Herzogia 19 (2006): 125–148
125
Notes on the lichens and lichenicolous fungi
of western Crete (Greece)
Toby SPRIBILLE, Matthias SCHULTZ, Othmar BREUSS & Erwin BERGMEIER
Abstract: SPRIBILLE, T., SCHULTZ, M., BREUSS, O. & BERGMEIER, E. 2006. Notes on the lichens and lichenicolous
fungi of western Crete (Greece). – Herzogia 19: 125–148.
We report a total of 248 species of lichens and lichenicolous fungi from recent floristic work in western Crete. A total
of 103 taxa are reported from the island for the first time; at least 16 taxa are new to Greece. Two species, Peccania
teretiuscula and Verrucaria werneri, are new to Europe and both are reported for only the second time since their description. Lichens that disperse by asexual reproductive structures (soredia, isidia) constitute only a small proportion
of the flora and most species with this dispersal strategy are relatively infrequent. Some possible reasons for this as
well as general patterns in the epiphytic lichen flora are discussed.
Zusammenfassung: SPRIBILLE, T., SCHULTZ, M., BREUSS, O. & BERGMEIER, E. 2006. Beitrag zur Kenntnis der
Flechten und lichenicolen Pilze West-Kretas (Griechenland). – Herzogia 19: 125–148.
In diesem Beitrag berichten wir über Nachweise von 248 Arten von Flechten und lichenicolen Pilzen von West-Kreta.
103 Taxa sind Erstnachweise für Kreta, davon werden auch mindestens 16 erstmals für Griechenland angegeben.
Peccania teretiuscula und Verrucaria werneri sind neu für Europa und waren bisher nur von der Typuslokalität bekannt. Flechten, die sich mittels asexueller Reproduktionseinheiten (Soredien, Isidien) ausbreiten, machen nur einen
kleinen Teil der Flechtenflora Kretas aus, und die meisten dieser Arten sind recht selten. Mögliche Gründe dafür sowie
allgemeine Muster der epiphytischen Flechtenflora werden diskutiert.
Key words: Ascomycetes, biodiversity, cyanolichens, conservation, epiphytes, floristics, island biogeography,
Mediterranean, reproductive strategy, sorediate lichens.
Introduction
One hundred years after the first publication on the lichens of Crete (ZAHLBRUCKNER 1906), the
exploration of the lichen flora of Crete remains to a certain extent in a phase of initial reconnaissance. Compared to its well studied island counterparts in the western Mediterranean, the island
has seen the publication in the last century of comparatively few floristic surveys. Relatively little
ecological work has been done, notwithstanding a few important, pioneering works in which
broad groupings of Cretan lichen habitats were outlined for the first time (RONDON 1969, PAPP
et al. 1998). Even so, it is difficult to characterize the ecological behaviour and geographical and
zonal distribution of most lichen species on Crete for want of data; and such work, in turn, is
impeded by the absence of any kind of regional flora for the eastern Mediterranean.
Much of what we know today about the lichens of Crete can be traced back to a handful of
publications. ZAHLBRUCKNER (1906) provided a list of 86 lichens collected on the island by
J. Dörfler and R. Sturany in 1904. This was followed by a floristic ‘Reisebericht’ based on
collections of A. Ginzberger in April 1914 and prepared by J. Steiner (STEINER 1917). Within
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the framework of the ‘Flora Aegaea’, the Hungarian lichenologist Ödön Szatala provided a
catalogue of lichens of the Aegean, in which the Cretan portion was based largely on existing
collections of Dörfler, Sturany and Ginzberger (SZATALA 1943a). In a second contribution,
SZATALA (1943b) listed lichens collected by Karl Heinz Rechinger in 1942 during the German
occupation. Many of these early specimens are in W or WU. The sum total of lichen species
known up to this point from Crete was about 240 (KLEINIG 1966). In 1964, a student excursion
from the University of Heidelberg added 80 new species to the flora and provided occasion
for a consolidated checklist of Cretan lichens (KLEINIG 1966). Further additions to the flora
were reported by RONDON (1969) and PAPP et al. (1998), as well as in a series of monographic
taxonomic treatments (e.g., TIMDAL 1991). The inventory of new species was ultimately summarized in a second checklist of Cretan lichens, including 68 additional previously unreported
taxa, by GRUBE et al. (2001).
In the framework of another botanical excursion, this time from the University of Göttingen in
May, 2004, the first author had the opportunity to collect lichens in a wide variety of habitats
at 32 different localities across western Crete. The collecting effort was not systematic, and
because of time limitations complete inventories were not possible at every site. Epiphytic
species received most of the emphasis, although species from all substrates were included in
the general survey. In all, c. 940 specimens were collected along an altitudinal gradient ranging
from sea level to over 1500 m in the western half of the island. Further lichen collections were
made by the second author during a visit to Crete in spring of 2005. Lichens were collected
along the trail to the Kamares Gorge (south slope of the Ida Mountains) as well as on coastal
cliffs close to Matala in the Messara Bay.
The aim of the present article is twofold. First, we would like to provide a contribution to the
lichen flora of Greece and the eastern Mediterranean by documenting the species found in the
course of our surveys, including numerous new records. Second, we wish to begin to lay the
groundwork for creating ecological and distributional profiles for the species of the Cretan
lichen flora by annotating each record with notes on substrate and occurrence. The need to do
this even for species already known from Crete is evident. Many, perhaps even most, of the
known species are based only on single records specifying only localities, often in the broadest
terms. The lack of ecological or distributional data has up to now represented a considerable
hurdle to more detailed studies, and we hope that the present annotated list will help lay the
groundwork for more detailed systematic and ecological studies of the Cretan lichen flora.
Materials and Methods
We visited a total of 34 different sites across western and central Crete (Table 1). The selection of localities reflected an attempt to capture a broad array of habitats ranging from arid
coastlines, phrygana and macchia to Platanus ravines, Castanea groves and native Quercus
woodlands on limestone, siliceous phyllite/quartzite bedrock and Neogene sediments from sea
level to about 1700 m. The large diversity of habitats at various elevations allowed us to collect epiphytes from a total of 17 different phorophyte species. Although an attempt was made
to capture as many different substrates as possible, collecting was generally biased towards
epiphytes.
Over 1000 specimens were collected. Identification of the material followed standard light
microscopic methods. Thin layer chromatography was carried out on about 150 specimens
following the methods described by CULBERSON (1972) and CULBERSON & JOHNSON (1982).
SPRIBILLE et al: Notes on the lichens and lichenicolous fungi of western Crete (Greece)
127
Table 1: Lichen collecting localities.
1
2
3
4
5
Date
05 May 2004
05 May 2004
06 May 2004
07 May 2004
07 May 2004
6
7
07 May 2004
08 May 2004
8
9
10
09 May 2004
09 May 2004
09 May 2004
11
10 May 2004
12
13
14
10 May 2004
10 May 2004
10 May 2004
15
11 May 2004
16
17
18
19
20
21
22
11 May 2004
11 May 2004
13 May 2004
14 May 2004
14 May 2004
14 May 2004
15 May 2004
23
24
25
26
15 May 2004
16 May 2004
16,19 May
2004
16 May 2004
27
17 May 2004
28
17 May 2004
29
17 May 2004
30
31
32
18 May 2004
18 May 2004
18 May 2004
33
30 Apr 2005
34
27 Apr and 02
May 2005
Locality
Vicinity of Knossos SE of Iraklio
Near Ano Archanes, base of Youchtas Mountain
Akrotiri Peninsula, Stavros.
Village of Imbros
Along footpath between village of Imbros and
upper entrance to Imbros Gorge
Imbros Gorge
Akrotiri Peninsula, vicinity of Moni Gouvernetou
and Moni Katholiko
Omalos Plain, Spilion Tsanis (Tsani Cave)
Southern edge of Omalos plain near road junction
Levka Ori, trail S of Omalos from Xiloskalo
towards Gingilos
Fassas Valley, 1 km SW of Langos, in Platanusdominated moist ravine
Fassas Valley, 2 km SW of Langos
Fassas Valley, between Langos and Nea Roumata
Levka Ori, just W of Agii Theodori, ca. 3 km SW
of Omalos, between mountains Mavri Kimite and
Tourli
Between Topolia and Koutsamatados, around
entrance to Cave of Agia Sofia
Elos
C. 1 km east of Elafonisi
Akrotiri Peninsula, below Moni Gouverneto
Kastellos, 1.5 km W of Armeni
Between Armeni and Kare
Near Prassies
SW of Psiloritis Mountains, Skholi Asomatou
(Asomaton Agricultural School)
Between Asomaton and Genna.
1.5 km W of Meronas on the road to Gerakari.
Between Gerakari and Spili: Gious Kambos
Plateau
mouth of Megalou Potamos on sea, below Preveli
Monastery
Limni Votomou, above Ano Zaros, in phrygana
facing town
Psiloritis Mtns., Rouvas Gorge, above town of
Ano Zaros
On plateau above Rouvas Gorge, near the chapel
of Agios Ioannis
Messara Plain, ruins of Gortis
Near Festos, excavation of Agia Triada
West of Pitsidia: Kommos Beach, 100–200 m
from sea
Southern Ida Mountains, trail to Kamares Gorge
(M. Schultz collections).
Matala SW of Messara Plain, rocky slopes,
coastal cliffs on trail to and at Red Beach (M.
