and infertile substrates in the thermo-, meso- and supra-
Mediterranean belts (Nahal 1983; Thanos & Doussi 2000; Mauri et al. 2016). On the island of Cyprus,
Calabrian pine occupies some 175,000 hectares, accounting for ~90% of all woodland coverage on the country
(Meikle 1977; Tsintides et al. 2002). Although pure stands sometimes occur, the majority of P. brutia
populations are found in mixed ecosystems, with Kermes oaks [Quercus coccifera subsp. calliprinos (Webb)
Holmboe], strawberry trees (Arbutus andrachne L.), and rockroses (Cistus L. spp.) usually present in the
understorey. Throughout the meso- and supra-Mediterranean belts of the Troodos massif (4001400 m. asl),
P. brutia forms extensive forests with the narrow-endemic golden oak (Quercus alnifolia Poech), while at
higher elevations it is replaced by P. nigra subsp. pallasiana (Lamb.) Holmboe, although both black- and
Calabrian pines can co-exist within a narrow phytogeographical belt from 1200 to 1400 m. asl.
Pinus brutia forms ectomycorrhizal (EcM) associations with a wide array of basidiomycetes and
ascomycetes. Such multifunctional mutualisms are fundamental for terrestrial ecosystems, enhancing plant
productivity, alleviating abiotic and oxidative stress, and regulating carbon, nitrogen and phosphorus cycling
(Smith & Read 2010; van der Heijden et al. 2015). The logs and branches of P. brutia moreover provide suitable
substrates for a number of cellulolytic decomposers (Bernicchia 2005; Bernicchia & Gorjón 2010; Loizides
2018), while several terrestrial saprotrophs are commonly encountered among the tree litter (Athanasiou &
Theohari 2001; Loizides et al. 2011; Polemis et al. 2012; Dimou et al. 2016). Although the physiology and
biogeography of P. brutia have been extensively studied (Panetsos 1981; Thanos & Marcou 1991; Petrou &
Milios 2012), little is known of the composition, structure and dynamics of its associated fungal diversity.
Several basidiomycetes have been reported from P. brutia ecosystems in genus-specific taxonomic treatments
and popular field guides from Cyprus, including a number of taxa described as new to science, such as
Clavulina iris Loizides et al. (Crous et al. 2019), Hydnellum dianthifolium Loizides et al. (Loizides et al. 2016),
Hygrophorus meridionalis Loizides et al. (Moreau et al. 2018), and Russula hobartiae Loizides & Vidal (Vidal
et al. 2019). However, comprehensive inventories from P. brutia ecosystems are lacking, resulting in a
fragmented understanding of the full range of macromycete diversity present in these important Mediterranean
habitats. The basidiomycete diversity in Calabrian pine ecosystems is extensively documented in this paper,
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following a 12-y-inventory carried out in Cyprus between 2007 and 2019. A total of 231 taxa are overall
compiled in an annotated checklist, 95 of which are reported from Cyprus for the first time. Some interesting
finds and previously published records are discussed, and imagery, accompanied by brief taxonomic notes for
critical taxa, are included.
Materials & Methods
Material was collected as part of a general inventory in Cyprus carried out by the author from 2007 to 2019. A large number
of sites across an extended altitudinal gradient were systematically surveyed following a sampling protocol described in
Loizides (2016, 2018), and Loizides et al. (2019a, 2019b). Collections were photographed in situ and details on the
macromorphological aspect, including size, colour, odour and oxidation of the flesh, were observed on freshly collected
specimens. Iron sulfate (FeSO4), Guiac tincture and Phenol were applied to observe chemical reactions on the flesh of
species of the genus Russula Pers. Potassium hydroxide (5% KOH) was applied to observe chemical reactions on the pileus
and flesh of Cortinarius (Pers.) Gray species. Microscopic studies were performed under a LEICA BM E binocular and an
AM T360B trinocular microscopes, at ×40, ×100, ×400 and ×1000 magnifications. Congo Red in 10% ammonia (NH3),
5% potassium hydroxide (KOH), lactophenol cotton blue (LPCB), aqueous Phloxine, Melzer’s solution and tap water were
used accordingly as mounting mediums and diagnostically important microscopic structures were observed. The checklist
is arranged in alphabetical order and includes previously reported taxa, as well as species newly identified in the course of
this survey marked below with an asterisk (*). Doubtful records, or species identified only to genus are excluded (see also
“Discussion”). Wood-inhabiting aphyllophoraceous basidiomycetes and ascomycetes are included in separate dedicated
checklists (Loizides 2018 & in prep.). Unless otherwise noted, specimens were collected, photographed and identified by
the author. Index Fungorum (http://www.indexfungorum.org), Mycobank (http://www.mycobank.org), and recently
published systematic revisions were consulted to provide most recently updated names for the cited taxa. Exsiccatae are
kept in the private collection of the author, with selected collections deposited at ACAM (Agricultural University of
Athens), BCN (Universitat de Barcelona Herbari), CEFE (Centre d’Ecologie Fonctionnelle et Evolutive, Montpellier), K
(Royal Botanic Gardens at Kew), and LIP (Université de Lille).
Species recorded
Agaricus augustus Fr.
Occasionally encountered in black-and Calabrian pine forests, with one collection from a mixed Pinus brutia/Quercus
alnifolia/Arbutus andrachne forest in Amíantos, 21-X-2011, ca 1300 m asl.
Agaricus bisporus (J.E. Lange) Imbach
Common in pastures and along Cupressus sempervirens L. groves, but once collected in a coastal P. brutia forest in
Akrotíri, 11-II-2014, ca 20 m asl.
Agaricus brunneolus (J.E. Lange) Pilát
This bitter-almond scented wood dweller is frequently seen at various elevations, e.g., Saittás ,9-XII-2007 & 6-I-2017,
ca 700 m asl; Platánia, 27-XI-2008, 1-XII-2009 & 23-XII-2018, ca 1200 m asl; Lysós, 18-I-2009, ca 600 m a.s.l; Mávro
Dásos, 5-XII-2012, ca 1200 m asl; Troodítissa, 17-XI-2017, ca 1400 m asl. Also reported by Viney (2005) with its old
nameA. porphyrrhizon P.D. Orton”, from the pine woods of Pentadáktylos, Dec. 2001.
Agaricus impudicus (Rea) Pilát
Probably the most common representative of the genus in Cyprus, with numerous sightings in all kinds of forests,
including Calabrian pine forests in Amíantos, 19-X-2008 & 10-X-2009, ca 1300 m asl; Troodítissa, 13-X-2008, 26-X-
2011, 31-X-2011 & 9-XI-2018, ca 1400 m asl; Plátres, 17-XI-2008, ca 1000 m asl; Saittás, 25-XI-2009 & 10-I-2017,
ca 700 m asl; Kannavioú, 29-XI-2017, ca 800 m asl.
*Agaricus litoralis (Wakef. & A. Pearson) Pilát
Three collections in different seasons, all from the same locality in a P. brutia forest at Agros, 4-IV-2007, 8-IV-2008
& 24-III-2011, ca 1000 m asl. Rare.
Agaricus macrocarpus F.H. Møller
Reported by Loizides et al. (2011) based on a collection from a mixed P. brutia/Q. alnifolia forest in Plátres, 29-XII-
2009, ca 1200 m asl, but several new species have been described in section Arvenses since (Parra Sánchez 2013),
whose morphological identification is far from straight forward. Several species of this group seem to occur in Cyprus,
including some not comfortably fitting available descriptions, that ultimately need to be resolved by DNA sequencing.
A collection from Syrianóchori, Jan. 2001, was also reported as “A. aff. macrocarpusby Viney (2005).
Agaricus moelleri Wasser
Occasionally seen in mixed P. brutia forests (Loizides et al. 2011): e.g., Amíantos, 19-X-2008, ca 1300 m asl; Saittás,
Basidiomycetes within Pinus brutia ecosystems in Cyprus
3
4-XII-2008 & 30-XI-2016, ca 700 m asl; or Platánia, 10-X-2009 & 7-XI-2009, ca 1100 m asl.
*Agaricus pampeanus Speg.
One collection fitting the description of this sparingly reported species, from a P. brutia/Quercus alnifolia forest
clearing at Mésa Potamós, 12-XII-2011, ca 800 m asl. Rare.
Agaricus pseudopratensis (Bohus) Wasser
Common in the lowlands under C. sempervirens and open fields, but rarely also seen in Cistus matorral (Loizides 2016)
and forest clearings: Saittás, 30-XI-2016, ca 650 m asl; Stavrós tis Psókas, 29-XI-2017, ca 1200 m asl.
*Agaricus sylvaticus Schaeff.
Rarely seen in riparian broadleaved forests and once in a Calabrian pine forest in Péra Pedí, 10-I-2017, ca 55 asl.
Agaricus sylvicola (Vittad.) Peck sensu lato
Occasionally encountered in black pine and broadleaved riparian forests (Loizides et al. 2011), with a couple of
collections from a Calabrian pine forest in Trimíklini, 23-XII-2007 & 17-XII-2011, ca 650 m asl.
Agaricus xanthodermus Genev.
The “yellow stainer” is rare in Cyprus (Loizides et al. 2011), with a couple of records from mixed P. brutia forest
clearings: Platánia, 16-XI-2014, ca 1100 m asl; Kannavioú, 29-XII-2016, ca 800 m asl.
Amanita ovoidea (Bull.) Link
Probably the most widespread and ecologically versatile Amanita Pers. species on the island, occurring from near-sea
level to ~1700 m asl in association with Pinus L., Quercus L., and occasionally Eucalyptus L’Hér. First reported on the
island by Nattrass (1937) from Ktíma (Paphos), Dec. 1932; and later also by Viney (2005) from Kaló Chorió, Nov.
1999, Loizides (2011), and Loizides et al. (2011, 2018) from Trimíklini, 13-X-2009, 10-XI-2012 & 14-XI-2012, ca
650 m asl; Kouká, 15-X-2009, ca 500 m asl; Karvounás, 16-X-2011 & 23-X-2011, ca 1200 m asl; Plátres, 19-XI-2011,
ca 1200 m asl; Platánia, 16-XI-2014, ca 600 m asl; and Akrotíri, 24-XI-2014 & 10-XII-2017, ca 20 m asl. Sometimes
collected for the table by the locals, which has led to a number of poisonings in the past likely due to confusion with A.
proxima (Loizides et al. 2018).
Amanita proxima Dumée
Several collections from Trimíklini, 30-X-2008, 10-XI-2012 & 1-XII-2017, ca 650 m asl; Kouka, 15-X-2009, ca 500
m asl; Karvounás, 13-X-2011, 16-X-2011 & 3-XI-2015, ca 1200 m asl; Kélefos, 31-X-2012, ca 500 m asl; and Akrotíri,
24-XI-2014 & 10-XII-2017, ca 20 m asl. Previously reported by Viney (2005) from Haléfka, Nov. 1997, and by
Loizides (2008), and Loizides et al. (2011 & 2018) from collections cited above. This fungus contains allenic
norleucine, a potentially deadly nephrotoxin (De Haro et al. 1998) and can be confused with A. ovoidea, with which it
shares the same habitat and distribution. Most likely the unidentified “white Amanita species briefly discussed and
sketched by Willimott (1933), responsible for a number of fatalities early last century.
Arrhenia rickenii (Hora) Watling
Frequently seen on coastal and inland dunes (Loizides 2016), but also in mossy P. brutia forests in the thermo-
Mediterranean belt: Mosfilotí, 23-I-2011, ca 250 m asl; Politikó, 9-I-2012, ca 400 m asl.
Arrhenia spathulata (Fr.) Redhead
Sparingly encountered in matorral and mossy forests in the dunal and thermo-Mediterranean belts, such as Trimíklini,
26-XI-2008, 9-XII-2011 & 31-XII-2013, ca 650 m asl.
*Atheniella flavoalba (Fr.) Redhead, Moncalvo, Vilgalys, Desjardin & B.A. Perry
One collection matching the description of this taxon, previously placed in genus Mycena (Pers.) Roussel. Found among
P. brutia litter in Kélefos, 2-I-2009, ca 500 m asl. Distribution unclear.
*Atractosporocybe inornata (Sowerby) P. Alvarado, G. Moreno & Vizzini
Previously placed in the genus Clitocybe (Fr.) Staude, this species was recently transferred to the new genus
Atractosporocybe P. Alvarado et al. (Alvarado et al. 2015). Fairly widespread in upland P. nigra subsp. pallasiana
forests and Cedrus brevifolia A. Henry ex Elwes & A. Henry plantations, but occasionally also encountered in mixed
P. brutia/Q. alnifolia forests in Plátres, 17-XII-2007, ca 900 m asl; Álona, 5-XI-2009, ca 1300 m asl.; vro Dásos,
1-XII-2012, ca 1200 m asl; and Platánia, 30-XII-2014, ca 1100 m asl.
*Baeospora myosura (Fr.) Singer
Sparingly seen on the island, this species inhabits fallen cones of conifers, particularly of P. brutia. Collected in
Amíantos ,9-XI-2009, ca 1300 m asl; Kélefos, 29-XI-2009, ca 500 m asl; and Platánia, 21-XII-2011, ca 1100 asl.
*Bovista aestivalis (Bonord.) Demoulin
A handful of collections, one from a P. brutia forest in Moniátis, 29-IX-2011, ca 750 m asl. Uncommon.
Chalciporus amarellus (Quél.) Bataille
Previously reported by Viney (2005) from Haléfka, Jan. 1998, this striking bolete is known only from three additional
collections in Saittás, 17-XI-2007, ca 700 m asl; Platánia, 26-XI-2009, ca 1100 m asl; and Kélefos, 28-XI-2009, ca 450
m asl (Loizides et al. 2019a). Although all collections originate from P. brutia forests, this species is probably a
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Loizides, M.
mycoparasite (Tedersoo et al. 2010; Nuhn et al. 2013).
Chroogomphus mediterraneus (Finschow) Vila, Pérez-De-Greg. & G. Mir
One of the most widespread and consistently occurring fungi in Cyprus, present from the dunal zone to the peaks of
the Troodos massif. Numerous sightings, including Péra Pedí, 21-XI-2007, ca 700 m asl; Pissouri, 25-I-2009, ca 200
m asl; Kélefos, 20-XI-2009, 28-XI-2009, 28-I-2010 & 2-XII-2014, ca 500 m asl; Kannavioú, 15-XII-2009, ca 800 m
asl; Mosfilotí, 23-I-2011, ca 250 m asl; Akámas, 18-XII-2014, ca 150 m asl; Akrotíri, 12-I-2015 & 10-II-2017, ca 20
m asl. Collections reported by Viney (2005) and Loizides et al. (2011) as C. rutilus (Schaeff.) O.K. Mill.”, all seem to
belong to this widespread species (see Scambler et al. 2018 and “Discussion” for further remarks).
*Clathrus ruber P. Micheli ex Pers.
The “latticed stinkhorn” is a rare species in Cyprus, known only from four collections in Saittás, 13-XII-2007, ca 700
m asl; Plátres, 17-X-2008 & 11-XII-2012, ca 900 m asl; and Kélefos, 1-I-2019, ca 500 m asl, all in mixed habitats.
Clavulina coralloides (L.) J. Schröt. sensu lato
Reported by Viney (2005) as C. cristata”, from Haléfka, Jan. 1998, and later by Loizides et al. (2011) from collections
in Platánia, 5-XII-2009, ca 1150 m asl, and Loizides (2016) from collections under Cistus, but DNA sequencing
suggests that more than one species might be involved (unpubl. data).
Clavulina iris Loizides, Bellanger & P.-A. Moreau
Numerous collections of this recently described and widespread species, appearing from mid-winter to early spring in
a variety of calcareous habitats in association with Cistus, P. brutia and Quercus, e.g. Péra Pedí, 24-III-2009 & 2-III-
2019, ca 550 m asl; Soúni, 16-III-2012, 25-II-2013, 21-II-2015, 2-III-2015, 4-III-2019 & 6-III-2019, ca 400 m asl;
Anogyra, 17-II-2015, ca 400 m asl; Platánia, 26-XII-2018, ca 1100 m asl; Kélefos, 1-I-2019, ca 500 m asl; and
Trimíklini, 28-II-2019, ca 650 m asl (for sequenced collections and a detailed description see Crous et al. 2019).
*Clitocella fallax (Quél.) Kluting, T.J. Baroni & Bergemann
Two collections from mixed forests in Cedar Valley, 18-XI-2009, ca 1100 m asl; and Kélefos, 20-I-2011, ca 450 m asl,
matching the descriptions of this rarely reported species but featuring rather variable spores, ranging from 5–7 × 3.5
4.5 μm to 6–8 × 45 μm. In the phylogeny provided by Kluting et al. (2014), European collections from Norway and
Spain form a well-supported clade distinct from a North American collection identified as this taxon, indicating the
presence of more than one species under this name. European collections likely correspond to C. fallax ss. str.
Clitocella popinalis (Fr.) Kluting, T.J. Baroni & Bergemann sensu lato
Reported by Viney (2005) as “Rhodocybe popinalisfrom pine forests of Haléfka, Jan. 2001, and subsequently
collected by the author in Kakomállis, 29-X-2009, ca 750 m asl; and Palechori, 2-XI-2009, ca 900 m asl. At present,
collections identified as C. popinalis and the closely related C. mundula (Lasch) Kluting et al., seem to nest in multiple
clades in published phylogenies (Kluting et al. 2014; Vizzini et al. 2016 & 2018), therefore deeper phylogenetic
investigations are needed to clarify their precise taxonomic status.
Clitocybe diatreta (Fr.) P. Kumm.
Reported by Viney (2005) from the pine woods of Áyios Amvrósios, Nov. 2000, and by Loizides et al. (2011) from a
P. brutia/Quercus coccifera subsp. calliprinos forest clearing in Kélefos, 24-XII-2009, ca 500 m asl.
*Clitocybe fragrans (With.) P. Kumm
One of several Clitocybe species with an aniseed odour, with a couple of collections from Kélefos, 2-XII-2008 & 2-I-
2009, ca 500 m asl. More frequently seen in high elevation P. nigra subsp. pallasiana forests.
*Clitocybe lituus (Fr.) Métrod
A couple of collections matching the description of this taxon from Álona, 5-XI-2009, ca 1300 m asl; and Saittás, 18-
XII-2009, ca 650 m asl. Uncommon or rare.
*Clitocybe metachroa (Fr.) P. Kumm.
Few collections from mixed P. brutia and Q. alnifolia forests in Mesa Potamos 2-XII-2007, ca 800 m asl; Platania 22-
XII-2007 & 28-XI-2008, ca 1100 m asl; and Mavro Dasos 1-XII-2012, ca 1200 m asl. Probably common, but a
remarkably variable taxon frequently confused with similar-looking species.
Clitocybe obsoleta (Batsch) Quél.
One collection matching the description of this species from a P. brutia forest in Péra Pedí, 10-I-2009, ca 550 m asl.
Also reported by Viney (2005) from collections under Cistus in Karavas, Dec. 2001, but these may belong to C.
cistophila Bon & Contu, instead (Loizides 2016). A number of aniseed-scented Clitocybe species seem to occur in
Cyprus, whose identity is not clear since several early-described taxa have yet to be phylogenetically defined.
Clitocybe odora (Bull.) P. Kumm.
Frequent under both broadleaved and coniferous trees, with several sightings from Calabrian pine ecosystems: Saittás,
9-XII-2007, ca 650 m asl; Péra Pedí, 13-X-2008, ca 650 m asl; Kannavioú, 15-XII-2009, ca 900 m asl; Kelláki, 21-
XII-2009, ca 600 m asl; Kélefos, 8-II-2011, 29-XI-2014, 10-XI-2017 & 1-I-2019, ca 500 m asl.
Clitocybe umbilicata P. Kumm.
Reported by Viney (2005) from Panagra, Dec. 2001.
Basidiomycetes within Pinus brutia ecosystems in Cyprus
5
Clitopaxillus alexandri (Gillet) G. Moreno, Vizzini, Consiglio & P. Alvarado
A distinctive species recently transferred to the new genus Clitopaxillus G. Moreno et al. (Alvarado et al. 2018a),
appearing gregariously in both Calabrian and black pine ecosystems sometimes forming fairy rings: e.g., Trimíklini, 1-
XII-2007, 9-XII-2011, ca 650 m asl; Moniátis, 13-XII-2007, 800 m asl; Mésa Potamós, 18-XII-2007, ca 800 m asl;
Kélefos, 28-XI-2009, ca 500 m asl; Platánia, 26-XII-2009, ca 1100 m asl; Péra Pedí, 14-I-2017, ca 550 m asl. Also
reported by Viney (2005) from Áyios Amvrósios, Dec. 1998, and Loizides et al. (2011) from collections cited above.
*Clitopilus daamsii Noordel.
One collection fruiting on a fallen P. brutia log in Amíantos, 6-I-2014, ca 1100 m asl, matching the description of this
rarely reported taxon. This species is morphologically close to C. hobsoni (Berk.) P.D. Orton, from which it differs by
larger spores, reported as (7)811.5(12.5) × 4.86.6(7) μm in the type collection (Noordeloos 1984), and measuring
(7.5–)8–10.5(11.5) × (4)4.56(7) μm in the Cypriot specimens.
Clitopilus geminus (Paulet) Noordel. & Co-David sensu lato
This widely reported taxon was previously placed in Rhodocybe Maire, but transferred to genus Clitopilus (Fr. ex
Rabenh.) P. Kumm., based on phylogenetic inferences (Co-David et al. 2009). Reported in Cyprus by Viney (2005) as
Rhodocybe gemina”, from pine woods in Panagra, Dec. 2001, and later confirmed by the author from Calabrian pine
woods in Platánia, 20-XI-2008 & 25-XI-2009, ca 1100 m asl, and Akámas, 14-XII-2014, 200 m asl. A couple of variants
seem to occur in Cyprus, whose exact phylogenetic and taxonomic status are not yet clear. Collections from Cistus
matorral are generally smaller, mild scented and feature white mycelial threads, matching the concept of C. geminus
var. subvermicularis (Maire) Noordel. & Co-David, originally described from Mauretania (Maire 1924).
Conocybe albipes Hauskn.
Perhaps better known asC. apala (Fr.) Arnolds, with one collection from Pissouri, 25-I-2009, ca 200 m asl, among
manured grass, in a P. brutia forest opening. First reported by Viney (2005) asBolbitius tener, fruiting in manure-
rich grass in Kalni Dec. 1998.
*Conocybe semiglobata Kühner & Watling
One collection from Calabrian pine woods in Péra Pedí, 2-III-2014, ca 550 m asl. Distribution unclear.
*Coprinellus disseminatus (Pers.) J.E. Lange
A handful of records from mixed forests in Plátres, 20-X-2007, ca 900 m asl; Moniátis, 20-XII-2010 & 14-X-2012, ca
800 m asl; and Platánia, 25-XI-2013, ca 1100 m asl. Uncommon.
Coprinellus domesticus (Bolton) Vilgalys, Hopple & Jacq. Johnson
Just a couple of collections, one from a burned P. brutia forest near Koúrdali, 15-III-2017, ca 800 m asl. Previously
reported by Viney (2005) from Karmi, Nov. 1997, and Loizides et al. (2011). Apparently rare.
Coprinopsis cortinata (J.E. Lange) Gminder
Two collections, one among P. brutia/Cistus litter in Kelláki, 15-III-2012, ca 650 m asl. Also seen in Cistus debris
(Loizides 2016). Apparently rare, but can be easily overlooked.
Coprinus comatus (O.F. Müll.) Pers.
Only sporadically seen in Cyprus, mostly in high elevation P. nigra subsp. pallasiana forest clearings and along forest
paths, with a couple of sightings of from a P. brutia, Platanus orientalis L. and Q. infectoria subsp. veneris forest in
Plátres, 20-X-2007 and 17-X-2008, ca 900 m asl. Also reported by Viney (2005), and Loizides et al. (2011).
Coprinus ovatus (Schaeff.) Fr.
Sparingly seen in late winter and spring, with one record from a mixed forest clearing at Platánia, 27-V-2018, ca 1100
m asl. Also reported by Viney (2005) at ndres, Feb. 2001. Uncommon.
Coprinus spadiceisporus Bogart
Occasionally encountered in and out of forests, with a couple of collections from open P. brutia forests in Pissouri, 30-
I-2011, ca 200 m asl; and Soúni, 26-III-2012, ca 400 m asl. Also reported by Loizides et al. (2011) from thermo-
Mediterranean matorral at Konia, 12-XII-2009.
*Cortinarius anthracinus Fr.
One collection from Mávro Dásos, 5.XII-2012, ca 1100 m asl. Distribution not yet understood.
*Cortinarius decipiens (Pers.) Fr.
One collection from Mávro Dásos, 1-XII-2012, ca 1100 m asl, matching the description of C. atrocoeruleus M.M.
Moser ex M.M. Moser (1967). However, in a revision of sections Hydrocybe and Fraternii, sequenced collections
identified as C. atrocoeruleus”, including the type collection, nested in the same clade as C. decipiens (Pers.) Fr.
(Suárez-Santiago et al. 2009). Until the situation is further clarified, the latter binomial is here tentatively adopted as a
prioritary synonym of the former.
Crinipellis scabella (Alb. & Schwein.) Murrill
A couple of collections on fallen twigs and herbal residue, one in a mossy P. brutia forest in Kélefos, 31-XII-2008, ca
500 m asl. Also reported by Viney (2005) from Geunyeli, Nov. 1997. Rare.
6
Loizides, M.
Cuphophyllus virgineus (Wulfen) Kovalenko
Reported by Viney (2005) from pine forests in Áyios Amvrósios, without date.
*Cystoderma carcharias (Pers.) Fayod
Frequently encountered in Calabrian and black pine forests with collections from Kannavioú, 15.XII-2009, ca 800 m
asl; Mávro Dásos 1-XII-2012, ca 1100 m asl; Plátres 1-XII-2017, ca 1200 m asl.
*Cystoderma fallax A.H. Sm. & Singer
Numerous sightings in both Calabrian and black pine forests, e.g., Plátres, 23-XII-2009, 26-XII-2009 & 19-I-2015, ca
1400 m asl; Platánia, 7-XII-2009, 9-XII-2012 & 2-I-2015, ca 1100 m asl; Mésa Potamós, 2-XII-2017, ca 750 m asl;
Karvounás, 3-XI-2015 & 14-XI-2018, ca 1300 m asl. Collections from Haléfka (Jan. 1998) reported by Viney (2005)
as “Cystoderma amianthinum, probably also belong to this widespread species.
Cystodermella cinnabarina (Alb. & Schwein.) Harmaja
A couple of collections from Platánia, 2-XII-2008 & 9-XII-2009, ca 1100 m asl. Also reported by Viney (2005), as
Cystoderma terreyi”, from Haléfka and Syrianóchori, Dec. 1998. Occassional or uncommon.
*Cystodermella granulosa (Batsch) Harmaja
Occasionally seen Calabrian pine forests, e.g., Moniátis, 13-XII-2007, ca 700 m asl; Péra Pedí, 26-XII-2007, 6-I-2011
& 10-I-2017, ca 550 m asl; Plátres, 1-XII-2017, ca 1200 m asl.
Cystolepiota cystophora (Malençon) Bon
One collection from a mossy Calabrian pine forest at Platánia, 27-XI-2009, ca 1100 m asl. Also reported by Viney
(2005) from Haléfka, Jan. 1999. Distribution not yet understood.
*Cystolepiota seminuda (Lasch) Bon
Just one collection from Platánia, 27-XI-2009, ca 1100 m asl. Apparently rare.
*Entoloma atromadidum A.M. Ainsw. & B. Douglas
Two collections from a mixed P. brutia/Q. alnifolia forest at Kannavioú, 13-XII-2009 & 15-XII-2009, ca 800 m asl,
previously reported as “E. bloxamii (Berk. & Broome) Sacc.(Loizides 2011). Cypriot collections are more likely to
represent the recently described E. atromadidum (Ainsworth et al. 2018), which produces darker basidiomes with
somewhat smaller spores than the epitype of E. bloxamii as reported in Morgado et al. (2013). Rare.
Entoloma cinereo-opacum (Noordel.) Vila, Català & Noordel.s
Sparingly encountered in mossy forest clearings and matorral, such as Moniátis, 9-XII-2007, ca 800 m asl; and Kélefos,
9-XII-2015, ca 500 m asl. Cypriot collections were previously reported as “E. sericeum var. cinereo-opacum Noordel.
in Loizides (2016). However, as shown by Vila et al. (2013), collections previously ascribed to this variant are
phylogenetically distinct and have since been elevated to species rank.
*Entoloma fuscohebes Vila, J. Carbó & F. Caball.
One collection matching the description of this seldomly reported species from Kélefos, 23-XII-2011, ca 500 m asl.
Distribition not yet understood.
Entoloma hirtipes (Schumach.) M.M. Moser sensu lato
A couple of collections keying out as this highly variable taxon, likely to represent a species-complex: Lysós, 18-1-
2009, ca 600 m a.s.l; Kélefos, 8-II-2011, ca 500 m asl. Collections from the pine woods of Haléfka were also reported
by Viney (2005) as “Entoloma aff. hirtipes”, without dates.