Schultz collections)
Elev. (m)
90–120
500
Sea level
900
750
Coordinates
35°18'N/25°10'E
35°13'N/25°09'E
35°36'N/24°06'E
35°15.5'N/24°09.5'E
35°15'N/24°10'E
400–700
100–250
35°14'N/24°09.5'E
35°35.5'N/24°08'E
1050
1100
1200–
1700
220
35°21.5'N/23°54'E
35°19.5'N/23°54.5'E
35°18'–19'N/
23°54'–54.5'E
35°25'N/23°53'E
310
330
1050–
1100
35°24'13''N/23°52'26''E
35°24'01''N/23°52'27''E
35°20'N/23°51'–52'E
300
35°25'N/23°41'E
500
0–5
200–250
370
413
400
350
35°22'N/23°38'E
35°17'N/23°32'E
35°35.5'N/24°08'E
35°19'N/24°26'E
35°17'32''N/24°28'56''E
35°19'N/24°31.5'E
35°15'N/24°39'E
350–400
700
750–800
35°15'N/24°38.5'–39'E
35°13'30''N/24°36'E
35°13'N/24°33.5'E
0–5
35°09'–10'N/24°28.5'E
510
35°09'N/24°54.5'E
700
35°09'N/24°54'E
900–1000
35°09'N/24°54'E
180
70–100
5–10
35°04'N/24°56'E
35°04'N/24°47'E
35°01'N/24°45'E
950–1000
c. 35°09.5'N/24°49.5'E
5–100
c. 34°59.25'N/24°45.0'E
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M. Schultz reviewed almost all of the Lichinaceae and Collemataceae and O. Breuß revised
the pyrenocarps. Unless otherwise indicated, specimens are deposited in B, with some duplicates in GOET, BG (including most Bacidias) and W; M. Schultz’ collections are deposited in
HBG. A few additional records were generously contributed by Stefan Abrahamczyk, Tassilo
Feuerer, Helmut Mayrhofer and Viktoria Wagner and are deposited as indicated. Vascular plant
nomenclature follows JAHN & SCHÖNFELDER (1995). Quercus macrolepis refers to Quercus
ithaburensis subsp. macrolepis.
Results and Discussion
A total of 248 species, 1 subspecies and 4 varieties were recorded in 94 genera. Of these, 103
taxa do not appear to have been previously reported from Crete. The species reported here
bring the total number of lichens known for Crete to 524 lichen taxa and 16 non-lichenized, lichenicolous fungi, up from the previously reported figures of 427 and 13, respectively (GRUBE
et al. 2001) following the subtraction of three species reported in the latter (see below).
At least three species reported by GRUBE et al. (2001) should be excluded: Caloplaca calcicola var. rechingeri Servít (‘Caloplaca rechingeri Servít’; cf. KLEINIG 1966) is a synonym
of C. cretensis (Zahlbr.) Wunder and Caloplaca rhinodinoides J. Steiner is a synonym of
Caloplaca variabilis var. variabilis (WUNDER 1974). Fuscopannaria leucosticta is accepted
by GRUBE et al. (2001) based on the reports of ZAHLBRUCKNER (1906) and SZATALA (1943b),
but the supporting specimens in both cases have been referred to Fuscopannaria olivacea
(JØRGENSEN 1978). It is possible that other species currently accepted for the flora of Crete
should be excluded, but determining where this is the case will require re-examination of
original material.
Patterns in the epiphytic lichen flora
GRUBE et al. (2001) state that strong degradation of the vegetation limits the abundance of
epiphytic lichens on Crete. While we have not conducted a systematic survey of Cretan epiphytic lichen vegetation, our observations suggest that this assumption should be revisited
with scrutiny of the types of disturbance and disturbed habitats involved. Lichen communities
occurring on trunks of Olea europaea and alley trees in villages are indeed likely to have been
strongly impacted by the widespread liming of trunks. Overgrazed low-growing stands of
hedge-trimmed Quercus coccifera are usually rather poor in epiphytic lichen species. However,
whether this is due to overgrazing or the fact that such stands often occur on very dry, dusty
sites is not immediately evident. We found richly developed epiphytic lichen communities on
both trunks and branches in heavily grazed woodlands; ultimately even overgrazed stands offer colonizable bark on the trunks and branch bases behind the protective outer layer of heavily
armed branch tips. It is in fact conceivable that grazing in some cases may provide additional
enrichment and niche development through nutrient input. Lobarion-like communities, which
in Crete can be recognized by the presence of Fuscopannaria olivacea and a suite of crustose
species, are found in both grazed and ungrazed Quercus woodlands but always occur in stands
with large, presumably old trees.
Data are not yet sufficient to map epiphytic lichen vegetation, but some broad patterns are
becoming evident. Lichen vegetation reflecting more humid conditions occurs at mid-montane
elevations and extends downslope on the north side of Crete into the area of Neogene sediments. Typical species that represent this formation are Collema furfuraceum, Fuscopannaria
SPRIBILLE et al: Notes on the lichens and lichenicolous fungi of western Crete (Greece)
129
olivacea, Pertusaria hymenea and Staurolemma omphalarioides. Ramalina-Evernia-dominated lichen vegetation is characteristic of some montane forests of the Psiloritis Mountains in
areas where cloud banks hang for protracted periods of time; these are also the only areas on
Crete in which species of Lobaria are known to occur.
One group of species definitely affected by the human impact of the island are the lignicoles.
Only nine species were found exclusively on lignum in the present survey: Buellia chloroleuca, Calicium glaucellum, C. salicinum, Mycocalicium subtile, Lecanora saligna, Lecanora
aff. hypoptoides, Platismatia glauca, Rinodina excrescens and Scoliciosporum umbrinum. The
first four species are found almost exclusively on lignum also in mainland regions. All are
known for Crete from only one or two records, reflecting the scarcity of dead wood that is so
evident when surveying lichens in Cretan woodlands.
One of the more important areas for rare species identified during the present survey is the
Fassas Valley, an area of humid, low elevation Platanus orientalis-dominated ravines southwest of Chania below the village of Nea Roumata. This and adjacent valleys differ from much
of the rest of the Cretan landscape in that they are underlain by siliceous rock, mainly phyllite and quartzite. These areas are accordingly less water-permeable and maintain numerous
perennial watercourses. Several relicts of the Tertiary vascular flora are known from this area,
including the bay tree Laurus nobilis, the fern Woodwardia radicans and the regionally endemic Lathyrus neurolobus (JAHN & SCHÖNFELDER 1995). The following lichens have been
found on Crete so far only in this area: Bacidia arceutina, Bacidina phacodes, Fuscopannaria
aff. atlantica, Hyperphyscia adglutinata, Lempholemma sp. 1, Lepraria lobificans, Micarea
bauschiana, Opegrapha atra and Opegrapha ochrocincta. All but the Lepraria and Micarea
are corticolous epiphytes. Further work on the lichen flora of the Platanus ravines is badly
needed in light of continued threats to ravine habitats from encroaching settlements, forest
clearing for orange plantations, and road construction.
Table 2: Proportion of reproductive strategies represented in the Cretan lichen flora
Sexual reproduction
With soredia
With isidia or fragmenting thallus
Total with vegetative propagules
Total number of taxa
Number of taxa
448
46
30
76
524
Per cent of total flora
85.5
8.8
5.7
14.5
100
Low proportion of species with vegetative propagules
An examination of the proportions of species with different reproductive strategies shows that
the vast majority of species reproduce sexually by spores (Table 2). Species with asexual reproductive structures (soredia, isidia and fragmenting thalli) constitute only 14.5 % of the total
Cretan lichen flora (Table 2). Comparable proportions have been reported by SIPMAN & RAUS
(1999) from the Aegean islands of Paros (14 %) and Santorini (18 %). It is difficult to meaningfully compare these statistics with data from mainland areas owing to the differences in
size and relief of study areas and the differing degree to which lichen floras have been studied.
That said, however, it is interesting to note that the percentage of lichen species with vegetative reproductive structures is higher in a mainland area of Spain (22 %) in a study reported
by SIPMAN et al. (2005) and consistently higher in every administrative region of Italy in the
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ITALIC database of MARTELLOS & NIMIS (2001): for example, 26.2 % for Emilia Romagna,
a mainland region, 22.6 % for Sicily and 22.4 % for Sardinia, the largest and second largest
islands in the Mediterranean, respectively, and 20.7 % for the whole of Italy.
The reasons for the low number of asexually reproducing species and the rarity of others are
likely to be complex. JAHNS (1984) points out that lichens with soredia-like structures are
formed under humid conditions and are at a disadvantage in dry climates owing to the low
water storage capacity of soredia. Theoretically, isidia-bearing species should be at an advantage under these circumstances due to their greater water storage capacity, but they are in
turn more strongly dispersal-limited. It might thus be tempting to assume that the relatively
low number of lichens with vegetative reproductive strategy on Crete is attributable to a drier
climate. However, there is evidence to suggest that climate may not be responsible for this
phenomenon. First, many parts of Crete, especially in the western mountains, are in fact very
humid, with annual precipitation of up to 1500 mm (2000 mm in summit areas), notwithstanding the characteristically Mediterranean summer moisture deficit. Secondly, several prominent
asexually reproducing lichen species are absent on Crete and present either on adjacent islands
or on the mainland. A good example of this is Hypogymnia physodes, which grows not only in
corresponding habitats on the Greek mainland but also on the Aegean islands of Paros, Naxos
and Ikaria (SIPMAN & RAUS 1999, SIPMAN et al. 2005). Given the well-developed epiphytic
lichen communities in the Cretan mountains, it seems likely that H. physodes would be able
to grow on Crete were its diaspores able to colonize the appropriate substrates. Thirdly, a
similarly irregular distribution of asexually reproducing lichen species between islands has
been reported by SIPMAN et al. (2005) from Ikaria and Naxos, two medium-sized islands in the
central Aegean, with several of the common species present on one island and absent on the
other. In tandem with these observations, SIPMAN et al. (2005) also report isolated occurrences
of the isidiate foliose lichen Pseudevernia furfuracea on the island of Ikaria, where the two
main chemotypes, var. furfuracea (‘var. olivetorina’) and var. ceratea, occur isolated on two
different mountains. A similar incongruence can be observed on Crete, where P. furfuracea
var. furfuracea is known from only a single locality, whereas var. ceratea is found in both the
Levka Ori and Ida mountain ranges. The two varieties exhibit largely sympatric distributions
in mainland areas (CULBERSON et al. 1977).