*Entoloma incanum (Fr.) Hesler
Two collections from Plátres, 16-X-2012, ca 1250 m asl; and Platánia, 19-VI-2018, ca 1100 m asl. Rare.
Entoloma jubatum (Fr.) P. Karst.
Reported by Viney (2005) from pine woods near Halefka, Jan. 1998, but not verified by the author.
*Entoloma mougeotii (Fr.) Hesler
Two collections matching the description of this taxon, one from a mixed P. brutia/P. orientalis/Q. infectoria subsp.
veneris forest in Plátres, 21-XII-2012, ca 900 m asl. Rare.
*Entoloma pleopodium (Bull.) Noordel.
Three collections of this scented species, two of them from mixed Calabrian pine forests in Plátres, 18-IV-2011 & 1-
V-2017, ca 900 m asl. Rare.
*Entoloma rusticoides (Gillet) Noordel.
One collection in Pissouri, 25-I-2009, ca 200 m asl, matching the description of this taxon. Distribution unclear.
Faerberia carbonaria (Alb. & Schwein.) Pouzar
Reported by Viney (2005) near Áyios Ilaríon, Dec. 2000, but not seen during this 12-y inventory.
*Galerina badipes (Pers.) Kühner
One identified collection from Platánia, 30-XII-2011, ca 1100 m asl. Perhaps widespread but overlooked, as large
numbers of similar-looking Galerina Earle species occur in Cyprus late in the season.
Basidiomycetes within Pinus brutia ecosystems in Cyprus
7
Galerina marginata (Batsch) Kühner
This deadly poisonous fungus inhabits decomposing logs of P. brutia in the thermo- and supra-Mediterranean belts,
but sometimes also found among wooden debris on the ground: Plátres, 24-XI-2008, 6-XI-2011 & 10-XI-2012, ca 800
m asl; Kélefos, 2-XI-2009, ca 500 m asl; Platánia, 10-I-2014 & 2-I-2015, ca 1150 asl; Plátres, 15-XII-2018, 1300 m
asl. Also reported by Loizides et al. (2011), and by Viney (2005) north of Haléfka, Jan. 2002. Occasional.
Galerina vittiformis (Fr.) Singer
Reported by Viney (2005) as “G. vittaeformis, under pine and Cistus, Dec. 1999, without locality. Yet to be verified.
*Gamundia leucophylla (Gillet) H.E. Bigelow
A couple of collections from P. brutia stands in Kelláki, 25-I-2011, ca 600 m asl; and Politikó, 9-I-2012, ca 400 m asl.
Distribution not yet understood.
Geastrum berkeleyi Massee
Reported by Viney (2005) among pine litter at Sirianochóri, Dec. 2001, and by Loizides (2012) from Prastió, 5-III-
2011, ca 550 m asl; and Péra Pedí, 25-III-2011, ca 530 m asl. Probably uncommon.
Geastrum campestre Morgan
Known from a handful of collections under Cistus (Loizides 2012 & 2016), and two collections under P. brutia from
Platánia, 3-XII-2009 & 16-XI-2014, ca 1100 m asl. Occasional.
Geastrum fimbriatum Fr.
Frequently seen in mixed forests, such as Platánia, 22-XII-2007, 7-XII-2009 & 20-XI-2011, ca 1100 m asl; or Plátres,
18-XII-2010, ca 1250 asl. Also reported by Viney (2005) under pines between Áyios Amvrósios and Sirianochóri,
without date, and by Loizides (2012) from collections cited above. Widespread.
Geastrum elegans Vittad.
Sparingly encountered in Cistus matorral (Loizides 2012 & 2016) and open P. brutia forests, such as Kélefos, 21-I-
2010 & 8-I-2011, ca 500 m asl.
*Geastrum michelianum (Sacc.) W.G. Sm.
Previously reported as “G. triplexby Viney (2005), from pine woods north of Haléfka, Jan. 1999; and by Loizides
(2012) from P. brutia woods in Trimíklini, 24-III-2009, ca 650 m asl; and Prast, 25-II-2011, ca 600 m asl. Genetic
studies revealed that “collared” collections previously identified as G. triplexconstitute a species complex, with
European collections corresponding to G. michelianum instead (Kasuya et al. 2012; Zamora et al. 2014). Uncommon.
*Gymnopus androsaceus (L.) Della Magg. & Trassin.
Sparingly seen in black- and Calabrian pine forests, with a couple collections from Moniátis, 23-XI-2007, in riparian
P. brutia, A. orientalis, P. orientalis and Q. alnifolia forest, ca 900 m asl; and Episkopí, 26-I-2018, in an open P.
brutia/C. sempervirens/J. phoenicaea forest, ca 150 m asl. Might be widespread but overlooked.
Gymnopus brassicolens (Romagn.) Antonín & Noordel.
A number of morphologically diverse collections from various habitats currently key out as this taxon, including
collections from mixed Calabrian pine forests in Saittás, 9-XII-2007 & 6-I-2017, ca 600 m asl; Stavrós tis Psókas, 25-
X-2008, ca 1200 m asl; and Kakomállis, 2-XI-2009, ca 900 m asl. Also reported by Viney (2005), as “Micromphale
brassicolens”, from the pine woods of Haléfka, Nov. 2000. More than one species might be involved, but available
sequences of this widely reported taxon are surprisingly scant in public databases.
Gymnopus dryophilus (Bull.) Murrill
A common and widespread species, with collections e.g., from Trimiklini 9-XII-2007, ca 650 m asl; Saittas 1-X-2009,
30-XII-2010 & 29-IX-2011; Kakomallis 31-X-2009, ca 800 m asl; Pera Pedi 10-I-2017, ca 550 m asl. Reported by
Viney (2005), as “Collybia dryophila”, without date and locality.
*Gymnopus hybridus (Kühner & Romagn.) Antonín & Noordel.
Not often reported in literature but frequently seen in Cyprus, mostly in mixed P. brutia/Q. alnifolia forests in Plátres,
10-XII-2009 & 11-XII-2012, ca 1200 m asl; Cedar Valley, 27-XII-2010 & 22-XI-2011, ca 1200 m asl; or Platánia, 20-
XI-2011 & 16-XI-2014, ca 1100 m asl.
Hebeloma crustuliniforme (Bull.) Quél.
One of several Hebeloma (Fr.) P. Kumm. species occurring on the island, frequently encountered in all kinds of forests,
e.g., Mávro Dásos, 1-XII-2012, ca 1200 m asl. See Beker et al. (2016) for sequenced collections.
Hebeloma cylindrosporum Romagn.
Known from just one collection from Platánia 3-XII-2012, ca 1100 asl (Beker et al. 2016). Rare.
Hebeloma sinapizans (Paulet) Gillet
Perhaps the most widespread Hebeloma species on the island, seen in large numbers in P. nigra subsp. pallasiana
forests, but also in mixed P. brutia/Q. alnifolia forests: e.g., Kyperoúnda, 3-XII-2012, ca 1200 m asl; Platánia, 9-XII-
2012, 1100 m asl; Mávro Dásos, 20-XI-2015, ca 1200 m asl (for further collection details and a full description see
Beker et al. 2016).
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Loizides, M.
Hebeloma subtortum P. Karst.
Perhaps better known as H. sordidum Maire, this ecologically versatile fungus was reported by Beker et al. (2016)
and further collected by the author in mixed P. brutia forests in Platánia, 25-XI-2013, ca 1100 m asl; and Plátres, 3-
XII-2017, ca 1200 m asl. Occasional.
*Hemimycena lactea (Pers.) Singer
Few collections, e.g., Platánia, 25-XI-2009 & 20-XI-2011, ca 1100 m asl; Amíantos, 2-X-2009, ca 1300 m asl. Probably
widespread but overlooked.
*Hemimycena pseudogracilis (Kühner & Maire) Singer
Two collections from Kélefos, 8-I-2011, ca 450 m asl; and Platánia, 25-X-2012, ca 1100 m asl key out as this poorly
known and variously interpreted taxon, although neither the macro- nor micromorphological features are a perfect fit.
Cypriot collections might represent an undescribed Mediterranean lookalike.
Hydnellum dianthifolium Loizides, Arnolds & P.-A. Moreau
A new collection and locality of this very rare species, seen in Kélefos, 5-III-2019, ca 500 m asl, leg. C. Hobart.
Previously known only from three collections in Cyprus and one collection in southern Italy (Puglia). See Loizides et
al. (2016) for a detailed description and previous collections’ details.
Hydnellum ferrugineum (Fr.) P. Karst. sensu lato
Common in P. nigra subsp. pallasiana forests in years with early rainfall, but sometimes also seen in mixed P. brutia/Q.
alnifolia forests, e.g., Karvounás, 13-X-2011, ca 1300 m asl; and once documented in a P. brutia/Q. coccifera subsp.
calliprinos forest in Kélefos, 2-XI-2012, ca 500 m asl (Loizides 2011). Multiple phylogenetic lineages are currently
identified as this taxon in public databases (Loizides et al. 2016; Larsson et al. 2019), which are currently the object of
a dedicated study (Loizides et al. in prep.).
*Hygrocybe calciphila Arnolds
One collection from a mossy P. brutia forest clearing at Kélefos, 23-XII-2012, ca 450 m asl. A rare species, proposed
for conservation in the Global Fungal Red List Initiative.
Hygrocybe conica (Schaeff.) P. Kumm. sensu lato
This widely applied binomial currently lumps multiple phylospecies yet to be taxonomically resolved. Several species
of this complex are apparently present in Cyprus, one of them regularly occurring in black- and Calabrian pine forests
e.g., in Platánia, 2-XII-2008 & 23-XII-2018, ca 1150 m asl; or Madarí, 30-XI-2015, ca 1000 m asl.
*Hygrocybe konradii R. Haller Aar.
One collection matching the concept of this species from a mixed forest in Kannavioú, 13-XII-2009, ca 900 m asl.
*Hygrophorocybe nivea (Velen.) Vizzini & Contu
A couple of collections from P. brutia/Q. alnifolia forests at Platánia, 27-XI-2009 & 16-XI-2012, ca 1100 m asl. The
monotypic genus Hygrophorocybe Vizzini & Contu was proposed to accommodate Clitocybe nivea Velen. (Vizzini
2014), a striking species with ellipsoid to sublacrymoid spores and hygrophoroid basidia. Spores measure 8–10 × 4.5
5.5 μm in the Cypriot collections. Rare, known only from one locality.
Hygrophorus meridionalis Loizides, P.-A. Moreau, Athanassiou & Athanasiades
Numerous sightings of this common Mediterranean species, described as new to science in 2018. See Moreau et al.
(2018) for a detailed description and extensive collection details.
Infundibulicybe costata (Kühner & Romagn.) Harmaj
A couple of collections from Calabrian pine forests in Kélefos, 31-XII-2008 & 29-XI-2014, ca 500 m asl. Previously
reported by Viney (2005), as “Clitocybe costata”, under pines between Haléfka and Syrianóchori, Dec. 2000; and by
Loizides et al. (2011, also as “C. costata”) from collections cited above. Uncommon.
Infundibulicybe geotropa (Bull.) Harmaja
Occasionally appearing late in the autumn and winter in wet riparian forests and mixed forest clearings, with few
collections from Plátres, e.g., 9-XII-2007 & 21-XI-2012, ca 900 m asl; and Platánia, 20-XI-2007, 3-XII-2009 & 30-
XII-2011, ca 1100 m asl. Infundibulicybe gigas (Harmaja) Harmaja, a taxon described from Finland (as Clitocybe
gigas”, Harmaja 1978), is reported to have a deeply infundibuliform pileus, denser lamellae, a squat stipe and
±lacrymoid spores, and does not appear to occur in Cyprus. The phylogenetic and taxonomic status of Clitocybe maxima
(P. Gaertn., G. Mey. & Scherb.) P. Kumm., sometimes consedered a synonym of either I. geotropa or I. gibba, is as yet
unclear.
*Infundibulicybe mediterranea Vizzini, Contu & Musumeci
A widespread species commonly seen in high-altitude P. nigra subsp. pallasiana forests, but frequently also in meso-
and supra-Meditarranean P. brutia forests, e.g., Stavrós tis Psókas, 25-X-2008, ca 1200 m asl; Platánia, 30-XII-2011,
ca 1100 m asl; Cedar Valley, 29-XI-2017, ca 1100 m asl; and Plátres, 30-XII-2017, ca 1200 m.
*Infundibulicybe meridionalis (Bon) Pérez-De-Greg.
Frequently encountered in Calabrian pine forests, such as Plátres, 21-XI-2007, ca 1200 m asl; Moniátis, 28-XI-2008 &
Basidiomycetes within Pinus brutia ecosystems in Cyprus
9
26-I-2009, ca 900 m asl; Mávro Dásos, 5-XII-2012, ca 1000 m asl; Péra Pedí, 14-I-2017, ca 600 m asl. Very similar to
I. squamulosa but with considerably larger spores, measuring 7–9 × 4.5–6 μm in the Cypriot collections.
*Infundibulicybe squamulosa (Pers.) Harmaja
A handful of collections from Platánia, 30-XII-2011 & 6-I-2014, ca 1100 m asl;rgos Tyllirías, 10-I-2011, ca 350 m
asl; and Plátres, 19-ΧΙ-2011 & 1-XII-2017, ca 1250 m asl. Distribution not quite clear, as a number of morphologically
very similar species co-occur on the island, difficult to distinguish in the field.
Inocybe flocculosa Sacc. sensu lato
A number of collections from diverse habitats match descriptions of this taxon, currently encompassing multiple
phylospecies: e.g., Péra Pedí, 29-XI-2011, ca 450 m asl; and Plátres, 21-XI-2012, ca 900 m asl. Previously reported by
Viney (2005), Loizides & Kyriakou (2011), Loizides et al. (2011), and Loizides (2016). It is unclear whether a
collection reported by Viney (2005) as “I. flocculosa var. crocifolia” corresponds to the same taxon or not.
*Inocybe fuscidula Velen.
One tentatively identified collection from a mossy bank in a P. brutia forest in Péra Pedí, 18-III-2011, ca 600 m asl.
Distribution unclear.
Inocybe geophylla (Bull.) P. Kumm. sensu lato
This widely applied binomial is polyphyletic and yet to be taxonomically resolved (Ryberg et al. 2008). More than one
species of this complex are present in Cyprus, with collections from, e.g. Calabrian pine forests in Moniátis, 25-XI-
2009, ca 900 m asl; Platánia, 27-XI-2009, ca 1100 m asl; or Kélefos, 2-XI-2009, 29-XI-2009 & 9-XII-2014, ca 450
500 m asl. A lilac counterpart also occurs on the island, previously reported as “I. geophylla var. lilacina (Peck) Gillet
in Loizides et al. (2011), e.g., from Amíantos, 10-X-2009, ca 1300 m asl. The latter variant, however, was recently
recombined as a distinct species following sequencing the holotype and appears to be restricted to the American
continent (Matheny & Swenie 2018). Large-scale genetic studies are needed to ultimately clarify this difficult species-
complex in Europe.