Another possible explanation is that asexually reproducing lichens do not disperse over long
distances as effectively as sexually reproducing species. This would contradict a widely held
assumption that at least sorediate species disperse as well or more effectively than sexual
species (e.g., BOWLER & RUNDEL 1975). This assumption has been at least in part based on
the observation that in sexual-asexual species pairs, the asexually reproducing species tend to
have wider distributional ranges (BOWLER & RUNDEL 1975). Relatively little work has been
conducted on dispersal strategies in lichens, although there is evidence, e.g., in calicioid fungi
that species with small spores are more effective long distance dispersers than species with
comparatively large spores (TIBELL 1994). Following the same general logic, spores should be
more effective long distance dispersal propagules than soredia, which tend to be considerably
larger. The spotty distribution of asexually reproducing species on Crete and other Aegean
islands in any case appears to be consistent with a pattern of irregular colonization of island
habitats. Island biogeographical factors – including area, isolation and dispersal strategies – are
well studied for other groups of organisms but are still virtually unexplored in lichenology. As
more floristic work is completed on Crete and other Aegean islands, this part of the world may
prove to be a productive outdoor laboratory for the study of insular effects on lichen floras.
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Endemism in the Cretan lichen flora
Whatever island effects can be detected for the Cretan lichen flora do not appear to be reflected,
at least at present, in a high number of endemic species. Relatively few new taxa have been
described from Crete, mainly by ZAHLBRUCKNER (1906) and STEINER (1917), and of these, all
but one have fallen into synonomy or been shown to be more widespread. This leaves only two
lichen species, Thelidium creticum (STEINER 1917) and the more recently described Toninia
cretica (TIMDAL 1991) that are known to occur only on Crete. Toninia cretica is found in calcareous rock fissures and is known only from four localities in the western and central part of the
island (TIMDAL 1991). Thelidium creticum is known only from the type collection from limestone at Knossos (STEINER 1917). Three more taxa will likely be added when Acarospora sp. 1,
Candelariella sp. 1 and Lempholemma sp. 1, apparently undescribed species discovered in the
present survey, are formally described. However, the endemic status of lichens described in the
past from Crete or other Mediterranean islands has tended to be short-lived as they are discovered in other hitherto little-explored areas. In light of this cycle of description and discovery,
it is probable that the proportion of endemics in the flora will at any rate remain low. The near
absence of endemic lichens stands in vivid contrast to the vascular flora, in which over 10 % of the
1800 vascular taxa are endemic to Crete and adjacent islands (JAHN & SCHÖNFELDER 1995).
Lichens recorded from western Crete
The following list documents the species found. An asterisk (*) indicates a species new for
Crete. It is difficult in many cases to assess whether a species is known from Greece as there
is no recent checklist of Greek lichens (see also SIPMAN & RAUS 2002). However, where it is
apparent that a taxon has not been previously reported for Greece, this is indicated by a double
asterisk (**). The numbers in parentheses refer to collecting localities (see Table 1); collection
numbers are those of the first author unless otherwise indicated; ‘sub’ indicates that a specimen
is filed under the given name in the herbarium.
**Acarospora sp. 1 – Parasitic on Diploschistes diacapsis in moist, open phrygana, 800 m. (25): 13542,
13543, 13761.
This species belongs to the subgenus Xanthothallia H. Magn., the members of which are characterized
by the presence of rhizocarpic acid in the cortex. A. sp. 1 possesses rhizocarpic acid in both the cortex
and medulla and an unknown xanthone in the medulla. The only other species in the genus known to
have rhizocarpic acid also in the medulla is Acarospora chrysocardia Poelt & Steiner, but that species has larger ascospores (POELT & STEINER 1971) and, significantly, lacks xanthones (LEUCKERT &
BUSCHARDT 1978). A detailed description of the new species is in preparation (Spribille, ined.).
Acrocordia gemmata (Ach.) A.Massal. – On Castanea sativa and Quercus macrolepis bark, 330–500 m.
(16): 13392 (sub Physconia distorta); (19): 13451.
*Agonimia opuntiella (Buschardt & Poelt) Vězda – On bark of Quercus macrolepis, 370 m. (19): 13443
(ver. C. Roux).
Anaptychia ciliaris (L.) Körb. – A montane species found between 750–1300 m. Epiphytic on branches of Acer sempervirens, Cupressus sempervirens, Pinus brutia, Pyrus spinosa, Quercus coccifera,
Zelkova abelicea. (4): 12853; (8): 13023, 13029; (9): 13070; (10): 13187, 13201, 13206; (14): 13311,
13374; (29): 13629, 13636, 13649, 13665; (33): Schultz 09426.
*Anema decipiens (A.Massal.) Forssell – On steep limestone boulders and overhangs close to sea level. (34):
Schultz 09465d, 09468b (with Thyrea confusa, Thelochroa montinii and Lichinella iodopulchra s.l.).
Squamules are usually greyish pruinose. Fairly widespread in southern Europe.
*Arthonia aff. calcicola Nyl. – On vertical limestone canyon walls and on exposed limestone boulders,
0–700 m. (6): 12970 (sub Caloplaca xantholyta); (17): 13408; (34): Schultz 09453a.
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Herzogia 19 (2006)
Spribille 12970 and 13408 are remarkable in possessing a very short hymenium 40–55 µm tall, much
shorter than described for Arthonia calcicola. The material otherwise broadly agrees with A. calcicola
in possessing protococcoid algae in an immersed thallus and a bluish-green epithecium.
Arthopyrenia punctiformis A.Massal. – On Ceratonia siliqua bark at sea level. (26): 13591.
Aspicilia caesiocinerea (Nyl. ex Malbr.) Arnold – On rock in phrygana, 750 m. (5): 12908 (sub
Lobothallia radiosa).
Aspicilia calcarea (L.) Mudd – On large exposed limestone boulders, c. 1000 m. (33): Schultz 09421.
*Aspicilia cheresina (Müll.Arg.) Hue var. justii (Servít) Clauzade & Cl.Roux – Parasitic on Aspicilia cf.
caesiocinerea on limestone, 1050 m. (8): 13056, 13058. TLC (13058): norstictic, connorstictic, stictic
and constictic acids.
Only the var. microspora (Arnold) Clauzade & Cl.Roux, which contains only norstictic acid, was previously reported from Crete (GRUBE et al. 2001).
Aspicilia coronata (A.Massal.) de Lesd. – On large exposed limestone boulders. (34): Schultz 09417b
(with Verrucaria marmorea, Bagliettoa parmigera).
Thallus ± entirely endolithic, apothecia whitish or blackish, colour and reaction of the epihymenium
separate the species from similar species of Hymenelia or Ionaspis.
Aspicilia cupreoglauca de Lesd. – On siliceous rock of shepherd’s hut, 800 m. (25): 13765.
Aspicilia farinosa (Flörke) Arnold – On large exposed limestone boulders, 1000 m. (33): Schultz 09418a
(with Rinodina immersa).
*Bacidia arceutina (Ach.) Arnold – On Laurus nobilis bark in humid Platanus orientalis ravine; 310 m.
(12): 13292 (BG, det. S. Ekman).
*Bacidia circumspecta (Vain.) Malme – On Quercus macrolepis bark, 370 m. (19): 13465 (BG, det. S.
Ekman).
*Bacidia rubella (Hoffm.) A.Massal. – On Quercus pubescens bark, 700 m. (24): 13527 (BG, ver. S.
Ekman).
Bacidia thyrrenica Llop ined. – On Quercus coccifera branches, c. 1000 m. (29): 13624 (B), 13633,
13667, 13676 (BG, ver. S. Ekman).
B. thyrrenica includes material traditionally assigned to B. rosella (Pers.) De Not. (S. Ekman, pers. comm.).
*Bacidina phacodes (Körb.) Vězda – On bark of Phillyrea latifolia and Platanus orientalis, 220–330 m.
(11): 13274; (13): 13298, 13304 (both BG, ver. S. Ekman).
Bagliettoa parmigera (J.Steiner) Vězda & Poelt – On large exposed limestone boulders, c. 1000 m. (33):
Schultz 09417c (with Verrucaria marmorea, Aspicilia coronata).
*Biatoridium monasteriense Körb. – On bark of Quercus macrolepis, 370 m. (19): 13450.
Bilimbia lobulata (Sommerf.) Hafellner & Coppins – On calcareous soil over rock, 1050 m. (8): 13065.
**Botryolepraria lesdainii (Hue) Canals et al. – On deeply shaded limestone rock faces, cave entrances,
and bare mineral soil below Cupressus in deep shade, 300–700 m. (6): 12988; (15): 13384; (28): 13618
(all specimens BG, ver. T. Tønsberg). TLC: lesdainin (major), two unidentified terpenoids (trace).
**Buellia chloroleuca Körb. – On wood of Cupressus sempervirens snag, c. 1400 m. (10): 13224. TLC:
xanthone.
Previously known in the Mediterranean from Spain and Italy (GIRALT et al. 2000), otherwise central
Europe and Scandinavia. New to the eastern Mediterranean.
*Buellia griseovirens (Turner & Borrer ex Sm.) Almb. – On Pinus brutia bark, 1000–1400 m. (10):
13194; (14): 13305 (sub Pertusaria pertusa), 13338. TLC: atranorin, norstictic acid.
Buellia subdisciformis (Leight.) Vain. – On exposed calciferous sandstone boulders near sea level. (34):
Schultz 09404b (with Lecanora prominens, Caloplaca erythrocarpa).
*Calicium glaucellum Ach. – On dead wood of Castanea sativa, E of Koutsamatados, 280–400 m,
35°24'14.0''N/23°41'13.9''E, 12.06.2005, leg. S. Abrahamczyk s.n. (GOET, det. T. Spribille).
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*Calicium salicinum Pers. – On snag in moist ravine, c. 900 m. (29): 13732.
**Caloplaca aquensis Houmeau & Cl.Roux – On calcareous conglomerate and exposed limestone near
sea level on the southern coast of Crete. (32): 13757 (det. C. Roux); (34): Schultz 09456.
Caloplaca aurantia (Pers.) Hellb. – On calcareous rock; sea level to about 700 m. (6): 12973, 12984; (7):
13002, 13003; (17): 13406, 13418; (31): 13755; (34): Schultz 09450b (with Verrucaria nigrescens).
Caloplaca biatorina (A.Massal.) J.Steiner – On exposed limestone boulders, c. 1000 m. (33): Schultz 09405.