*Inocybe griseolilacina J.E. Lange
One collection from a P. brutia/Q. coccifera subsp. calliprinos forest in Kélefos, 19-XI-2009, ca 450 m asl.
Inocybe griseovelata Kühner
Reported by Viney (2005) under pines near Mýrtou, Jan. 2000, but not so far confirmed by the author.
*Inocybe hirtella Bres.
Several collections of this bitter-almond scented species, equally frequent in Calabrian and black pine forests, such as
Plátres, 23-XII-2009, ca 1300 m asl; Soúni, 28-VI-2010, ca 400 m asl; Pýrgos Tyllirías, 10-I-2011, ca 350 m asl; or
Pissouri, 2-I-2012, ca 200 m asl. Widespread.
Inocybe lacera (Fr.) P. Kumm. sensu lato
A couple of collections key out as this variously interpreted taxon, e.g., from Calabrian pine forests at Kélefos, 2-I-
2009, ca 450 m asl. Also reported by Viney (2005) from pine woods west of Haléfka, Feb. 1998. Several forms and
varieties have been described in literature, whose systematic position are not yet clarified.
*Inocybe langei R. Heim
Few late winter or early spring sightings in thermo-Mediterranean Calabrian pine forests, e.g., Prastió, 22-III-2011, ca
600 m asl; and Pissouri, 2-I-2012, ca 200 m asl. Occasional or locally frequent in some years.
*Inocybe muricellata Bres.
One collection found in a mixed P. brutia/Q. coccifera subsp. calliprinos forest in Kélefos, 23-XII-2012, ca 500 m asl.
Likely rare.
*Inocybe obscura (Fr.) Quél. sensu auct.
One record on a mossy bank under P. brutia and P. pinea L. near Yiolou, ca 300 m asl. This collection fits the invalidly
published taxon I. obscura Gilletss. auct., tentatively treated as a synonym of I. cincinnata. Taxonomy within this
group of violet-stiped Inocybes is in need of phylogenetic revision. Distribution unclear.
Inocybe obscurobadia (J. Favre) Grund & D.E. Stuntz
Reported by Viney (2005) from pine woods near Mýrtou, Jan. 2000, but basidiomes depicted in this photograph
resemble rather I. furfurea Kühner, erroneously regarded as a synonym in the past. It is also unclear whether collections
matching the description under Cistus (Loizides 2016), sometimes reported as I. tenuicystidiata E. Horak & Stangl
(e.g., Esteve-Raventós et al. 2002), are conspecific or distinct from I. obscurobadia ss. str., as nomenclature within this
cluster has not yet been resolved.
*Inocybe phaeoleuca Kühner
One collection from a mossy P. brutia/P. orientalis forest in Plátres, 21-XI-2012, ca 900 m asl. Distribution unclear.
Inocybe posterula (Britzelm.) Sacc.
Several collections from Calabrian and black pine forests, e.g., Saittás, 4-XII-2008, ca 700 m asl; Kélefos, 27-XII-
2008, ca 450 m asl; and Platánia, 27-XII-2009 & 2-I-2015, ca 1100 m asl, previously reported in Loizides et al. (2011).
10
Loizides, M.
Widespread.
*Inocybe tarda Kühner
Three collections from mixed woodlands at Kélefos, 21-XI-2011, ca 450 m asl; Ayía Paraskeví, 23-XI-2011, ca 600 m
asl; and Plátres, 21-XI-2012, ca 900 m asl, match the description of this species. It is unclear whether a collection
labelled as Inocybe aff. nitidiuscula” by Viney (2005) corresponds to the same species, since some authors (e.g.,
Kuyper 1986; Stangl 1999) consider the two taxa as synonymous, and others (e.g., Kühner R. 1955; Eyssatier & Roux
2011) as distinct.
*Inocybe tenebrosa Quél.
Just two collections of this distinctive species, notable for its unusual banana odour, one from a P. brutia forest opening
at Platánia, 27-XI-2009, ca 1100 m asl. Rare.
Inocybe vulpinella Bruyl.
Occasionally seen in thermo-Mediterranean pine forests and matorral, such as Klirou, 5-II-2012, ca 400 m asl.
Previously reported by Loizides (2016) from collections under Cistus.
Inosperma bongardii (Weinm.) Matheny & Esteve-Rav.
Recently transferred from Inocybe (Fr.) Fr. to genus Inosperma (Kühner) Matheny & Esteve-Rav., based on multigene
phylogenies (Matheny et al. 2020). One collection from Archimandrita, 2-VI-2011, ca 450 m asl, leg. T. Alexandridis,
previously reported as “Inocybe bongardiiin Loizides et al. (2011). A collection from pine forests in Haléfka, Feb.
1999, was reported by Viney (2005) as “Inocybe aff. bongardii”. Rare.
*Inosperma cervicolor (Pers.) Matheny & Esteve-Rav.
A number of ecologically diverse collections currently key out as this species, originating from mixed P. brutia/Q.
alnifolia forests in Plátres, 2-I-2010, 1200 m asl; a grassy P. brutia/Ceratonia siliqua forest opening in Pissouri, 30-I-
2011, ca 200 m asl; as well as mixed P. brutia/Q. coccifera subsp. calliprinos forests in Kélefos, 8-II-2011, ca 550 m
asl; and Prastió, 25-II-2011, ca 600 m asl. Distribution not yet understood.
Lacrymaria lacrymabunda (Bull.) Pat.
The “weeping widow” is rarely seen in Cyprus, with one collection originating from a recently burned P. brutia forest
in Pelendri, 11-III-2010, ca 800 m asl. Also reported by Viney (2005) as “Psathyrella lacrymabunda”, among pine
litter in Karmi, Dec. 2000.
Lactarius deliciosus (L.) Gray
One of the most widespread and commonly occurring fungi in Cyprus, frantically collected for the table by the locals
and sold in markets throughout the country. Fruiting prolifically on serpentine and acidic substrates in high-altitude P.
nigra subsp. pallasiana forests, but is also locally frequent in lower altitudes under P. brutia, e.g. in Moniátis ,13-XII-
2007, ca 700 m asl; Millomeri, 13-XI-2008, ca 800 m asl; Mésa Potamós, 24-XII-2008, 17-IX-2009 & 20-XII-2009,
ca 900 m asl; Amíantos, 3-X-2009, ca 1300 m asl; Plátres, 20-XI-2007, 23-XII-2009, 17-XII-2011, 17-XI-2012, 19-I-
2015, 1-XII-2017 & 17-X-2018, ca 1200 m asl; Stavrós tis Psókas, 22-XI-2011, ca 1200 m asl; Mávro Dásos, 1-XII-
2012, 28-XI-2015 & 3-XII-2015, ca 1200 m asl; Platánia, 1-XII-2009, 21-XII-2011 & 26-XII-2018, ca 1100 m asl;
Karvounás, 14-XI-2018, ca 1300 m asl. First reported in Cyprus by Nattrass (1937), and subsequently by Viney (2005),
Loizides (2008), and Loizides et al. (2011).
Lactarius sanguifluus (Paulet) Fr.
Mostly occurring in P. nigra subsp. pallasiana ecosystems in Cyprus, with only rare sightings in P. brutia forests, such
as Platánia, 9-XII-2012, ca 1150 m asl; and Plátres, 17-XII-2012, ca 1200 m asl. Common in some years.
Lactarius semisanguifluus R. Heim & Leclair
More widespread than L. deliciosus, growing prolifically in a variety of calcareous habitats in the thermo-, meso- and
supra-Mediterranean belts, typically (but not exclusively) in the presence of P. brutia: e.g. Kélefos, 23-X-2007, 29-X-
2007, 29-XI-2009, 9-II-2011, 2-XII-2014, 24-XI-2017 & 1-I-2019, ca 450 m asl; Péra Pedí, 20-XI-2007, 13-X-2008,
7-I-2016, 10-I-2017 & 19-I-2019, ca 600 m asl; Kakomállis, 29-X-2009, ca 700 m asl; Pareklisiá, 11-I-2011, ca 150 m
asl; Mosfilotí, 23-I-2011, ca 250 m asl; Mávro Dásos, 1-XII-2012, ca 1100 m asl; Akámas, 14-XII-2014, ca 200 m asl;
Akrotíri, 17-I-2015, ca 20 m asl. Very common.
*Lentinellus cystidiosus R.H. Petersen
Frequently seen on fallen P. brutia twigs and branches, such as Péra Pedí, 24-XII-2008, 7-XI-2009 & 10-I-2017, ca
550 m asl; Akámas, 14-I-2009, ca 200 m asl; Kakomállis, 2-XI-2009, ca 900 m asl.
*Lepiota alba (Bres.) Sacc.
Documented in Kélefos, 10-XI-2017, ca 500 m asl. It is as yet uncertain whether L. erminea (Fr.) P. Kumm., often
segregated on the basis of a raphanoid odour and longer spores (e.g., Huijsman 1943), is a synonym of this taxon.
Collections from high altitude P. nigra subsp. pallasiana forests in Troodos were previously reported under the latter
binomial (Loizides et al. 2011) and appear to be morphologically distinct.
Lepiota brunneoincarnata Chodat & C. Martín
This deadly poisonous species is not occasionally seen in Cyprus, with collections from various habitats (Loizides et
Basidiomycetes within Pinus brutia ecosystems in Cyprus
11
al. 2011) including P. brutia forests in Platánia, 27-XI-2008 & 7-XII-2009, ca 1100 m asl; and Kélefos, 29-X-2012, ca
500 m asl.
Lepiota castanea Quél.
Also a deadly poisonous species, with few records from Calabrian pine woods in Moniátis, 13-XII-2007, ca 700 m asl;
Plátres, 24-XI-2007, ca 900 m asl; Platánia, 20-XI-2008 & 27-XI-2008, ca 1100 m asl; and Mosfilotí, 23-I-2011, ca
250 m asl. Occasional.
Lepiota clypeolaria (Bull.) P. Kumm. sensu lato
Few collections match this frequently reported taxon, which presently occupies more than one clade in phylogenetic
analyses (Caballero et al. 2015; Vizzini et al. 2019). Found in a variety of habitats in Cyprus, mostly mixed Calabrian
pine forests in Platánia, 3-XII-2009 & 16-XI-2014, ca 1100 m asl; and Karvounás, 16-X-2011, ca 1200 m asl. A
collection north of Haléfka, Jan. 2002, was also reported as “Lepiota aff. clypeolariaby Viney (2005).
Lepiota cristata (Bolton) P. Kumm.
Sparingly appearing in black- and Calabrian pine forests, including a collection from Platánia, 27-XI-2008, ca 1100 m
asl. Quite rare.
Lepiota echinella Quél. & G.E. Bernard
A couple of collections from Calabrian pine woods in Ayía Paraskeví, 11-XI-2009, ca 550 m asl; and Péra Vása, 7-XI-
2012, ca 700 m asl. Also seen once in black pine forests, but generally uncommon or rare.
*Lepiota forquignoni Quél.
Known only from one collection at Mosfilotí, 23-I-2011, ca 250 m asl. Rare.
Lepiota griseovirens Maire
Reported by Loizides et al. (2011) from two collections in different localities at Kélefos, both on 20-XI-2009 in P.
brutia/Platanus orientalis L. forests, ca 450 m asl. Rare.
*Lepiota lepida Guinb. & M. Bodin
Two collections of this rarely reported species from Platánia, 1-XII-2009 & 3-X-2018, in mixed P. brutia forest
opening, ca 1100 m asl. The spores of the Cypriot collections measure 6–7 × 3–4 μm.
*Lepiota pseudohelveola Kühner
A couple of collections match the concept of species from Kélefos, 28-XI-2009, in mixed P. brutia/Q. coccifera subsp.
calliprinos forest, ca 500 m asl; and Péra Pedí, 14-I-2017, in P. brutia forest, ca 600 m asl. More than one species of
this cluster are present in Cyprus, but it is yet unclear whether L. pseudolilacea is a synonym of this taxon.
Lepiota pseudolilacea Huijsman
Seen in a grassy P. brutia forest clearing in Saittás, in 5-X-2008, 7-X-2009, 30-XII-2010, 29-IX-2011 and 16-X-2012.
Lepiota lilacea Bres. also occurs in Cyprus and is very similar, but has smaller spores and is typically found outside of
forests (Loizides et al. 2011).
Lepiota subgracilis Kühner
Previously reported by Loizides et al. (2011) from a couple of collections in mixed P. brutia/Q. coccifera subsp.
calliprinos forests in Kélefos, ca 500 m asl; and Péra Pedí, 28-XI-2009, ca 550 m asl. Lepiota kuehneri Huijsman ex
Hora, L. kuehneriana Locq., Lepiota latispora (Kühner ex Wasser) Bon, and L. wasseri Bon are probably all synonyms
of this taxon (Vellinga 2001). Infrequently seen.
Lepiota subincarnata J.E. Lange
An occasionally encountered woodland dweller, with collections from Kélefos, 27-XI-2007, 29-XI-2009 & 8-I-2011,
in a riparian P. brutia/Platanus orientalis forest, ca 450 m asl; Platánia, 5-XII-2009, in P. brutia forest, ca 1200 m asl;
and Stavrós tis Psókas, 20-XI-2017, 1100 m asl in mixed P. brutia forest. Deadly poisonous.
Lepiota sublaevigata Bon & Boiffard
Occasionally seen in thermo-Mediterranean P. brutia forests and Cistus matorral, e.g., Péra Pedí, 7-XI-2009, ca 550 m
asl; Kélefos, 10-XI-2017, ca 500 m asl.
Lepista nuda (Bull.) Cooke sensu lato
A common and widespread woodland dweller found in various habitats in Cyprus, with numerous collections from P.
brutia forests in Plátres, 21-XI-2007, 1-XII-2009, 24-XI-2012 & 3-XII-2018, ca 1100 m asl; Moniátis, 9-XII-2009, ca
900 m asl; Platánia, 20-XI-2008, 23-XI-2009, 27-XI-2009, 30-XII-2014, 20-XI-2015, 26-XII-2018, ca 1100 m asl;
Stavrós tis Psókas, 18-XI-2009, ca 1200 m asl; Saittás, 6-I-2017, ca 700 m asl. Also reported by Viney (2005) from
pine woods around Kyrenia and Haléfka. See further notes under L. sordida.
*Lepista panaeolus (Fr.) P. Karst.
Just two collections of this rare species in Cyprus, both from grassy P. brutia forest openings in Akámas, 4-I-2011 &
14-ΧΙΙ-2014, ca 200 m asl.
Lepista sordida (Schumach.) Singer sensu lato
Very common in a variety of habitats, especially grassy, low-elevation Calabrian pine wood openings: e.g., Pissouri,
12
Loizides, M.
12-II-2007, 30-I-2011 & 2-I-2012, ca 200 m asl; Saittás, 13-XII-2007, 700 m asl; Mosfilotí, 6-I-2009 & 23-I-2011, ca
250 asl; Péra Vása, 8-II-2015, ca 600 m asl. Multiple lineages identified as L. nuda and L. sordida seem to be be present
in phylogenetic trees, therefore these two widely applied binomials might further split in the future and taxonomic
revisions are to be expected (Alvarado et al. 2015).
*Leucoagaricus georginae (W.G. Sm.) Candusso
One collection from Platánia, 25-X-2012, in a mossy P. brutia/C. sempervirens forest clearing, ca 1100 m asl. Rare.
Leucoagaricus melanotrichus (Malençon & Bertault) Trimbach
One collection from a P. brutia forest in Ayía Paraskeví, 11-XI-2009, ca 600 m asl. Also reported in Loizides (2016)
from a collection under Cistus in a P. brutia/C. brevifolia forest at Tripilos, 18-XI-2009, ca 1100 m a.s.l. Rare.
Leucopaxillus gentianeus (Quél.) Kotl.
Among the commonest fungi in Cyprus, occurring abundantly in a variety of habitats including mixed P. brutia forests
in Platánia 3-XII-2009, 3-XII-2012 & 26-I-2018, ca 110 m asl; Plátres, 23-XII-2009, 7-XII-2012, 11-XII-2012, 17-
XII-2012 & 1-XII-2017, ca 1200 m asl; Stavrós tis Psókas, 18-XI-2009 & 22-XI-2011, ca 1200 m asl; or Mávro Dásos,
5-XII-2012, ca 1000 m asl.
Leucopaxillus malenconii Bon
Two collections fit the description of this Mediterranean species previously reported in Loizides et al. (2011): one from
a riparian P. orientalis, Alnus orientalis and P. brutia forest in Moniátis, 9-XII-2007, ca 850 m asl; and one from a P.
brutia forest in Platánia, 5-XII-2009, ca 1200 m asl. Rare.
Limacella illinita (Fr.) Maire
Few sightings in Plátres 15-XI-2007 & 25-XI-2009, ca 1150 m asl; Trimíklini, 20-XII-2008, ca 650 m asl; Saittás, 10-
I-2017, ca 700 m asl, all in P. brutia forests, with some collections corresponding to “f. ochracea” characterized by
ochraceous tinges on the pileus. Also reported by Viney (2005) from pine woods near Áyios Ilaríon, Dec. 2000.
Limacella subfurnacea Contu sensu auct.
Occasionally seen in and out of forests, with one collection from a P. brutia forest edge in Finikária, 20-I-2011, ca 200
m asl. Previously reported by Viney (2005) from pine woods in Haléfka (Dec. 1998), and Ayía Iríni (Dec. 2000).
Limacella grisea Singer (1989) might be an earlier name for this species.
Lycoperdon atropurpureum Vittad.
One collection in a mossy P. brutia forest in Kélefos, 31-X-2012, ca 500 m asl. Also reported from Áyios Mámas, 10-
III-2012, ca 500 m asl, among Cistus litter in a P. brutia forest clearing (Loizides 2016). Distribution unclear.
Lycoperdon excipuliforme (Scop.) Pers.
One collection from an open P. brutia forest in Pareklisiá, 14-II-2009, ca 200 m asl. Probably rare.
*Lycoperdon lividum Pers.
Occasionally encountered, such as in open P. brutia forests at Kélefos, 10-XI-2017, ca 500 m asl.
Lycoperdon molle Pers.
A couple of collections from P. brutia forests in Saittás, 30-XII-2010 & 28-X-2011, ca 700 m asl. Distribution not quite
understood, since its distinction from L. umbrinum, L. subumbrinum and L. umbrinoides is not straight forward.
Lycoperdon perlatum Pers.
Frequently encountered in black- and Calabrian pine forests, e.g., Saittás, 13-XII-2007, ca 700 m asl; Plátres, 27-X-
2008, ca 1200 m asl; Trimíklini, 9-XII-2008, ca 650 m asl; Kélefos, 29-XI-2014 & 24-XI-2017, ca 500 m asl. Also
reported by Viney (2005), without date, from the pine woods of Haléfka; by Loizides et al. (2011) from collections
cited above; and by Loizides (2016) from Cistus matorral in Kalavasyós.
Lycoperdon pratense Pers.
Previously reported by Viney (2005) as “Vascellum pratense”, this puffball is usually found in fields or woodland
edges. A couple of sightings from P. brutia forest clearings in Prastió, 5-III-2011, ca 550 m asl; and Akámas, 18-XII-
2014, ca 200 m asl.
*Lycoperdon umbrinum Pers.
A couple of collections from a mixed P. brutia/Q. coccifera subsp. calliprinos forest in Kelefos, 2-XI-2012, ca 500 m
asl; and a P. brutia forest in Prastio 6-III-2012, ca 550 m asl. Distribution not yet understood.
Lyophyllum fumosum (Pers.) P.D. Orton
A morphologically variable and ecologically versatile species found in diverse ecosystems in Cyprus, including P.
brutia forests in, e.g., Saittás, 25-XI-2007, 1-XII-2011 & 12-XII-2011, ca 700 m asl; Amíantos, 10-X-2009, ca 1300 m
asl; and Plátres, 20-XII-2009 & 11-XII-2012, ca 12001300 m asl. Previously reported by Loizides et al. (2011) from
collections cited above, and Loizides (2016) from Cistus matorral. Lyophyllum cistophilum Vila & Llimona, L.
phaeophyllum Vila & Llimona, and L. subglobisporum Consiglio & Contu, might be synonyms of this taxon.
Collections previously reported by Viney (2005) as Lyophyllum decastes (Fr.) Singer”, probably also correspond to
this widespread species.
Basidiomycetes within Pinus brutia ecosystems in Cyprus
13
*Lyophyllum loricatum (Fr.) Kühner
Just three collections all late in the season, two of them from mixed P. brutia/P. orientalis forests at Platánia, 25-XI-
2013 & 26-XII-2018, ca 1100 m asl. Apparently rare.
*Macrocystidia cucumis (Pers.) Joss.
The “cucumber cap” is sparingly seen in black- and Calabrian pine forests: Platánia, 9-XII-2009, ca 1100 m asl; Ayía
Paraskeví, 18-II-2011, ca 550 m asl; Akámas, 15-I-2016, ca 200 m asl; Plátres, 1-XII-2017, ca 1200 m asl.
Macrolepiota excoriata (Schaeff.) Wasser
Frequently encountered in thermo-Mediterranean Calabrian pine wood edges and grassy wood openings, e.g., in
Kélefos, 3-XII-2008, ca 500 m asl; Akámas, 14-I-2009, 200 m asl; Kalavasos, 14-II-2011, ca 180 m asl; Péra Pedí, 10-
I-2017, ca 600 m asl (Loizides et al. 2011).
*Macrolepiota mastoidea (Fr.) Singer
So far only seen in Calabrian pine forests of the Akámas Peninsulla where it appears in large numbers locally, e.g., 28-
XI-2009, ca 200 m asl. Rare or altogether absent elsewhere on the island.
*Macrolepiota procera f. permixta (Barla) Vizzini & Contu
Just one collection from a P. brutia forest opening in Karvounás, 20-XI-2015, ca 1200 m asl. This form, characterised
by the vinaceous-red bruising of basidiomes, was previously regarded as a distinct species (Pacioni 1979; Breitenbach
& Kränzlin 1991; Vellinga EC. 2001). However, as shown by Vizzini et al. (2011), this character has no phylogenetic
basis and collections identified as this species (including the epitype collection), nest in the M. procera (Scop.) Singer
clade. Evidently very rare in Cyprus, not a species to go unnoticed.
*Macrolepiota subsquarrosa (Locq.) Bon
Several collections match the description of this species, e.g., from P. brutia forests in Plátres, 20-XI-2007 & 27-X-
2012, ca 10001300 m asl; P. brutia/Q. coccifera subsp. calliprinos forests in Kélefos, 20-XI-2009 & 21-I-2015, ca
500 m asl; and P. brutia forests at Kykkos, 29-XI-2017, ca 1200 m asl. Perhaps widespread, but the phylogenetic
identity of this taxon has not yet been fully clarified and is often difficult to distinguish from the similar M. excoriata
and M. mastoidea.
Mallocybe dulcamara (Pers.) Vizzini, Maggiora, Tolaini & Ercole. sensu auct.
A variously interpreted spring taxon whose taxonomic identity is yet to be fully resolved (Matheny et al. 2020).
Reported by Viney (2005) from Karmi as “Inocybe dulcamara”, May 2000. Collections from a mixed P. brutia/A.
andrachne/Q. coccifera subsp. calliprinos forest in Prastió, 22-III-2011, ca 550 m asl, match the description of this
taxon, but the current combination might be invalid as per Art. 41(1) of ICN (Turland et al. 2018).
Marasmius wynneae Berk. & Broome
Very common and widespread, found in various habitats and elevations including P. brutia forests in, e.g., Pissouri,
15-I-2008 & 2-I-2012, ca 200 m asl; or Pareklisiá, 14-II-2009 & 25-I-2011, ca 200 m asl. Also reported by Viney
(2005) from Haléfka, Dec. 1998.
Melanoleuca exscissa (Fr.) Singer
Often seen in grassy areas at lower elevations, with at least one collection in a P. brutia wood opening in Péra Pedí, 1-
III-2013, ca 550 asl. Previously reported by Viney (2005) from Panagra, Dec. 2004. Possibly widespread, but the
morphological identification of Melanoleuca Pat. species is far too complicated to draw reliable conclusions.
*Melanoleuca iris Kühner
One collection from a grassy P. brutia forest in Pareklisiá, 18-II-2009, ca 200 m asl. Distribution unclear.
Mycena amicta (Fr.) Quél.
Commonly seen among pine litter, or on logs, pine cones and wooden debris, e.g., in Calabrian pine woods in Saittás,
29-X-2008, ca 700 m asl; Akámas, 4-I-2011, ca 200 m asl; or Moniátis, 12-XII-2011, ca 700 m asl. Also reported by
Viney (2005) from Kyrenia, Jan. 2000.
Mycena arcangeliana Bres.
Reported by Viney as M. oortiana(2005) and occasionally seen on fallen logs and tree stumps, e.g., in a mixed
Cedrus brevifolia/P. brutia/Q. alnifolia forest in Cedar Valley, 27-XII-2010, ca 1100 m asl; or in mixed P. brutia/Q.
alnifolia/A. andrachne forests in Platánia, 9-XII-2012, ca 1100 m asl.
*Mycena capillaripes Peck
Many sightings from mixed Calabrian pine forests, e.g., in Saittás, 24-XII-2010, ca 650 m asl; Akámas, 4-I-2011, ca
200 m asl; and Amíantos, 19-XI-2013, ca 1200 m asl. Common and widespread.
*Mycena clavicularis (Fr.) Gillet
Appearing in vast numbers in wet P. brutia forests during the autumn and winter months, such as: Moniátis, 22-XII-
2010, ca 900 m asl; Kannavioú, 27-XII-2010, ca 900 m asl; Kelláki, 25-I-2011, ca 600 m asl; or Plátres, 11-XII-2012,
26-XI-2014 & 1-XII-2017, ca 1200 m asl. Very common and widespread.
14
Loizides, M.
*Mycena epipterygia (Scop.) Gray sensu lato
Several varieties of this fungus have been described in literature, whose phylogenetic and taxonomic status remain
unclear. Few collections corresponding to some of these variants originate from P. brutia forests in Cyprus, such as
Mésa Potamós, 20-XII-2007, 7-I-2009 & 17-XII-2009, ca 700 m asl; Platánia, 7-XII-2009, 9-XII-2009 & 30-XII-2011,
ca 1100 m asl; and Plátres, 6-I-2017, ca 1200 m asl.
*Mycena flavescens Velen.
One collection in a mixed P. brutia/Q. alnifolia/P. orientalis forest in Platánia, 30-XII-2011, ca 1100m asl. Distribution
unclear.
Mycena galopus (Pers.) P. Kumm.
Reported by Viney (2005), without dates or localities, and only sparingly seen by the author: Trimíklini, 30-XII-2007,
in P. brutia forest, ca 650 m asl; Kélefos, 21-XI-2011, in a riparian P. brutia/P. orientalis/A. orientalis forest, ca 450
m asl. Distribution unclear, as several forms and varieties are described in literature.
*Mycena haematopus (Pers.) P. Kumm.
Rare, known only from two collections, one in a riparian P. brutia/P. orientalis/A. orientalis forest at Kélefos, 21-XI-
2011, ca 450 m asl.
*Mycena mirata (Peck) Sacc.
One collection keying out as this species, albeit with larger spores than those mentioned in literature, measuring 1115
× 5.57.5 μm in the Cypriot specimens. Found in a mixed P. brutia/Q. alnifolia/A. andrachne forest in Platánia, 21-
XII-2011, ca 1100 m asl. Distribution unknown.
*Mycena pseudopicta (J.E. Lange) Kühner
One collection from Kélefos, 2-I-2009, in a mossy P. brutia forest, ca 550 m asl. Apparently rare.
Mycena pura (Pers.) P. Kumm. sensu lato
Numerous collections belonging to this species-cluster, shown by Harder et al. (2010, 2013) to encompass multiple
phylospecies yet to be taxonomically resolved. More than one species of this complex are present in Cyprus, with
numerous collections from Calabrian pine forests in Kélefos, 2.I-2009, 20-XI-2009, 25-XI-2009 & 28-XI-2009, ca 500
m asl; Platánia, 3-XII-2009, ca 1100 m asl; Karvounás, 21-X-2011, 1200 m asl; Kouka, 29-XI-2011, ca 600 m asl;
Madarí, 3-XII-2012, ca 1300 m asl; Mésa Potamós, 10-I-2017, ca 800 m asl; Kannavioú, 29-XI-2017, ca 900 m asl.
Also reported by Viney (2005) in Larnaka tis Lapithou, Dec. 1998.
*Mycena renati Quél.
This striking species was only seen once on a P. brutia log at Stavrós tis Psókas, 18-XI-2009, ca 1200 m asl. Rare.