Caloplaca cerina (Hedw.) Th.Fr. – On phrygana shrubs and trunks and branches of Acer sempervirens,
Ceratonia siliqua, Pyrus spinosa, Quercus coccifera and planted Pinus halepensis, near sea level to c.
1700 m. (1): 12831; (2): 12833; (7): S.R. Gradstein s.n. (GOET); (10): 13124, 13127, 13128, 13203;
(26): 13593; (29): 13678, 13724.; (33): Schultz 09422, 09449.
Caloplaca chalybaea (Fr.) Müll.Arg. – On large exposed limestone boulders, c. 1000 m. (33): Schultz
09420.
Caloplaca citrina (Hoffm.) Th.Fr. – On highly enriched bird rock in front of goat stable also used as a
pigeon roost, c. 200 m. (18): 13441.
Caloplaca crenularia (With.) J.R.Laundon s.l. – On siliceous rocks, 220–900 m. (5): 12907; (11): 13245;
(24): 13537; (25): 13559.
**Caloplaca crenulatella (Nyl.) H.Olivier – On concrete retaining wall in shade, 350 m. (22): 13490.
Caloplaca erythrocarpa (Pers.) Zwackh – On siliceous rocks in montane phrygana, 800–1000 m. (25):
13557, 13569, 13758, 13766; (33): Schultz 09403, 09404c (with Lecanora prominens, Buellia subdisciformis).
Caloplaca flavescens (Huds.) J.R.Laundon – Mainly on limestone rock walls, c. 500–1000 m. (6): 12976;
(8): 13034 (sub Lobothallia radiosa), 13054; (28): 13599.
Caloplaca flavorubescens (Huds.) J.R.Laundon subsp. flavorubescens – On twigs of Quercus coccifera
and Rhamnus lycioides subsp. oleoides, 1000 m. (29): 13695, 13727.
Caloplaca haematites (St.-Amans) Zwackh – On trunks and branches of Acer sempervirens, Cupressus
sempervirens, Juglans regia, Olea europaea and Pyrus spinosa, sea level to c. 1700 m. (7): V. Wagner
s. n. (GOET); (8): 13028; (10): 13141, 13216, 13219; (14): 13368; (23): 13502, 13503; (29): 13725.
Cretan material has smaller ascospores than described for C. haematites but is clearly distinguishable
from C. cerina on account of the disc colour and well-developed grey thallus.
Caloplaca herbidella (Hue) H.Magn. – On bark of Castanea sativa, Cupressus sempervirens and
Pinus brutia, 500–900 m. (14): 13327, 13360, 13370; (16): 13400; N of Agia Irini, 35°20'45.9''N/
23°49'27.8''E, 800 m, 08.06.2005, leg. S. Abrahamczyk s. n. (GOET).
A montane species, on Crete perhaps limited to the Levka Ori; previously known only from Omalos
(GRUBE et al. 2001).
Caloplaca inconnexa (Nyl.) Zahlbr. – Mainly on Aspicilia species over siliceous rock and persisting in
part on lichen-free rock, also on Aspicilia over limestone, 800 – c. 1500 m. (8): 13050; (10): 13093;
(25): 13759.
*Caloplaca marmorata (Bagl.) Jatta – On limestone, 1000 m. (8): 13039, 13052, 13061.
Other Greek reports are from Euboea (NAVARRO-ROSINÉS & HLADUN 1996), and several other Aegean
islands (SIPMAN & RAUS 1999, 2002, as cf.).
*Caloplaca navasiana Nav.-Ros. & Cl.Roux – On calcareous rocks in the littoral zone. (17): 13409 (ver.
C. Roux).
Previously known from mainland Greece, Cyprus (LITTERSKI & MAYRHOFER 1998), and the western
Mediterranean (NAVARRO-ROSINÉS & ROUX 1995).
*Caloplaca obscurella (Körb.) Th.Fr. – On Quercus macrolepis trunk, 370 m. (19): 13464 (det. H.
Sipman).
*Caloplaca polycarpa (A.Massal.) Zahlbr. – Parasitic on Bagliettoa on partly shaded calcareous rock, c.
200 m. (7): 13001.
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Caloplaca variabilis (Pers.) Müll.Arg. s.l. – Found on three distinctly different substrates: 1) on siliceous
rock, 800–1500 m: (10): 13107; (25): 13554; 2) on calcareous rock, 500–1050 m: (2): 12841; (8):
13035, 13049; (30): 13739; (34): Schultz 09457b; 3) on fine twigs of Quercus coccifera, 1000 m: (29):
13700 (! H. Sipman).
We interpret the species here to include forms that approach C. circumalbata (Delile) Wunder. Material
from siliceous rock has larger ascospores on average (13–18 × 5.5–8.5 µm) than specimens from calcareous rock (11–14.5 × 5.0–8.5 µm), but the former does not appear to correspond to C. diphyodes
(Nyl.) Jatta nor to any other taxonomic delineations in WUNDER (1974). The specimen from Quercus
twigs has ascospores 10.5–12.5 × 4.8–7.0 µm and appears to be the first report of a member of this
group as a true epiphyte; the site where it occurred did not appear to be particularly influenced by dust,
and in fact included many typical Lobarion species.
Caloplaca xantholyta (Nyl.) Jatta – On limestone rock wall, c. 600 m. (6): 12970.
Candelariella aurella (Hoffm.) Zahlbr. – On bases of phrygana shrubs and on limestone, 500–1050 m.
(2): 12837; (8): 13064.
*Candelariella faginea Nimis, Poelt & Puntillo – On bark of Acer sempervirens and Berberis cretica,
also on wood of Cupressus snag, 1000–1500 m. (8): 13027; (9): 13067; (10): 13129, 13143.
One of the specimens (13067) resembles the closely related C. xanthostigma in having small thallus
granules c. 0.1 mm diam., but agrees with C. faginea in possessing asci with variable ascospore numbers in one and the same apothecium.
**Candelariella plumbea Poelt & Vĕzda – On siliceous rock, 900 m. (25): 13563, 13565.
Described from Austria (Poelt & Vĕzda 1976) and subsequently reported only from the former
Yugoslavia and northern Italy.
*Candelariella reflexa (Nyl.) Lettau – On Cupressus sempervirens bark in shaded gorge, c. 400 m. (6):
12955.
**Candelariella sp. 1 – On bark of Cupressus sempervirens branches, c. 1200 m. (10): 13154, 13205.
Ascospores perfectly round, 4–5 µm in diameter, variably 8, 16 or 24 per ascus; apothecia strongly
convex, <0.5 mm diam.; thallus consisting of small granules to 0.1 mm diam. This appears to be the
first species of Candelariella with sphaerical ascospores. We hesitate to describe it until we have seen
more specimens, as the material is quite scanty.
Candelariella vitellina (Hoffm.) Müll.Arg. – On siliceous rock, c. 800 m. (25): 13556.
*Catapyrenium psoromoides (Borrer) R.Sant. – On bark of Quercus macrolepis, 370 m. (19): 13469.
Catillaria chalybeia (Borrer) A.Massal. var. chalybeia – On siliceous and calcareous rock, wood and
Platanus bark, 220–1000 m. (5): 12909 (sub Tephromela atra); (11): 13245 (sub Caloplaca crenularia); (13): 13286-B; (29): 13735.
Catillaria chalybeia var. chloropoliza (Nyl.) H.Kilias – On siliceous rock of shepherd’s hut in open
fields, 800 m. (25): 13555, 13558.
Catillaria nigroclavata (Nyl.) Schuler – On Olea europaea branches and on fencepost in village, 220–
1000 m. (4): 12860 (sub Lecidella elaeochroma); (11): 13262; (20): 13480 (sub Pertusaria leioplaca);
(33): Schultz 09424a, 09432a (with Lecidella elaeochroma).
Spribille 13480 is a form in which most apothecia contain asci with 8 ascospores/ascus, but some have
16 ascospores per ascus and the ascospores are 4.8–5.5 × 1.8–2.0 µm. This appears to represent a transition in the polysporous state between Catillaria nigroclavata and the recently described Catillaria
praedicta Tretiach & Hafellner (TRETIACH & HAFELLNER 1998). Interestingly, the specimen appears
to be at least facultatively lichenicolous on Pertusaria leioplaca.
*Catinaria atropurpurea (Schaer.) Vězda & Poelt – On Cupressus sempervirens bark, 900 m. (14): 13354.
*Cladonia cervicornis (Ach.) Flot. subsp. cervicornis – On soil beneath shrubs in phrygana; c. 200 m.
(18): 13425.
PAPP et al. (1998) reported the similar C. cervicornis subsp. verticillata from near Chania, but that
subspecies has better developed podetia and less dominant squamules.
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Cladonia convoluta (Lam.) Anders – On soil in phrygana, c. 100–300 m. (5): 12878; (18): 13426, 13438.
Cladonia foliacea (Huds.) Willd. – On soil in phrygana, c. 100–500 m. (2): 12844; (7): 12991.
Cladonia furcata (Huds.) Schrad. subsp. furcata – On soil in phrygana, 200–800 m. (18): 13429; (25):
13574, 13583, 13585.
Cladonia furcata subsp. subrangiformis (Sandst.) Abbayes – On soil in phrygana, 220–800 m. (5):
12880, 12887; (11): 13252; (25): 13584.
*Cladonia humilis (With.) J.R.Laundon – On bare soil bank in shade, 700 m: (24): 13540; also on moss
on trunk of Phillyrea latifolia, 1000 m: (29): 13712. TLC: atranorin, fumarprotocetraric acid.
Cladonia pocillum (Ach.) Grognot – On moss cushions on rock outcrop, sea level to c. 750 m. (5):
12869, 12870; (34): Schultz 09459.
Cladonia pyxidata (L.) Hoffm. – On soil in phrygana and road cuts, and in moss on canyon walls, rarely
epiphytic on Platanus orientalis and Quercus macrolepis in humid localities; 180–800 m. (2): 12845;
(5): 12868, 12871, 12877; (11): 13254; (13): 13293; (18): 13430; (23): 13491; (24): 13513; (25):
13581; (30): 13740.
Clauzadea immersa (Weber) Hafellner & Bellem. – On limestone rocks in phrygana and canyon walls,
500–700 m. (5): 12884; (6): 12969.