*Mycena rosea Gramberg
Occasionally seen in a variety of habiatas: Plátres, 27-X-2008, in P. brutia forest, ca 1200 m asl; Péra Pedí, 28-X-2009,
in P. brutia/ Q. coccifera subsp. calliprinos forest, ca 550 m asl; Platánia, 21-XII-2011, in P. brutia/Q. alnifolia forest,
ca 1100 m asl. Uncommon or rare.
Mycena sanguinolenta (Alb. & Schwein.) P. Kumm.
Few sightings, one among P. brutia/Crataegus azarolus/Cistus litter in Saittás, 24-XII-2010, ca 650 m asl. Previously
reported by Viney (2005) from Haléfka, Dec. 2001. Probably widespread but often unnoticed due to its tiny size.
Mycena seynii Quél.
One of the commonnest basidiomycetes in Cyprus, fruiting throughout the island where fallen P. brutia cones are
present. Hundreds of sightings, from Trimíklini, 29-XI-2007, 17-XII-2011 & 31-XII-2013, ca 650 m asl; to Saittás, 30-
XI-2007, 24-XII-2011 & 30-XII-2013, ca 700 m asl; Kélefos, 2-I-2009, 2-XI-2009, 25-XI-2009, 8-I-2011 & 9-XII-
2015, ca 550 m asl; Stavrós tis Psókas, 18-XI-2009, ca 1200 m asl; Moniátis, 20-XII-2010, ca 800 m asl; Pissouri, 2-I-
2011, ca 200 m asl; Kelláki, 25-XI-2011, ca 600 m asl; Kannavioú, 28-XII-2016, ca 900 m asl; or Plátres, 1-XII-2017,
ca 1200 m asl.
*Mycena cf. stipata Maas Geest. & Schwöbel
A couple of collections keying out as this species, both found on carbonized P. brutia logs and twigs in Asgata, 24-
XII-2011 & 26-XII-2011, ca 200 m asl. Cypriot collections feature partially encrusted and considerably larger cystidia
than those reported in literature, measuring 70115 × 1316 μm, while the spores measure (7)811 × 4.55.5 μm.
Either a highly variable taxon, or a Mediterranean counterpart to be clarified by future DNA sequencing.
*Panaeolus acuminatus (P. Kumm.) Quél.
Sparingly encountered in and out of forests, with one collection originating from a grassy P. brutia forest clearing in
Platánia, 21-XII-2011, ca 1100 m asl. Occasional.
*Phaeoclavulina myceliosa (Peck) Franchi & M. Marchetti
Few collections key out as this species, from a mixed riparian forest in Plátres, 23-IX-2008, 5-X-2009 & 10-XI-2012,
ca 900 m asl; as well as calcareous Calabrian pine forests in lefos, 23-XII-2012, ca 500 m asl; and Péra Vása, 29-
XII-2012, ca 700 m asl. Probably widespread, though presently unclear whether European collections identified as this
Basidiomycetes within Pinus brutia ecosystems in Cyprus
15
taxon are conspecific to the North American ones.
Phallus impudicus L.
The notorious stinkhornis only sparingly encountered in Cyprus with some sightings originating from Calabrian pine
forests in Saittás, 20-XII-2009 & 12-ΧΙΙ-2011, ca 700 m asl; and Péra Vása, 9-XII-2012, ca 700 m asl.
Pholiota gallica Holec & M. Kolařík
This species was previously known as P. lubrica var. obscura Bon & Chevassut, “P. highlandensis var.
citrinosquamulosa Maire ex Bidaud & Borgarino, and occasionally misidentified as “Pholiota brunnescens A.H. Sm.
& Hesler”, before it was recombined under its current name (Holec & Kolařík 2014). In Cyprus, it has already been
reported in Cistus mattoral in Asgata (Loizides 2016), but was also collected in P. brutia forests in Akámas, 23-II-
2016, ca 200 m asl.
Pholiota mixta (Fr.) Kuyper & Tjall.-Beuk.
Reported by Viney (2005) on buried conifer wood, beside the Buffavento dirt road, Jan. 2001. Not seen by the author.
Pholiotina filaris (Fr.) Singer
Reported from Kaló Chorió by Viney (2005), but this may correspond to the recently described P. mediterranea Siquier
& Salom (Siquier & Salom 2017).
*Pisolithus tinctorius (Pers.) Coker & Couch
A couple of sightings by a dirt road in Calabrian pine forests at Kélefos, 19-X-2008 & 4-XII-2016, ca 450500 m asl;
a grassy P. brutia forest clearing in Kato Plátres, 21-X-2008, ca 800 m asl; and a P. brutia/Q. alnifolia forest in Spília,
3-XII-2015, ca 1100 m asl. Less common than P. arhizus (Scop.) Rauschert, the latter typically found outside of forests
and lacking a well-defined stalk (Loizides et al. 2011). A couple of the images identified as P. arrhizus” in Viney
(2005) also seem to depict P. tinctorius. The two taxa were widely regarded as synonymous in the past, but in recent
years have shown to be genetically distinct (e.g., Phosri et al. 2012).
Psathyrella spadiceogrisea (Schaeff.) Maire
Reported by Viney (2005) east of Haléfka, Jan. 2001, in mixed tree litter.
*Psathyrella tephrophylla (Romagn.) Bon
A couple of collections match the description of this species, one of them from a grassy P. brutia forest opening in
Kelláki, 25-I-2011, ca 600 m asl. Distribution unclear.
Psilocybe crobula (Fr.) Singer
Rarely encountered in Cyprus, with just a handful of collections from P. brutia forests in Péra Pedí, 7-XI-2009, ca 550
m asl; Madarí, 28-XI-2015, ca 1300 m asl; and Kykkos, 29-XI-2017, ca 1200 m asl. Also reported in Áyios Ilaríon,
Dec. 2000, on fallen pine bark (Viney 2005).
*Ramaria apiculata (Fr.) Donk
A couple of collections from mixed P. brutia/Q. alnifolia/Cistus forests in Ayía Paraskeví, 14-XI-2009, ca 600 m asl;
and Amíantos, 23-X-2011, ca 1200 m asl. Distribution not yet understood.
*Ramaria rubella (Schaeff.) R.H. Petersen
One collection on a decorticated P. brutia log at Kélefos, 23-XII-2012, ca 500 m asl. A somewhat faded collection
from Ayía Paraskeví, 28-III-2009, previously reported as “Ramaria bataillei (Maire) Cornerin Loizides et al. (2011),
may also represent this taxon. Rare.
Ramaria sanguinea (Pers.) Quél.
One collection of strongly rufescent basidiomes matching the description of this species, found in a mixed P. brutia/Q.
alnifolia forest at Stavrós tis Psókas, 25-X-2008, ca 1150 m asl (Loizides et al. 2011). Distribution unclear.
*Ramariopsis subtilis (Pers.) R.H. Petersen
Two collections from Kannavioú matching the descriptions of this taxon on 13-XII-2009 & 15-XII-2009, found in
mixed Calabrian pine forests, 900 m asl. Rare.
Rhizocybe vermicularis (Fr.) Vizzini, P. Alvarado, G. Moreno & Consiglio
Possibly the most widespread basidiomycete appearing in spring, fruiting in large numbers in Calabrian pine forests at,
e.g. Trimíklini, 3-III-2008, 4-III-2009, 24-II-2010, 1-III-2010, 21-III-2011, 1-III-2013 & 28-II-2019, ca 600 m asl; Péra
Pedí, 15-III-2008, 4-III-2009, 15-III-2009, 19-III-2009, 22-III-2009, 12-III-2015 & 2-III-2019, ca 550 m asl; Ayía
Paraskeví, 3-IV-2011, 3-III-2013, ca 550 m asl; Pareklisiá, 8-III-2012 & 25-II-2015, ca 200 m asl; Soúni, 13-III-2012,
5-III-2013, 7-III-2015 & 10-III-2018, ca 400 m asl; Prastió, 25-II-2-15, ca 600 m asl; Kélefos, 5-III-2014 & 5-III-2019,
ca 500 m asl; Episkopí, 28-II-2015, ca 150 m asl; Agrós, 30-III-2015 & 16-III-2019, ca 1000 m asl. Also reported by
Viney (2005) as “Clitocybe vermicularis”, above Haléfka, Mar. 1997.
*Rhizopogon graveolens f. pomaceus Vaček
A sequenced collection from a P. brutia forest in Kélefos, 28-I-2010, ca 500 m asl, nested with the isotype of this
poorly known taxon (det. & pers. comm. M. Martín), which according to Martín & García (2009) probably corresponds
to R. rubescens (Tul. & C. Tul.) Tul. & C. Tul. ss. str. Distribution unclear.
16
Loizides, M.
*Rhizopogon occidentalis Zeller & C.W. Dodge
Few collections matching the description of this taxon, characterized by prominent rhizomorphs engulfing the entire
exoperidium. Seen in both black- and Calabrian pine forests at Kélefos, 6-II-2011 & 12-II-2011, ca 450m asl; and Péra
Pedí, 10-XI-2012, ca 550 m asl.
Rhizopogon vulgaris (Vittad.) M. Lange sensu auct.
An ambiguous and variously interpreted taxon, sometimes regarded as a synonym of R. roseolus (Corda) Th. Fr.
Collections identified as the latter in Cyprus, however, appear to be morphologically distinct and restricted to the higher
elevations of Troodos, found in strict association with P. nigra subsp. pallasiana. There are numerous tentatively
identified collections of R. vulgaris sensu auct. from P. brutia forests in Trimíklini, 17-II-2010, ca 600 m asl; Péra
Pedí, 1-III-2014, ca 550 m asl; Akrotíri, 24-XI-2014, ca 20 m asl; or Soúni, 9-III-2014, ca 400 m asl. Further reported
by Viney (2005) in Kharcha, Nov. 1997, and by Loizides (2016) from Cistus matorral. A collection under Cistus in
Kormakitis reported by Nattrass (1937) as R. luteolus Fr.”, also likely belongs to this species. A difficult complex in
need to be resolved by dedicated phylogenetic investigations.
*Rhodocollybia butyracea (Bull.) Lennox
Common and widespread in Cyprus, frequently seen in black- and Calabrian pine forests. Numerous sightings from,
e.g., Kélefos, 27-XI-2007, 29-XI-2009 & 10-XI-2017, ca 450500 m asl; Platánia, 7-XI-2008, 20-XI-2008, 3-XII-
2009, 5-XII-2011 & 5-I-2012, ca 1100 m asl; or Mésa Potamós, 10-I-2017, ca 800 m asl.
*Rhodocybe matesina Picillo & Vizzini
One collection of this recently described species (Crous et al. 2017), until now known only from Italy: Platánia, 26-
XII-2018, ca 1100 m asl, among P. brutia and C. sempervirens litter. The spores of the Cypriot collection measure 5–
7 × 4–5 μm. Rare.
*Rimbachia neckerae (Fr.) Redhead
This minute cyphelloid basidiomycete was documented once growing among mosses, in a P. brutia forest at Kélefos,
22-XII-2012, ca 500 m asl. Distribution unclear, but probably overlooked.
Rugosomyces onychinus (Fr.) Raithelh.
Occasionally seen in black and Calabrian pine ecosystems, with collections from Moniátis, 13-XII-2007, ca 800 m asl;
Platánia, 23-XI-2009, ca 1100 m asl; Plátres, 26-XII-2009, ca 1300 m asl; and Péra Pedí, 10-I-2017, ca 550 m asl.
Russula acrifolia Romagn.
Fruiting prolifically in P. nigra subsp. pallasiana forests, but occasionally also seen in mixed P. brutia forests, such as
Amíantos, 15-X-2008, ca 1300 m asl; Madarí, 20-XI-2015, ca 1200 m asl; Troodítissa, 11-VI-2018, ca 1300 m asl.
Very common.
*Russula atropurpurea (Krombh.) Britzelm.
Occasionally seen, with a couple of collections from P. brutia/Q. alnifolia forests in Plátres, 17-XI-2011, ca 1200 m
asl; and Platánia, 2-XII-2012, ca 1100 m asl.
Russula aurea Pers.
Widespread in P. nigra subsp. pallasiana forests in years with early rainfall (Loizides et al. 2011), but occasionally
also seen in mixed P. brutia/Q. alnifolia forests in, e.g., Platánia, 20-XI-2009 & 25-VI-2018, ca 1150 m asl.
*Russula badia Quél.
One collection in a pure P. brutia forest in Saittás, 21-XI-2012, ca 700 m asl. Distribution not yet understood.
Russula chloroides (Krombh.) Bres.
Very common, appearing prolifically in mixed black- and Calabrian pine forests, typically at altitudes above 1000 m.
Numerous sightings, e.g., from Amíantos, 15-X-2008, ca 1300 m asl; Troodítissa, 8-IX-2009, 25-X-2011, 31-X-2011,
16-XI-2014 & 14-VI-2018, ca 1300 m asl; Platánia, 25-VI-2018, ca 1150 m asl; Madarí, 20-XI-2015, ca 1350 m asl.
Russula delica Fr.
One of the most common and ecologically versatile fungi on the island, fruiting in vast numbers from ~200 m asl to
the peaks of Troodos. Equally abundant on both calcareous and serpentine soil, with hundreds of sightings from mixed
or pure Calabrian pine forests e.g. in Plátres, 21-XI-2007, 15-X-2008, 19-XI-2011, 1-XII-2017 & 16-X-2018 ca 1100
1300 m asl; Péra Pedí, 21-XI-2007, ca 600 m asl; Saittás, 25-XI-2007, 29-IX-2011, 16-X-2011 & 20-X-2018 ca 700 m
asl; Cedar Valley, 18-XI-2009, 29-XI-2017 & 6-XII-2019, ca 1100 m asl; Mésa Potamós, 9-XII-2007, 6-I-2017, 2-XII-
2017 & 1-XII-2019, ca 700850 m asl; Amíantos, 19-X-2008, 10-X-2009, 16-X-2011 & 21-X-2011, ca 12001300 m
asl; Troodítissa, 12-VIII-2010 & 16-VI-2014, ca 1300 m asl; Karvounás, 13-X-2011 & 13-XI-2018, ca 1250 m asl;
Platánia, 23-X-2011 & 19-VI-2018, ca 11001200 m asl; Stavrós tis Psókas, 22-XI-2011, ca 1200 m asl; Germasógeia,
9-XI-2012, ca 200 m asl; Mávro Dásos, 1-XII-2012 & 3-XII-2012, ca 1000 m asl. Also reported in Syrianóchori, Nov.
2000 (Vibey 2005).
Russula foetens Pers.
Occasional in mixed forests, with a couple of collections from a P. brutia/Q. coccifera subsp. calliprinos forest in
Trimíklini, 25-XI-2012, ca 650 m asl; and P. brutia/Q. alnifolia forest in Platánia, 25-VI-2018, ca 1150 m asl.
Basidiomycetes within Pinus brutia ecosystems in Cyprus
17
Russula hobartiae Loizides & J.M. Vidal
This sequestrate endemic species was recently described from the peaks of Troodos, where it occurs in almost exclusive
association with P. nigra subsp. pallasiana (Vidal et al. 2019). Seen only once under P. brutia in Platánia, 16-VI-2014,
ca 1100 m asl, leg. M. Tordelli & C. Hobart.
Russula sanguinea Fr.
Sparingly encountered, seen in Calabrian pine forests at Péra Pedí, 8-XII-2007 & 10-I-2017, ca 550 m asl; Mávro
Dásos, 5-XII-2012, ca 1000 m asl; Plátres, 17-X-2018, ca 1250 m asl; and Péra Vása, 7-XI-2012, ca 600 m asl.
Previously reported by Viney (2005) from Syrianóchori, Dec. 1998, by Loizides et al. (2011) from collections cited
above, and by Loizides (2016) from Cistus matorral.
Russula torulosa Bres. sensu lato
Several collections match various interpretations of this taxon, most likely encompassing more than one phylospecies.
The phylogenetic and taxonomic status of some satellite taxa such as R. fuscorubra (Bres.) J. Blum, or R. fuscorubroides
Bon, also remains unclear, therefore this complex needs to be resolved by molecular phylogenetics and the appointment
of neo/epitypes. Few collections from Calabrian pine forests in Mandriá, 25-XI-2007, ca 700 m asl; Péra Pedí 8-XII-
2007 & 10-I-2017, ca 550 m asl; Saittás, 15-XI-2007 & 30-XII-2010, ca 700 m asl; Platánia, 10-X-2009 & 25-XI-2013,
ca 1100 m asl. Also reported by Viney (2005), without localities given.
*Russula werneri Maire
Few collections from P. brutia forests match the concept of this rare taxon described from Morocco (Maire & Werner
1938): Saittás, 17-XI-2007 & 5-X-2008, ca 700 m asl; Trimíklini, 10-XI-2012 & 21-XI-2012, ca 650 m asl.
Sarcodon leucopus (Pers.) Maas Geest. & Nannf.
Frequently encountered in Cyprus but very rare elsewhere, and considered extinct in large parts of western and central
Europe. Mostly appearing in high-altitude P. nigra subsp. pallasiana forests (Loizides et al. 2011) in years with early
rainfall, but seen only once under P. brutia in the Platánia picnic area, 19-VI-2018, ca 1100 m asl.
Scleroderma polyrhizum (J.F. Gmel.) Pers.
Occasionally encountered in P. brutia forest clearings and road edges, such as Plátres, 2-X-2007, ca 1150 m asl;
Moniátis, 13-XII-2007, ca 750 m asl; Trypilos, 8-XI-2009, ca 1250 m asl (Loizides et al. 2011).
Scleroderma verrucosum (Bull.) Pers.
An uncommon species first reported by Viney (2005) in Karmi, Nov. 1997. Mostly seen in mixed forests and cultivated
land, with collections from a riparian P. brutia/P. orientalis forest in Moniátis, 29-X-2008, ca 900 m asl; a P. brutia
forest edge in Agrós, 12-III-2012, ca 1000 m asl; a P. brutia/Q. coccifera subsp. calliprinos forest in Kélefos, 23-XII-
2012, ca 500 m asl; and a grassy P. brutia forest opening also in Kélefos, 29-XII-2014, ca 450 m asl.
*Singerocybe phaeophthalma (Pers.) Harmaja
Previously placed in Clitocybe, this species has been transferred to back to genus Singerocybe Harmaja based on
phylogenetic data (Qin et al. 2014; Alvarado et al. 2015, 2018a, 2018b). Just a couple of records in Cyprus, one from
a P. brutia forest clearing at Platánia, 5-XII-2011, ca 1100 m asl. Uncommon or rare.
Sparassis crispa (Wulfen) Fr.
The “cauliflower fungus” is rare and highly localised in Cyprus (Loizides et al. 2011), largely restricted to the western
provinces of the island, particularly the Paphos forest: Cedar Valley, 18-XI-2009, ca 1100 m asl; Stavrós tis Psókas,
22.XI.2011, ca 1250 m asl; Kannavioú, 28-XII-2016, ca 800 m asl.
Stropharia aeruginosa (Curtis) Quél.
Rarely encountered, with one of the collections coming from a mixed Calabrian pine forest in Moniátis, 9-ΧII-2009,
ca 800 m asl. Also reported by Viney (2005) in Lapithos, Dec. 2000.
Suillus bellinii (Inzenga) Kuntze
One of the most prolifically occurring fungi on the island, fruiting in huge numbers in black- and Calabrian pine forests
throughout the autumn and winter months. Hundreds of sightings, e.g. in Saittás, 15-XI-2007, 30-XII-2010, 29-IX-
2011 & 6-I-2017, ca 700 m asl; Moniátis, 13-XII-2007, 25-XI-2009 & 6-I-2017, ca 700 m asl; Mésa Potamós, 23-XII-
2007, 12-XII-2011 & 10-I-2017, ca 800 m asl; Kélefos, 25-XI-2009, 6-XII-2013, 21-I-2015, 9-XII-2015, 10-I-2017,
14-I-2017 & 3-I-2019, ca 450500 m asl; Platánia, 10-X-2009, 3-XII-2009, 20-XII-2014, 20-XI-2015 & 16-XI-2018,
ca 1100 m asl; Plátres, 26-XII-2009, 2-I-2010, 8-XII-2015, 1-XII-2017, 26-X-2018 & 3-XII-2018, ca 1200 m asl;
Pýrgos Tyllirías, 10-I-2011, ca 200 m asl; Amíantos, 1300 m asl; 21-X-2011; Akámas, 18-XII-2014, ca 200 m asl;
Karvounás, 13-XI-2018, ca 1300 m asl. Also reported by Viney (2005) in Áyios Amvrósios, Nov. 1999 & Jan. 2000,
and Loizides et al. (2011) from collections cited above. A collection reported by Nattrass (1937) as “Boletus boudieri
Quél.”, from Kórnos, 1931, probably also corresponds to this species.
Suillus collinitus (Fr.) Kuntze
Extremely common throughout the island, found in association with various pine species from the dunal zone, to the
peaks of Troodos. Dozens of sightings in Saittás, 17-XI-2007, 18-XII-2009, 28-X-2011, 18-XI-2016 & 3-XII-2018, ca
700 m asl; Kélefos, 11-XI-2007, 20-X-2009, 25-XI-2009, 2-XI-2012, 31-XII-2012, 2-XII-2014, 21-I-2015 & 1-I-2019,
18
Loizides, M.
ca 450550 m asl; Plátres, 21-XI-2011, ca 11001200 m asl; Platánia, 10-X-2009, 16-XI-2014, 2-I-2015 & 16-XI-
2018, ca 1100 m asl; Aphrodite’s Rock, 2-II-2009, ca 100 m asl; Péra Pedí, 4-X-2009, ca 550 m asl; Amíantos, 10-X-
2009, ca 1300 m asl; Pýrgos Tyllirías, 10-I-2011, ca 200 m asl; Trimíklini, 10-XI-2012, ca 650 m asl; Soúni, 9-III-
2014, ca 400 m asl; Akrotíri, 24-XI-2014, ca 20 m asl; Akámas, 14-XII-2104 & 19-XII-2104, ca 200 m asl.
Tapinella panuoides (Fr.) E.-J. Gilbert
Reported by Loizides et al. (2011) as “Paxillus ionipus Quél.”. Occasionally seen on logs of P. nigra subsp. pallasiana
and P. brutia, with collections from Péra Pedí, 12-III-2008, ca 550 m asl; and Archimandrita, 16-II-2013, ca 450 m asl.
*Tephrocybe striipilea (Fr.) Donk
Two collections matching descriptions of this taxon in Cedar Valley, 18-XI-2009, ca 1000 m asl, in P. brutia and C.
brevifolia forest; and Platánia, 21-XII-2011, ca 1100 m asl, in P. brutia and C. brevifolia forest clearing. Rare.
*Tephroderma fuscopallens Musumeci & Contu
The monotypic genus Tephroderma Contu & Musumeci, was in recently proposed to accommodate T. fuscopallens, a
species originally collected from North France (Musumeci & Contu 2014) and subsequently documented in Turkey
(Sesli & Topçu Sesli 2016). One collection found among lichens in a mixed P. brutia/C. sempervirens/Cistus forest in
Episkopí, 26-I-2018, ca 150 m asl. Distribution unclear.
Tricholoma batschii Gulden ex Mort. Chr. & Noordel.
Previously reported by its synonym T. fracticum (Britzelm.) Kreiselin Viney (2005), and Loizides et al. (2011), this
widespread species appears in large numbers in Calabrian pine forests, e.g. Mandriá, 25-XI-2007, ca 700 m asl; Péra
Pedí, 31-XII-2007 & 10-I-2017, ca 550 m asl; Lysós, 20-I-2008, ca 600 m asl; Plátres, 22-XII-2009, 26-XII-2009, 2-I-
2010, 8-XII-2015, 1-XII-2017 & 3-XII-2018, ca 1200 m asl; Platánia, 3-XII-2012, ca 1100 m asl; Akámas, 14-XII-
2012, ca 200 m asl; Kélefos, 2-XII-2014, ca 450 m asl. See “Discussion” for further notes.
Tricholoma caligatum (Viv.) Ricken
A typically Mediterranean species, considered a delicacy and widely collected for pickling by the locals (Loizides 2008,
2011; Loizides et al. 2011). Found in various habitats across the Troodos mountain range, including mixed Calabrian
pine forests in Saittás, 20-XII-2007, ca 700 m asl; Plátres, 22-XII-2009, 26-XII-2009, 2-I-2010, 8-XII-2015, 1-XII-
2017 & 3-XII-2018, ca 1200 m asl; Platánia, 1-XII-2009, 3-XII-2009, 9-XII-2009, 30-XII-2011 & 16-XI-2018, ca 1100
m asl; Mésa Potamós, 20-XII-2009, 2-XII-2017 & 20-XII-2018, ca 800900 m asl; Mávro Dásos, 1-XII-2012, ca 1000
m asl; Moniátis, 20-XII-2012, ca 800 m asl; Karvounás, 14-XI-2018, ca 1300 m asl. Common.
*Tricholoma chrysophyllum A. Riva, C.E. Hermos. & Jul. Sánchez
A handful of sightings matching the profile of this rarely reported Mediterranean taxon (Riva 1998), including a
collection from a mixed P. brutia/Q. alnifolia/A. andrachne forest in Platánia, 1-XII-2009, ca 1000 m asl; and
collections from P. brutia forests at Péra Pedí, 10-I-2017, ca 550 m asl. Less common than its lookalike T. equestre
(L.) P. Kumm., which is mostly seen in P. nigra subsp. pallasiana forests in Cyprus (Loizides et al. 2011).
Tricholoma squarrulosum Bres.
Previously regarded a variety of T. atrosquamosum Sacc. (and reported as such in Loizides 2011), this has now been
shown to be a phylogenetically distinct species (Heilmann-Clausen et al. 2017). Common in mixed P. brutia/Q.
alnifolia forests, e.g., in Platánia, 1-XII-2009, 3-XII-2009, 9-XII-2009 & 30-XII-2014, ca 1100 m asl; Plátres, 23-XII-
2009, 26-XII-2009, 17-XII-2012 & 12-XII-2015; or Mávro Dásos, 1-XII-2012, ca 1000 m asl.
Tricholoma sulphureum (Bull.) P. Kumm. sensu lato
Collections identified as this taxon formed multiple clades in the phylogenies of Heilmann-Clausen et al. (2017).
Probably more than one species of this cluster occur in Cyprus, including a collection from a mixed P. brutia/Q.
alnifolia/A. andrachne forest at Mésa Potamós, 10-I-2017, ca 800 m asl. A collection from a Q. alnifolia/P. brutia/A.
orientalis riparian forest reported under this name in Loizides (2011), appears to be morphologically distinct, as is an
odorless collection from a P. brutia forest in Kélefos, 20-XI-2019, ca 450 m asl. Widespread DNA sequencing and
appointment of neo/epitypes for T. sulphureum ss. str. are necessary before any new taxa can be proposed.
Tricholoma terreum (Schaeff.) P. Kumm.
Common in Cyprus, fruiting abundantly from the thermo-Mediterranean belt (Viney 2005; Loizides 2016) to the
subalpine peaks of Troodos (Loizides et al. 2011). Seen in Calabrian pine forests e.g. in Mandriá, 21-XI-2017, ca 700
m asl; Saittás, 29-XI-2007, 30-XII-2013 & 6-I-2017, ca 700 m asl; Péra Pedí, 31-XII-2007, 6-I-2011 & 10-I-2017, ca
550 m asl; Platánia, 22-XII-2007, 1-XII-2009, 3-XII-2009, 9-XII-2009 & 15-XII-2018, ca 1100 m asl; Plátres, 23-XII-
2009, ca 1200 m asl; Stavrós tis Psókas, 22-XI-2011, ca 1200 m asl; Mávro Dásos, 5-XII-2012, ca 1000 m asl; Panayiá,
23-I-2013, ca 1000 m asl; Kannavioú, 29-XII-2016, ca 900 m asl; Moniátis, 10-I-2017, ca 800 m asl.
*Tricholomopsis rutilans (Schaeff.) Singer
Known from a single basidiome found on a P. brutia stump at Platánia, 9-XII-2012, ca 1150 m asl. Rare.
Xerocomellus redeuilhii A.F.S. Taylor, U. Eberh., Simonini, Gelardi & Vizzini
Occasional, with several collections from lowland P. brutia forests. See Loizides et al. (2019) for collection details.
Basidiomycetes within Pinus brutia ecosystems in Cyprus
19
Xerocomellus chrysenteron (Bull.) Šutara
Just a handful of collections from P. nigra subsp. pallasiana forests, and a single collection from a mixed P. brutia/C.
brevifolia/Abies sp. forest at Cedar Valley, 4-IV-2016, ca 1100 m asl (Loizides et al. 2019). Rare in Cyprus.
Xerocomellus cisalpinus (Simonini, H. Ladurner & Peintner) Klofac
A widespread species in Europe but rare in Cyprus, known from a single collection in a mixed P. brutia, C. brevifolia
and Abies sp. stand at Cedar Valley, 15-VII-2012, ca 1000 m asl (Loizides et al. 2019).
Xeromphalina fellea Maire & Malençon sensu lato
Reported by Viney (2005) from Haléfka, Jan. 1999, but several Xeromphalina Kühner & Maire species are present on
the island, whose exact taxonomic position is not entirely clear and needs to be resolved by DNA sequencing.