Clauzadea metzleri (Körb.) D.Hawksw. – On limestone outcrops and rock walls, 90–500 m. (1): 12830
(det. C. Roux); (6): 12963; (7): 13006.
*Collema coccophorum Tuck. – On calcareous soil crust, c. 1000 m. (33): Schultz 09416.
A species common worldwide in dry regions.
*Collema conglomeratum Hoffm. var. conglomeratum – On bark of Quercus, c. 1000 m. (33): Schultz
09425b, 09438a.
Similar to Collema ligerinum in growth form and substrate but well separated by the constantly 2celled, fusiform ascospores.
Collema crispum (Huds.) Weber ex F.H.Wigg. var. crispum – On calcareous soil crusts, 90–1000 m. (1):
12827; (33): Schultz 09414.
Collema crispum var. metzleri (Arnold) Degel. – On soil in phrygana and on lime pebbles, 180–510 m.
(18): 13436; (27): 13594. (30): 13737.
Collema cristatum (L.) Weber ex F.H. Wigg. – On soil, pebbles, rock walls and moss over rock, 180–1700
m. (5): 12886; (6): 12974; (7): 13009, (10): 13089. (25): 13575; (30): 13738; (33): Schultz 09413.
Collema flaccidum (Ach.) Ach. – On Platanus orientalis bark, 330 m. (13): 13290.
*Collema fragile Tayl. – On dry limestone rocks near seashore. (17): 13420.
Otherwise known in Greece from Corfu (DEGELIUS 1954).
Collema furfuraceum (Arnold) Du Rietz – On Castanea sativa, Cupressus sempervirens, Quercus
ilex and Quercus macrolepis, 370–700 m. (6): 12989; (16): 13402; (19): 13448, 13459 (mixed with
Collema nigrescens); (24): 13507, 13529 (with C. nigrescens); (33): Schultz 09441a, 09445b.
The species is characterized by broad, distinctly ridged and pustulate lobes with cylindrical to coralloid
isidia. Apothecia are occasionally formed.
*Collema cf. latzelii Zahlbr. – On limestone rock faces, c. 700 m. (28): 13601, 13614-B.
Collema multipunctatum Degel. – On bark of Cupressus sempervirens and Quercus spp., 500–800 m. (6):
12954 (sub Leptogium teretiusculum); (24): 13512; in Quercus-Hain, Bezirk Rethimnon, Kloster Arcadi
östlich Karoussi südöstlich Rethimnon, 3.10.1982, T. Feuerer & N. Höhne 12671, det. M. Schultz (HBG).
Collema nigrescens (Huds.) DC. – On bark of Quercus pubescens, 370–1000 m. (19): 13459;
(24): 13522, 13529; (33): Schultz 09430a (with Pleurosticta acetabulum), 09445a.
Although this species is not uncommon, it was apparently overlooked in early studies, and reported as
new to Crete only recently by GRUBE et al. (2001) from Arcadi Monastery.
*Collema subflaccidum Degel. – On trunk of Quercus ilex, c. 1000 m. (33): Schultz 09441c.
The species is separated from Collema furfuraceum by the lack of distinct ridges and pustules on
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Herzogia 19 (2006)
the broadly rounded lobes as well as the presence of very fine granulose isidia. Also known from
Cephalonia, Greece (DEGELIUS 1954, as C. subfurvum) and Cyprus (LITTERSKI & MAYRHOFER
1998).
*Collema tenax (Sw.) Ach. em. Degel. – On soil and sand-filled rock clefts and occasionally spreading
onto calcareous rock, at all sampled elevations. (6): 12957; (8): 13040; (10): 13090 (cf.); (17): 13420;
(21): 13485; (25): 13573; (28): 13611; (33): Schultz 09411; (34): Schultz 09407, 09467.
Collema undulatum Flot. – On limestone, 1500–1800 m; (10): 13098; Kalk, Bezirk Heraklion, IdaGebirge, am Aufstieg von der Analipsis-Kapelle zum Koussakas, 1800 m, 24.9.1982, T. Feuerer & N.
Höhne 12603, det. M. Schultz (HBG).
Known from Italy, Romania and Syria (DEGELIUS 1954) and the report by KLEINIG (1966) from the
island of Dia.
Degelia plumbea (Lightf.) P.M.Jørg. & P.James – Epiphytic on trunks of Castanea sativa, Phillyrea
latifolia and Quercus coccifera, 500–1000 m; (16): 13387; (29): 13659, 13660, 13716; N of Agia Irini,
35°20'45.9''N/23°49'27.8''E, 800 m, 08.06.2005, leg. S. Abrahamczyk s.n. (GOET).
Both the ‘Mediterranean’ and typical forms of the species are present in our material (P.M. Jørgensen,
pers. comm.). Degelia plumbea always occurs in the Cretan equivalent of ‘Lobarion’ communities,
typically associated with Bacidia spp., Fuscopannaria olivacea, Nephroma laevigatum and Physconia
distorta but usually lacking Lobaria species.
Dermatocarpon miniatum (L.) W.Mann – On vernally seepy rock, 1050–1500 m. (8): 13044, 13059;
(10): 13087, 13096.
Diploschistes diacapsis (Ach.) Lumbsch – On soil in phrygana, sea level to c. 800 m. (6): 12959; (7):
12993; (18): 13424; (25): 13579, 13580; (34): Schultz 09460.
Diploschistes muscorum (Scop.) R.Sant. – On soil and plant detritus in phrygana, 750 m. (5): 12879.
Diploschistes ocellatus (Vill.) Norman – Over calcareous walls of ruins, 180 m. (30): 13747.
Diplotomma alboatrum (Hoffm.) Flot. – On bases of phrygana shrubs and bark of Acer sempervirens,
c. 500 m. (2): 12839; (6): 12930.
Diplotomma chlorophaeum (Hepp ex Leight.) Szatala – On siliceous rock, 900 m. (25): 13559 (sub
Caloplaca crenularia), also 13765, as cf. (sub Aspicilia cupreoglauca).
Diplotomma epipolium (Ach.) Arnold – On siliceous rock of shepherd’s hut, c. 800 m. (25): 13562.
Dirina massiliensis Durieu & Mont. f. massiliensis – On N-facing limestone cliff close to sea, c. 100 m.
(7): 13016.
*Endocarpon adsurgens Vain. – On moss over vernally moist limestone rock outcrop, 1050 m. (8): 13060.
The squamules are appressed, not ascending, suggesting E. pusillum, but the ascospores are colourless
and relatively small (25–32 × 12–13 µm).
Evernia prunastri (L.) Ach. – On trunks of Pinus brutia and branches of Quercus coccifera, 900–1000
m. (14): 13329; (29): 13655, 13662.
Fulgensia fulgida (Nyl.) Szatala – Terricolous in phrygana and on soil in archaeological excavation,
180–200 m. (18): 13423; (30): 13741.
Fulgensia schistidii (Anzi) Poelt – On Schistidium over rock, 1500 m. (10): 13099.
Fulgensia subbracteata (Nyl.) Poelt – On calcareous soil crust, c. 1000 m. (33): Schultz 09410; (34):
Schultz 09458.
**Fuscopannaria aff. atlantica P.M.Jørg. – On bark of Platanus orientalis trunks, 310 m. (12): 13282
(det. P. M. Jørgensen).
This recently described species (JØRGENSEN 2005) is otherwise known only from western Europe, east
to Italy. Fertile material is needed to be sure of the identification.
Fuscopannaria mediterranea (Tav.) P.M.Jørg. – On bark of Platanus orientalis and Quercus pubescens,
330–560 m. (12): 13281; (23): 13496 (B, BG).
Fuscopannaria olivacea (P.M.Jørg.) P.M.Jørg. – On trunks of Castanea sativa, Cupressus sempervirens,
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Phillyrea latifolia, Platanus orientalis, Quercus coccifera, Q. macrolepis, and Q. pubescens, 330–1000
m. The most common epiphytic Fuscopannaria on Crete. (13): 13284; (14): 13349, 13350, 13356;
(16): 13386; (19): 13442, 13444, 13445; (23): 13495; (24): 13519; (29): 13644, 13658, 13714 (BG),
13715; (33): Schultz 09423.
There appears to be some variability in the degree of pointedness of the perispore, with some individuals from locality (29) exhibiting at times more or less pointed perispores while others are neatly
rounded.
*Heppia solorinoides (Nyl.) Nyl. – On calcareous soil crusts, c. 1000 m. (33): Schultz 09409.
Easily recognized by the whitish squamules with deeply cracked surface.
*Hyperphyscia adglutinata (Flörke) H.Mayrhofer & Poelt – On bark of Olea europaea trunk, 220 m.
(11): 13260.
*Lecania cyrtellina (Nyl.) Sandst. – On knot in bark of Cupressus sempervirens, c. 1400 m. (10): 13221.
Lecania erysibe (Ach.) Mudd – On calcareous rock, 400 m. (21): 13486.
*Lecania naegelii (Hepp) Diederich & P.Boom – On Quercus coccifera branch, 1000 m. (29): 13688.
Lecania spadicea (Flot.) Zahlbr. – On limestone rocks at or near sea level, locally abundant. (17): 13412;
(34): Schultz 09452.
*Lecania sylvestris (Arnold) Arnold – On limestone rock, c. 500 m. (6): 12967 (sub Solenopsora olivacea).
Lecanora albescens (Hoffm.) Branth & Rostrup – On siliceous rock, 750–1400 m. (5): 12896 (sub
Verrucaria nigrescens); (10): 13077, 13079 (sub Lecidella anomaloides).
Lecanora campestris (Schaer.) Hue var. campestris – On siliceous rock under dense macchia, 220 m.
(11): 13244 (det. C. Roux).
Lecanora carpinea (L.) Vain. – On Acer sempervirens and Pyrus spinosa, 1000–1500 m. (10): 13134,
13135; (29): 13719 (sub L. chlarotera).