Discussion
Clearly, the basidiomycete diversity present in P. brutia ecosystems is substantial, with 95 of the 231 taxa
included in the present checklist reported from Cyprus for the first time. Considering that an additional 22
aphyllophoraceous basidiomycetes were associated with P. brutia in a previous checklist (Loizides 2018), but
also that ascomycetes and several dozens of unidentified collections have been excluded, it becomes apparent
that the macromycete diversity in Calabrian pine ecosystems amounts to at least several hundreds of species.
Interestingly, only few taxa seem to exhibit a transcontinental distribution and have been molecularly verified
in more than one continent. These, include mostly opportunistic saprotrophs and wood decomposers such as
Agaricus bisporus, Coprinus comatus, Cystodermella cinnabarina, C. granulosa, Galerina marginata, Phallus
impudicus, or Rhodocollybia butyracea. Lepista nuda and L. sordida have also been reported from several
countries and continents, but appear to be polyphyletic and occupy multiple clades in phylogenetic trees
(Alvarado et al. 2015). Among ectomycorrhizal taxa, Tricholoma batschii has been molecularly confirmed in
both ends of the Atlantic and is widespread in Cyprus, but a number of lookalikes also occur in mixed pine/oak
ecosystems, whose exact taxonomic position is not yet entirely clear. Brown-capped Tricholoma species have
not been adequately sampled in Mediterranean ecosystems and the phylogenetic status of taxa like T.
cedretorum Bon ex A. Riva, T. ezcarayense C.E. Hermos. & Jul. Sánchez, T. striatum (Schaeff.) Quél., and T.
tridentinum Singer, is yet to be fully clarified (Heilmann-Clausen et al. 2017). The widespread distribution and
ecological plasticity of several Hebeloma species present in Cyprus is also notable, particularly H. sinapizans
and H. crustuliniforme, which display a pan-European distribution and are associated with dozens of tree-hosts,
as is H. subtorum whose distribution extends to North Africa (Beker et al. 2016). Few taxa of Inocybe are
reported from different continents (e.g., I. flocculosa, I. geophylla), but these probably involve multiple
biological species (Ryberg et al. 2008; Matheny & Sweney 2018). Similarly, extra-European reports of some
Russula Pers. taxa originally described from Europe (e.g., R. acrifolia, R. atropurpurea, R. foetens, R.
sanguinea), are in need of molecular verification.
Other than the few widely distributed species, the majority of taxa documented exhibit continental
endemism and some are even regional endemics narrowly restricted to the Mediterranean basin. At least one
species, the sequestrate Russula hobartiae, appears to be narrowly endemic in Cyprus and to the Troodos
massif, where it exclusively occurs at elevations above 1000 m (Vidal et al. 2019). The recently described
Clavulina iris and Hygrophorus meridionalis are apparently common and widespread, but again are confined
to southern latitudes and are both strongly associated with Mediterranean flora (Moreau et al. 2018; Crous et
al. 2019). Other typically Mediterranean species documented are Amanita gioiosa, A. ovoidea, A. proxima,
Leucopaxillus malenconii, Russula werneri, Suillus bellinii, Tricholoma caligatum and T. chrysophyllum, in
addition to the recently described Rhodocybe matesina and Tephroderma fuscopallens, whose
phylogeographical distribution is here extended to their second and third countries, respectively. Few other
taxa, such as Clitopilus daamsii, Hygrocybe calciphila, Hygrophorocybe nivea, Lepiota lepida, Leucoagaricus
georginae and Tephrocybe striaepilea are rare, and seldom appear in published literature.
A number of previous reports are considered doubtful or spurious and have been excluded. Chroogomphus
rutilus (Schaeff.) O.K. Mill., previously reported by both Viney (2005) and Loizides et al. (2011), does not
appear to occur on the island and most sequenced collections from Cyprus have turned out to belong to C.
mediterraneus (Scambler et al. 2018). A second species of Chroogomphus (Singer) O.K. Mill., C. subfulmineus
Niskanen et al., is indeed present οn the island, but appears to be confined to the higher eleveations of Troodos
20
Loizides, M.
and is so far known only from P. nigra subsp. pallasiana ecosystems. A collection previously reported as
Ramaria batailleiin Loizides et al. (2011), is now thought to represent a faded collection of R. rubella and
is also excluded, as is Entoloma bloxamii (Loizides 2011), whose collections from Kannavioú likely represent
the recently described E. atromadidum. A collection reported by Viney (2005) as Suillus mediterraneensis
(Jacquet. & J. Blum) Redeuilh, from Syrianóchori, Jan. 2001, is probably misidentified, since the image
provided appears to depict a typical S. bellini. Although the presence of S. mediterraneensis on the island has
been molecularly verified (unpubl. data), this species is rare and so far confined within coastal P. halepensis
plantations suggesting an anthropogenic introduction. Suillus granulatus (L.) Roussel, on the other hand,
reported by Viney (2005) from the same locality (Syrianóchori), does not occur on the island and the image
provided for this collection again appears to depict the widespread S. bellini. A collection from Áyios
Amvrósios, Dec. 2000, reported by Viney (2005) as “Hygrophorus latitabundus Britzelm.”, depicts a pale, dry
and probably unrelated fungus, while collections identified as Rugosomyces chrysenteron (Bull.) Bonare
more likely to represent its Mediterranean lookalike R. fallax Bon. Other doubtful records include Clitocybe
ditopa (Fr.) Gillet, Cystoderma amianthinum (Scop.) Fayod, Lyophyllum decastes, Macrolepiota konradii
(Huijsman ex P.D. Orton) M.M. Moser, Ripartites tricholoma (Alb. & Schwein.) P. Karst., Sericeomyces
serenus (Fr.) Heinem., and Tricholoma portentosum (Fr.) Quél., whose published images by Viney (2005) do
not resemble these species, nor have they been subsequently verified on the island during this 12-y-survey.
Although by no means exhaustive, the present inventory provides the first comprehensive account of
basidiomycete diversity in P. brutia ecosystems and a basis on which future phylotaxonomic investigations
and conservation policies can build. Since the majority of the taxa reported here are yet to be genetically tested
and several species-clusters remain unresolved, it is likely that the taxonomic status of some collections will
change in the future. Generic and infrageneric revisions are thus to be expected, particularly within critical
genera such as Clitocybe s.l., Lepista s.l., or Lyophyllum s.l., which in their current circumscription are not
monophyletic (Alvarado et al. 2015, 2018a & 2018b; Bellanger et al. 2015; Bellanger 2016). Clarification of
old binomials through DNA sequencing of type material or appointment of epitypes, is also necessary for
clarifying critical taxa currently encompassing multiple phylospecies. These include species-clusters currently
lumped under Amanita mairei, Clavulina coralloides, C. rugosa, Clitopilus geminus, Entoloma hirtipes,
Hydnellum ferrugineum, Hygrocybe conica and Tricholoma sulphureum, to name but a few (Olariaga et al.
2009; Lodge et al. 2015; Heilmann-Clausen et al. 2017; Loizides et al. 2018). More importantly, documenting
and understanding fungal diversity in neglected but ecologically important Mediterranean ecosystems has in
recent years become an urgent priority (Richard et al. 2011; ntgen et al. 2015; Loizides et al. 2019a). Given
the accelerated climate warming and aridification trends in the eastern Mediterranean region (Giorgi and
Lionello 2008; Hoerling et al. 2012; Lelieveld et al. 2012; Zittis et al. 2015, 2018 & 2019; Lionello & Scarascia
2018), an enhanced understanding of the full spectrum of fungal diversity and plant-fungi interactions in
Mediterranean ecosystems will greatly improve our ability to predict shifts in biodiversity, identify urgent
conservation priorities and draft effective conservation policies. Towards this end, the documentation of fungal
diversity in other priority habitats in Cyprus, such as Pinus nigra subsp. pallasiana, Quercus alnifolia, and
Cedrus brevifolia ecosystems, as well as coastal dunes and halophytic wetlands, will follow in future dedicated
checklists.
Acknowledgments
I am grateful to Elias Polemis, Juan-Carlos Zamora and Carmel Sammut for critically reviewing and improving the
manuscript prior to submission. Thanks to María P. Martín for the sequencing and identification of Rhizopogon graveolens f.
pomaceus; to Pablo Alvarado (ALVALAB) for sequencing collections cited in this work; to Pierre-Arthur Moreau and Jean-
Michel Bellenager for taxonomic and phylogenetic advice; and to Caroline Hobart for her help and friendly support. Thanks
also to Theologis Alexandrides and Christos Attashis for providing collections and information.
Basidiomycetes within Pinus brutia ecosystems in Cyprus
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Basidiomycetes within Pinus brutia ecosystems in Cyprus
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Basidiomycetes within Pinus brutia ecosystems in Cyprus
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Loizides, M.
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... However, it is apparently a taxon with a southern distribution, found so far both in Mediterranean European countries and North Africa. Collections of this species have so far been reported from France, Algeria, Morocco and Cyprus Holec & al. 2016, Loizides 2016, 2021. This paper expands its distribution to the Balkan Peninsula and reports the first finding of the species in Bulgaria. ...
... This paper expands its distribution to the Balkan Peninsula and reports the first finding of the species in Bulgaria. The Bulgarian collection confirms the occurrence of P. gallica on non-burnt ground in association with Mediterranean vegetation Holec & al. 2016;Loizides 2016Loizides , 2021, in the present case dry grasslands in close proximity to evergreen oaks. ...
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Novel species of fungi described in this study include those from various countries as follows: Antarctica , Apenidiella antarctica from permafrost, Cladosporium fildesense from an unidentified marine sponge. Argentina , Geastrum wrightii on humus in mixed forest. Australia , Golovinomyces glandulariae on Glandularia aristigera , Neoanungitea eucalyptorum on leaves of Eucalyptus grandis , Teratosphaeria corymbiicola on leaves of Corymbia ficifolia , Xylaria eucalypti on leaves of Eucalyptus radiata . Brazil , Bovista psammophila on soil, Fusarium awaxy on rotten stalks of Zea mays , Geastrum lanuginosum on leaf litter covered soil, Hermetothecium mikaniae-micranthae (incl. Hermetothecium gen. nov.) on Mikania micrantha , Penicillium reconvexovelosoi in soil, Stagonosporopsis vannaccii from pod of Glycine max . British Virgin Isles , Lactifluus guanensis on soil. Canada , Sorocybe oblongispora on resin of Picea rubens . Chile , Colletotrichum roseum on leaves of Lapageria rosea . China , Setophoma caverna from carbonatite in Karst cave. Colombia , Lareunionomyces eucalypticola on leaves of Eucalyptus grandis . Costa Rica , Psathyrella pivae on wood. Cyprus , Clavulina iris on calcareous substrate. France , Chromosera ambigua and Clavulina iris var. occidentalis on soil. French West Indies , Helminthosphaeria hispidissima on dead wood. Guatemala , Talaromyces guatemalensis in soil. Malaysia , Neotracylla pini (incl. Tracyllales ord. nov. and Neotracylla gen. nov.) and Vermiculariopsiella pini on needles of Pinus tecunumanii . New Zealand , Neoconiothyrium viticola on stems of Vitis vinifera , Parafenestella pittospori on Pittosporum tenuifolium , Pilidium novae-zelandiae on Phoenix sp. Pakistan , Russula quercus-floribundae on forest floor. Portugal , Trichoderma aestuarinum from saline water. Russia , Pluteus liliputianus on fallen branch of deciduous tree, Pluteus spurius on decaying deciduous wood or soil. South Africa , Alloconiothyrium encephalarti , Phyllosticta encephalarticola and Neothyrostroma encephalarti (incl. Neothyrostroma gen. nov.) on leaves of Encephalartos sp., Chalara eucalypticola on leaf spots of Eucalyptus grandis × urophylla , Clypeosphaeria oleae on leaves of Olea capensis , Cylindrocladiella postalofficium on leaf litter of Sideroxylon inerme , Cylindromonium eugeniicola (incl. Cylindromonium gen. nov.) on leaf litter of Eugenia capensis , Cyphellophora goniomatis on leaves of Gonioma kamassi , Nothodactylaria nephrolepidis (incl. Nothodactylaria gen. nov. and Nothodactylariaceae fam. nov.) on leaves of Nephrolepis exaltata , Falcocladium eucalypti and Gyrothrix eucalypti on leaves of Eucalyptus sp., Gyrothrix oleae on leaves of Olea capensis subsp. macrocarpa , Harzia metro­sideri on leaf litter of Metrosideros sp., Hippopotamyces phragmitis (incl. 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Thailand , Cordyceps jakajanicola on cicada nymph, Cordyceps kuiburiensis on spider, Distoseptispora caricis on leaves of Carex sp., Ophiocordyceps khonkaenensis on cicada nymph. USA , Cytosporella juncicola and Davidiello­myces juncicola on culms of Juncus effusus , Monochaetia massachusettsianum from air sample, Neohelicomyces melaleucae and Periconia neobrittanica on leaves of Melaleuca styphelioides × lanceolata , Pseudocamarosporium eucalypti on leaves of Eucalyptus sp., Pseudogymnoascus lindneri from sediment in a mine, Pseudogymnoascus turneri from sediment in a railroad tunnel, Pulchroboletus sclerotiorum on soil, Zygosporium pseudomasonii on leaf of Serenoa repens . Vietnam , Boletus candidissimus and Veloporphyrellus vulpinus on soil. Morphological and culture characteristics are supported by DNA barcodes.
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A six-gene phylogeny of the Inocybaceae is presented to address classification of major clades within the family. Seven genera are recognized that establish a global overview of phylogenetic relationships in the Inocybaceae. Two genera—Nothocybe and Pseudosperma—are described as new. Two subgenera of Inocybe—subg. Inosperma and subg. Mallocybe—are elevated to generic rank. These four new genera, together with the previously described Auritella, Tubariomyces, and now Inocybe sensu stricto, constitute the Inocybaceae, an ectomycorrhizal lineage of Agaricales that associates with at least 23 plant families worldwide. Pseudosperma, Nothocybe, and Inocybe are recovered as a strongly supported inclusive clade within the family. The genus Nothocybe, represented by a single species from tropical India, is strongly supported as the sister lineage to Inocybe, a hyperdiverse genus containing hundreds of species and global distribution. Two additional inclusive clades, including Inosperma, Tubariomyces, Auritella, and Mallocybe, and a nested grouping of Auritella, Mallocybe, and Tubariomyces, are recovered but with marginal statistical support. Overall, the six-gene data set provides a more robust phylogenetic estimate of relationships within the family than do single-gene and single-gene-region estimates. In addition, Africa, India, and Australia are characterized by the most genera in the family, with South America containing the fewest number of genera. A total of 180 names are recombined or proposed as new in Inosperma, Mallocybe, and Pseudosperma. A key to genera of Inocybaceae is provided.