Lecanora chlarotera Nyl. – On trunks and branches of trees and shrubs, the most common epiphytic
Lecanora species on Crete, sea level to 1700 m. (2): 12836; (4): 12848; (5): 12919, 12929, 12943,
12938, 12952; (9): 13068; (10): 13130, 13136, 13145, 13146, 13197, 13213; (11): 13256; (14): 13313,
13320, 13339, 13364, 13376; (19): 13467; (20): 13484; (23): 13500; (24): 13530, 13531; (26): 13590;
(29): 13690, 13719; (33): Schultz 09429.
*Lecanora cf. crenulata Hook. – On limestone rocks in phrygana, 750 m. (5): 12890.
Our material has ascospores 8.2–10.0 × 3.8–6.5 µm, agreeing with the dimensions provided by
HAWKSWORTH & DALBY (1992) but these dimensions are clearly smaller than those provided by
CLAUZADE & ROUX (1985).
Lecanora dispersa (Pers.) Sommerf. – On exposed limestone, 750–1050 m. (5): 12889; (8): 13063 (sub
Verrucaria nigrescens).
*Lecanora aff. hypoptoides (Nyl.) Nyl. – On bare wood of fence post, c. 900 m. (4): 12859 (sub Lecanora
saligna).
Characterized by lead gray to brownish-tinged apothecia 0.1–0.3 mm diam. with retreating margin, epihymenium with bluish green, K- or K+ intensifying, HNO3+ mauve pigment, simple, narrowly ellipsoid
ascospores, and Lecanora-type ascus. Our material has small ascospores 7.0–7.8 × 2.0–3.0 µm.
*Lecanora leuckertiana Zedda – On limestone rock faces, c. 500–800 m. (6): 12964, 12965, 12985; c.
1 km S Imbros an der Straße nach Hora Sfakion, O-exponierte Kalkschrofen über dem Eingang zur
Imbros Schlucht, c. 800 m; 35°15'N/24°10'E, 13.05.1997, H. Mayrhofer 13939 & R. Ertl (GZU, det.
L. Zedda). TLC (12964, 12965, 12985): usnic and isousnic acid, zeorin.
Known in Greece from the Aegean islands of Paros (ZEDDA 2000), Kalimnos and Kos (SIPMAN &
RAUS 2002), and Ikaria (SIPMAN et al. 2005) and probably widespread.
Lecanora muralis (Schreb.) Rabenh. s.l. – On siliceous rocks, 1400 m. (10): 13144. TLC: usnic acid, zeorin.
Members of this species complex are more common on Crete than indicated here and were not systematically sampled in this survey.
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Lecanora polytropa (Hoffm.) Rabenh. – In crevices of limestone rock wall, 1700 m. (10): 13092.
The specimen does not appear to differ morphologically from typical L. polytropa, which is otherwise
considered a strict acidophile.
*Lecanora prominens Clauzade & Vězda – On exposed calcareous sandstone near sea level. (34):
Schultz 09404a.
Lecanora pruinosa Chaub. – On exposed limestone, sea level to 1000 m. (6): 12970 (sub Caloplaca
xantholyta); (8): 13036; (34): Schultz 09454 (sub Solenopsora olivacea). TLC (13036): xanthones.
Lecanora rugosella Zahlbr. – On trunks of Acer sempervirens and Platanus orientalis, 330–1000 m.
(13): 13297; (29): 13623.
Lecanora rupicola (L.) Zahlbr. subsp. sulphurata (Ach.) Leuckert & Poelt – On siliceous rock, 800 m.
(25): 13549, 13772.
*Lecanora saligna (Schrad.) Zahlbr. – On wood of Cupressus snag and village fencepost, 900–1400 m.
(4): 12857, 12859; (10): 13232. TLC (12859): isousnic acid.
*Lecanora symmicta s.l. – Three chemical races were found: 1) with usnic acid and zeorin: On bark of
Olea europaea, on phyllite rock faces, also on limestone, 110–1050 m. (8): 13041; (11): 13266; (20):
13481, 13483; Deres, 35°27'50''N/23°50'09''E, 117 m, 17.06.2005, leg. S. Abrahamczyk s. n. (GOET);
2) with usnic acid only: On moss over rock and over bark of Quercus ilex and directly on bark of Q.
macrolepis, 370 – c. 500 m. (6): 12918, 12941; (19): 13471-B; and 3) with usnic acid and unidentified
xanthone in Rf class 7 [A, B, C]: on bark of Pinus brutia, 900 m. (14): 13308.
We found only the leprose, sterile form. SIPMAN & RAUS (2002) refer material with usnic acid and zeorin to L. expallens, but that species contains thiophanic acid as a major constituent (TØNSBERG 1992).
Pending a revision of this group, we prefer to refer the collections to L. symmicta, which contains usnic
acid and zeorin (ZEDDA 2000).
Lecidella anomaloides (A.Massal.) Hertel & H.Kilias – On siliceous rock, c. 1300 m: (10): 13079; calcareous rock, 1050 m: (8): 13057, 13058.
This species is normally associated with siliceous rock, but the material seems typical.
Lecidella carpathica Körb. – On siliceous rock, c. 1500 m. (10): 13073.
Lecidella elaeochroma (Ach.) M.Choisy – One of the most common epiphytic lichen species on Crete,
on nearly all tree species, also on bare wood, 330–1700 m. (4): 12850, 12855; (5): 12864; (6): 12928,
12944, 12950; (8): 13142; (10): 13117, 13120, 13207, 13218, 13223; (13): 13296; (14): 13316, 13362;
(16): 13397; (19): 13473; (29): 13626, 13681, 13687; (33): Schultz 09431, 09432b.
Material from Acer sempervirens at high elevations (13117, 13120) may conform to the var. flavicans
(Ach.) Hertel. The chemical variation in this species on Crete would be worth detailed study.
Lecidella euphorea (Flörke) Hertel – On Platanus orientalis bark and Cupressus sempervirens wood,
220–1400 m. (10): 13195; (11): 13257.
*Lempholemma sp. 1 – On Platanus orientalis bark in moist ravines, c. 300–330 m. (12): 13279,
13286.
The material is richly fertile but cannot be assigned to any presently accepted European species; the
epiphytic habitat is also unusual.
*Lepraria lobificans Nyl. – On shaded vertical rock faces in humid Platanus orientalis ravine, 220 m.
(11): 13267, 13271 (both BG). TLC: atranorin, stictic acid and satellites, zeorin, unidentified cf. anthraquinones.
Lepraria nivalis J.R.Laundon – On moss over siliceous and calcareous rock faces and on branch of
Phillyrea latifolia, 220 – c. 700 m. (6): 12966 (BG); (11): 13264 (BG), 13273. TLC: atranorin, protocetraric acid (major).
Leprocaulon microscopicum (Vill.) Gams – On siliceous rock, trunks of Castanea sativa, 220–800
m. (11): 13247; (16): 13398 (BG); N of Agia Irini, 35°20'45.9''N/23°49'27.8''E, 08.06.2005, leg. S.
Abrahamczyk s.n. (GOET). TLC (13247): usnic acid, zeorin.
Leptogium biatorinum (Nyl.) Leight. – On limestone rock walls, c. 700 m; (6): 12977.
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Leptogium gelatinosum (With.) J.R.Laundon – In moss cushions over canyon walls and cliffs, and epiphytic in moss mats on branches of Phillyrea latifolia and Quercus coccifera, 220–1500 m. (10):
13080, 13081, 13238; (11): 13269; (28): 13606; (29): 13698, 13706.
*Leptogium palmatum (Huds.) Mont. [syn. L. corniculatum (Hoffm.) Minks, see JØRGENSEN & NASH
2004] – Terricolous in phrygana and in moss cushions on canyon walls, c. 700–900 m. (25): 13774;
(28): 13605.
Leptogium schraderi (Bernh.) Nyl. – On calcareous soil crust among mosses near sea level. (34): Schultz
09464.
Leptogium subtile (Schrad.) Torss. – On Olea europaea bark, 410 m. (20): 13482.
*Leptogium tenuissimum (Dicks.) Körb. – On soil and in crevices, 700–900 m. (25): 13570; (28): 13613;
on trunk of Quercus ilex, (33): Schultz 09443b, 09444.
*Leptogium teretiusculum (Wallr.) Arnold – Epiphytic on Cupressus sempervirens and Quercus macrolepis, also saxicolous once on siliceous rock in dense macchia; 220–700 m. (6): 12954; (11): 13246;
(19): 13462. (24): 13507 (sub Collema furfuraceum).
Lethariella intricata (Moris) Krog – On bark and wood of Cupressus sempervirens, c. 1400 m. (10):
13198, 13200, 13209, 13229.
This conspicuous species is known on Crete only from the greater vicinity of the mountain Gingilos,
above the Samaria Gorge south of the Omalos Plateau. The nearest known localities are apparently in
northern Greece (Spribille, unpubl.).
*Lichinella iodopulchra (Croz.) P.Moreno & Egea s.l. – On steep limestone boulders and overhangs near
sea level. (34): Schultz 09401, 09468a (with Anema decipiens).
Thallus often greyish pruinose, squamulose-lobate to lobate, lobes usually with revolute margin,
fruiting bodies hidden in swollen lobe margin.
*Lichinella sinaica (Galun & Marton) P.Moreno & Egea – On steep limestone boulder near sea level.
(34): Schultz 09406.
Smaller than previous species, squamules predominantly erect, peltate, ± cylindrical to flattened,
fruiting bodies hidden in tips of the squamules, usually epruinose. Described from Sinai Peninsula and
later reported from southeastern Spain, Yemen and the U.S.A.
*Lobaria amplissima (Scop.) Forssell – On branches of Acer sempervirens and Quercus coccifera, 1000
m. (29): 13620, 13639 (B, CONN).
The extremely reduced, completely dendriscocauloid specimens conform to the traditional concept of
the morphospecies referred to as Dendriscocaulon umhausense (Auersw.) Degel. However, molecular
analysis of 13639 within the context of a wider revision of this group (B. Goffinet, Storrs, Connecticut,
unpubl. data, 2004) confirms that this taxon agrees with the dendriscocauloid, blue-green phototype of
L. amplissima. Green foliose phototype L. amplissima is known in Greece from the Aegean island of
Ikaria (SIPMAN et al. 2005) and mainland localities in Epirus, NW Greece (Spribille, unpubl.). Reports
of Dendriscocaulon umhausense from elsewhere in the Mediterranean should also be revisited as to
whether they may also represent only the purely dendriscocauloid form of L. amplissima.
*Lobaria scrobiculata (Scop.) DC. – On Quercus coccifera branch in thick mats of the moss Leucodon
sciuroides, 1000 m. (29): 13631.
Lobothallia radiosa (Hoffm.) Hafellner – On exposed limestone and siliceous rock, c. 750–1500 m.
Three chemical races were found: 1) lacking lichen substances (on siliceous rock and limestone, [10]:
13084, 13102); 2) with norstictic acid and unknown substance (on limestone, [8]: 13034); and 3) with
stictic and norstictic acid, satellites and unknown substance (on limestone, [5]: 12908).
Megaspora verrucosa (Ach.) Hafellner & V.Wirth – On Cupressus sempervirens bark and moss over
bark, 1000–1400 m. (10): 13212, 13214; (33): Schultz 09433.
Melanelia exasperata (De Not.) Essl. – On branches of Acer sempervirens, Pyrus spinosa, Quercus coccifera
in montane localities, 1000–1400 m. (8): 13025; (10): 13111, 13186; (29): 13641, 13674, 13689, 13721.
Melanelia glabra (Schaer.) Essl. – On trunk of Quercus ilex, c. 1000 m. (33): Schultz 09448.
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*Micarea bauschiana (Körb.) V.Wirth & Vězda – On shaded, crumbling phyllite rock outcrop along
brook, 220 m. (11): 13263 (det. B. J. Coppins).
*Micarea micrococca (Körb.) Gams ex Coppins – On bark of Castanea sativa, 500 m. (16): 13390 (sub
Placynthiella icmalea; det. B. J. Coppins).
Micarea misella (Nyl.) Hedl. – On stalks of shrubs in dry phrygana, 250 m. (18): 13427 (det. B.J.
Coppins).
Mycobilimbia lurida (Ach.) Hafellner & Türk – On soil in siliceous rock crevices, 900–1500 m. (10):
13085; (25): 13586.
*Mycocalicium subtile (Pers.) Szatala – On dead Castanea wood, E of Koutsamatados, 280–400 m,
35°24'14.0''N/23°41'13.9''E, 12.06.2005, leg. S. Abrahamczyk s.n. (GOET, det. T. Spribille).
Neofuscelia attica (Leuckert et al.) Essl. – On siliceous rock of small shepherd’s hut and in open, moist
phrygana; 900 m. (25): 13567, 13775. TLC: norstictic acid (major), cf. alectoronic acid (minor), connorstictic acid (minor) and unidentified fatty acid (minor).
Nephroma laevigatum Ach. – On trunks of Castanea sativa and Phillyrea latifolia, 500–1000 m.
(16): 13385; (29): 13707; N of Agia Irini, 35°20'45.9''N/23°49'27.8''E, 800 m, 08.06.2005, leg. S.
Abrahamczyk s.n. (GOET).
KLEINIG (1966) also reports this species from the Omalos Plateau and Levka Ori above Thymia. It
appears to be infrequent at montane elevations.
Ochrolechia balcanica Verseghy – Epiphytic on bark of Acer sempervirens, Castanea sativa, Cupressus
sempervirens, Pyrus spinosa and Quercus coccifera, also on lignum of Cupressus snag; 500–1500 m.
(6): 12926; (10): 13119, 13138, 13234; (14): 13359, 13375; (16): 13393; (29): 13627, 13632, 13684;
(33): Schultz 09428, 09437.
Ochrolechia dalmatica (Erichs.) Boqueras (syn. Pertusaria dalmatica Erichs.) – On bark of Acer sempervirens, Castanea sativa, Pinus brutia and Quercus pubescens; 500–1100 m. (14): 13325; (16):
13391; (24): 13521; (29): 13628. TLC (all specimens): gyrophoric acid (major), ±atranorin (minor,
possibly a contaminant), ±low–running xanthones (minor).
Characterized by a thick, continuous verrucose thallus with a prominently zoned silvery white prothallus, C- cortex and medulla and defined to confluent, ±flat soralia with C+ pink-red soredia.
Ochrolechia pallescens (L.) A.Massal. – On bark at base of Pinus brutia, 900 m. (14): 13310. TLC (thallus and apothecium): gyrophoric acid (major), atranorin (minor), xanthone (minor).
*Opegrapha atra Pers. – On bark of Platanus orientalis in shaded, humid stream bottoms, 220–300 m.
(11): 13258; Aïr Kirgianis, 35°25'43.9''N/23°40'45.3''E, 300 m, 18.05.2005, leg. S. Abrahamczyk & E.
Bergmeier s.n. (GOET).
*Opegrapha ochrocincta Werner – On Platanus orientalis bark, 220 m. (11): 13285 (ver. C. Roux).
Opegrapha rupestris Pers. – On vertical limestone rock face in shaded gorge, c. 500 m. (6): 12983.
In addition to the typical form, we found a form with strongly clustered lirellae similar to O. conferta
Anzi but with slightly narrower ascospores: on concrete pavement, 100 m, (31): 13755 (sub Caloplaca
aurantia).
Opegrapha varia Pers. – On woody stalks of old Hedera helix and on Quercus macrolepis and Q. pubescens trunks, 370–700 m. (6): 12917; (19): 13453; (24): 13523.
*Parmelia saxatilis (L.) Ach. – On bark of Pinus brutia and Cupressus sempervirens and on wood of C.
sempervirens snags and scars, 900–1100 m. (10): 13190, 13211, 13227; (14): 13326.
Parmelina pastillifera (Harm.) Hale – On bark of Acer sempervirens, Pyrus spinosa and Zelkova
abelicea, c. 500–1500 m. (6): 12935; (8): 13031; (9): 13071; (10): 13109, 13125; (14): 13328 (sub
Parmelina tiliacea); (29): 13717.
Parmelina tiliacea (Hoffm.) Hale – On bark of Castanea sativa, Phillyrea latifolia, Pinus brutia, Quercus
coccifera and Q. macrolepis, 370–1000 m. (14): 13328; (16): 13405; (19): 13466; (24): 13509; (29):
13685, 13710; (33): Schultz 09446.
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This species appears to occupy more humid habitats on average than P. pastillifera, often in areas with
‘Lobarion’ communities.
**Peccania cerebriformis Henssen & Büdel – On limestone rock walls, c. 700 m. (28): 13614-B.
A distinct species with peltate, brain-like folded lobules or squamules. Described from Lanzarote and
later reported from southeastern Spain, Kuwait and Oman. This is the first record from the eastern
Mediterranean.
**Peccania teretiuscula (Flagey) Henssen – On calcareous rock near seashore and in phrygana, 0–750
m. (5): 12894; (7): 13011; (17): 13415.
This species was described from Algeria by FLAGEY (1895) and until now had been reported only from
the type collection. Further recent collections of this species along with a detailed description will be
provided in a separate publication (SCHULTZ & VAN DEN BOOM 2006). New to Europe.
Peltigera canina (L.) Willd. – On soil in phrygana and over a terrace retaining wall, 750 m. (5): 12873,
12902.
Peltigera polydactylon (Neck.) Hoffm. – Terricolous in calcareous phrygana and over phyllite rock ledges
in forest, once epiphytic on tree bases and lower tree trunks of Quercus pubescens, 750–800 m. (5):
12872; (24): 13505, 13535.
Pertusaria albescens (Huds.) M.Choisy & Werner – Montane, on bark of Acer sempervirens, Cupressus
sempervirens, Phillyrea latifolia, Pinus brutia, Quercus coccifera and Q. pubescens, also on wood
of Cupressus snag, 700–1700 m. (10): 13208, 13215; (14): 13306, 13343, 13365; (24): 13528; (29):
13622, 13646, 13679, 13709; (33): Schultz 09435. TLC: fatty acids.
In addition, we have seen several soft-isidiate specimens conforming to Pertusaria jurana Erichs.,
considered by some to be a synonym of P. albescens: (6): 12934; (10): 13231; (14): 13347, 13366.
TLC: fatty acids.
*Pertusaria coccodes (Ach.) Nyl. – On trunk of Quercus ilex, c. 1000 m. (33): Schultz 09425a (with
Collema conglomeratum), 09447.
Pertusaria hymenea (Ach.) Schaer. – On Castanea sativa, Quercus coccifera, Q. ilex, Q. macrolepis and
Q. pubescens, 370–1000 m. (6): 12945; (16): 13395; (19): 13447, 13460; (23): 13499; (24): 13516;
(29): 13640.
Pertusaria leioplaca DC. (syn. P. leucostoma A.Massal.) – On Olea europaea bark, 410 m. (20):
13480.
Pertusaria pertusa auct. – On bark of Acer sempervirens, Cupressus sempervirens, Olea europaea,
Pinus brutia and Quercus coccifera, 500–1300 m. (6): 12936; (10): 13228; (14): 13305, 13318, 13324,
13367; (23): 13493; (29): 13673.
*Pertusaria sp. 1 – On Cupressus sempervirens bark, c. 1400 m. (10): 13204, 13205 (sub Candelariella
sp. 1). TLC: no lichen substances.
The specimen appears to agree with a possibly undescribed taxon outlined by SIPMAN & RAUS (2002)
that in the past may have been confused with Pertusaria rhodiensis Erichs. The first author had the
opportunity to study the type of Pertusaria rhodiensis at W. The specimen consists of a small patch of
Pertusaria on a piece of branch, with the thallus apparently transitioning on one side into a Lecanora.
A small fragment was removed from the middle of the Pertusaria thallus for investigation of secondary metabolites, including two apothecia that were also sectioned and studied. TLC yielded norstictic
acid, thus in agreement with the original diagnosis of ERICHSEN (1938) of the thallus as being K+
yellow turning red and Pd+. In a detailed study of Pertusaria chemotypes, HANKO (1983) was unable
to detect lichen substances in a specimen labelled as P. rhodiensis at HBG and presumed to be an isotype, and accordingly concluded that P. rhodiensis lacked lichen substances. Another sample lacking
secondary constituents and producing no positive spot tests is known from Italy (Monte Pollino, leg.
Poelt, GZU) and was also studied by HANKO (1983) and subsequently also by SIPMAN & RAUS (2002),
though it was not seen in the present study. Our samples have in common with the Monte Pollino
specimen (as described by SIPMAN & RAUS 2002) the presence of only 1 ascospore per ascus (2/ascus
in the type of P. rhodiensis!) and the lack of lichen substances; in addition, our specimens have a K+
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purplish epithecium and ascospore wall. We agree with SIPMAN & RAUS (2002) that this may represent
an undescribed taxon that superficially closely resembles P. rhodiensis. To avoid any future confusion,
we hereby designate the W specimen (Rhodos, M. Attairo, 1100 m, auf Phillyrea, Mai 1933, K.H.
Rechinger, W) as lectotype of Pertusaria rhodiensis Erichs., Revue de Mycologie 3: 103 (1938).
*Phaeophyscia nigricans (Flörke) Moberg – On Quercus macrolepis, 370 m. (19): S. Abrahamczyk s.n.
(GOET); 13470.
Phaeophyscia orbicularis (Neck.) Moberg – On Zelkova abelicea trunk, 1100 m. (9): 13072.
*Phlyctis argena (Spreng.) Flot. – On bark of trunks and branches of Acer sempervirens, Cupressus
sempervirens, Pyrus spinosa, Quercus coccifera, often on the undersides of branches, also on dead
wood of Cupressus and Quercus ilex, 500–1300 m. (6): 12923, 12924, 12953; (10): 13226, 13239;
(14): 13307, 13315, 13330, 13355, 13363, 13382; (29): 13638, 13669, 13699, 13705. TLC: norstictic
and connorstictic acids.
This apparently overlooked species is perhaps the most common sorediate lichen in montane woodlands of western Crete.
Physcia adscendens (Fr.) H.Olivier – Common, on bark of Acer sempervirens, Cupressus sempervirens,
Olea europaea, Quercus coccifera, Q. macrolepis, Pinus spinosa, on phrygana shrubs and on rock,
near sea level to c. 1700 m. (2): 12832; (7): V. Wagner s.n. (GOET); (10): 13116; (14): 13358, 13377;
(19): 13452; (25): 13566; (29): 13651, 13677, 13703.
Physcia aipolia (Ehrh. ex Humb.) Hampe – Corticolous on Acer sempervirens, Pyrus spinosa, Quercus
coccifera and Q. pubescens, 700–1700 m. (5): 12865 (sub Physcia leptalea); (10): 13140; (24): 13525;
(29): 13642, 13648, 13675; (33): Schultz 09443a (with Leptogium tenuissimum).
Physcia biziana (A.Massal.) Zahlbr. var. leptophylla Vězda – On bark of Platanus orientalis, Quercus
coccifera trunks and native, montane Cupressus sempervirens trunks as well as planted low elevation
C. sempervirens in a monastery garden, 250–1400 m. (4): 12854; (7): Gradstein s.n. (GOET); (10):
13217; (11): 13255.
Physcia leptalea (Ach.) DC. – On twigs and branches of Acer sempervirens, Pyrus spinosa, Quercus
coccifera and Q. pubescens, 700–1000 m. (4): 12851; (5): 12865; (24): 13518; (29): 13703, 13718.
Physcia stellaris (L.) Nyl. – On bark of Acer sempervirens trunk, 1000–1700 m. (10): 13123, 13137;
(29): 13663.
Physconia distorta (With.) J.R.Laundon – Extremely common on Acer sempervirens, Castanea sativa, Cupressus sempervirens, Pinus brutia, Platanus orientalis, Pyrus spinosa, Quercus coccifera and
Zelkova abelicea, 330 – c. 1600 m. (4): 12852; (5): 12866; (6): 12922, 12948; (9): 13069; (10): 13180,
13182; (13): 13294; (14): 13341, 13372; (16): 13392; (29): 13671; (33): Schultz 09427.
*Physconia perisidiosa (Erichs.) Moberg – On Quercus macrolepis trunks, 370 m. (19): 13457, 13463.
Physconia subpulverulenta (Szatala) Poelt – On Castanea sativa, Pinus brutia and Pyrus spinosa, 500–
1050 m. (14): 13337, 13380; (16): 13399.
Physconia venusta (Ach.) Poelt – On Pinus brutia and Quercus coccifera, 1050 m. (14): 13323, 13346.
*Placidiopsis cinerascens (Nyl.) Breuss – On pale to reddish bare mineral soil in Phlomis fruticosaSarcopoterium spinosum and Phlomis-Euphorbia dendroides phrygana, c. 200–360 m. (18): 13433;
(21): 13487.
*Placidiopsis custnani (A.Massal.) Körb. – On soil in phrygana, 750 m. (5): 12874; (25): 13577.
**Placidium adami-borosi Szatala – On soil over rock on cool, north-facing limestone cliffs, 1500 m.
(10): 13100.
A rare species in the Mediterranean.
*Placidium imbecillum (Breuss) Breuss – On terrace retaining wall in open phrygana, 750 m. (5): 12876.
Placidium pilosellum (Breuss) Breuss – On compact (hardpan, vernal puddles!), reddish, bare mineral
soil on ridgetop in open phrygana, c. 200 m. (18): 13432.
*Placopyrenium trachyticum (Hazsl.) Breuss – On vernally moist calcareous rock, 1000 m. (8): 13045.
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*Placynthiella icmalea (Ach.) Coppins & P.James – On Castanea sativa bark, 500 m. (16): 13390.
Placynthium nigrum (Huds.) Gray – On limestone rocks and thin soil deposits over walls of ruins, sea
level to 1000 m. (8): 13043; (17): 13413, 13414; (30): 13748; (34): Schultz 09461.
*Placynthium subradiatum (Nyl.) Arnold – On steep limestone boulder, c. 1000 m. (33): Schultz 09408.
Platismatia glauca (L.) W.L.Culb. & C.F.Culb. – On wood of Cupressus sempervirens, c. 1400 m. (10):
13192.
Obviously a rare species on Crete. The only other record is from the mountain Gingilos (GRUBE et al.
2001), within 1 km of the present collecting site in the Levka Ori.
Pleurosticta acetabulum (Neck.) Elix & Lumbsch – Common and widespread on branches and trunks of
Acer sempervirens, Cupressus sempervirens, Phillyrea latifolia, Pinus brutia, Pyrus spinosa, Quercus
coccifera, Q. pubescens and Q. macrolepis, 370–1700 m. (6): 12933; (8): 13026; (10): 13110, 13189,
13210; (14): 13314, 13344, 13357; (19): 13468; (24): 13526; (29): 13643, 13652, 13711, 13723; (33):
Schultz 09442, 09430b (with Collema nigrescens).
*Porpidia cinereoatra (Ach.) Hertel & Knoph – On shaded siliceous rock in Quercus pubescens forest
and in dense macchia, 220–700 m. (11): 13243; (24): 13533. TLC (both specimens): confluentic acid,
unidentified substance.
Protoblastenia calva (Dicks.) Zahlbr. – On calcareous rock, 750–1700 m. (5): 12889; (10): 13101.
**Protoblastenia cyclospora (Körb.) Poelt – On limestone rock faces, c. 500 m. (6): 12978.
Pseudevernia furfuracea (L.) Zopf var. furfuracea – On bark of trunks and branches of Cupressus sempervirens, 1200–1500 m. (10): 13199, 13220.
Also reported from this locality and substrate by KLEINIG (1966), this continues to be the only known
site for this variety on Crete. P. furfuracea is thus represented by both varieties in the Omalos Basin at
sites a few kilometers from each other.
Pseudevernia furfuracea var. ceratea (Ach.) D.Hawksw. – On bark of Pinus brutia, 900 m. (14): 13342.
Otherwise reported from the Ida Mountains and Samaria (SZATALA 1943b, KLEINIG 1966, both as
Parmelia olivetorina). This seems to be the more widespread chemical race of P. furfuracea on Crete,
while the var. furfuracea is still known from only a single site. The incongruous distribution of the
two varieties on Crete mirrors the distributional separation of the chemotypes reported by SIPMAN et
al. (2005) from the Aegean island of Ikaria. We investigated both chemotypes using standard TLC but
could not separate olivetoric and physodic acids using this method, as they produce more or less identical bands in the three solvent systems A, B and C (CULBERSON et al. 1977); the differentiation here
is thus based solely on the C spot test.
Psora decipiens (Hedw.) Hoffm. – On soil in phrygana, 0–900 m. (2): 12843; (5): 12882, 12893; (7):
12992, 12994; (17): 13421 (O); (25): 13578, 13588; (30): 13744; (27): 13596 (O).
Psora pseudorussellii Timdal – On moss-covered limestone rock walls, 700 m. (28): 13607 (det E.
Timdal).
P. pseudorussellii was described from North America by TIMDAL (1986). The report from Crete by
GRUBE et al. (2001) was the first for Europe.
*Psorotichia vermiculata (Nyl.) Forssell – On exposed limestone boulders near sea level. (34): Schultz
09451.
Black areolate crust with immersed, dark red apothecia.
*Pterygiopsis affinis (A.Massal.) Henssen – On steep limestone boulders and overhangs near sea level.
(34): Schultz 09465c (with Thyrea confusa, Thelochroa montinii), 09469, 09470.
Blackish or greyish pruinose areolate crust with ± distinctly effigurate margin, marginal areoles usually short and broad, apothecia rarely seen, asci with 24–32 ascospores.
Ramalina farinacea (L.) Ach. var. farinacea – On branches of Quercus coccifera, 1000 m. (29): 13653.
Ramalina fastigiata (Pers.) Ach. – Epiphytic on branches of Pinus brutia, Pyrus spinosa and Quercus coccifera, 900–1000 m. (14): 13322, 13378; (29): 13654, 13656, V. Wagner s.n. (GOET); (33): Schultz 09440.
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Herzogia 19 (2006)
Ramalina fraxinea (L.) Ach. var. fraxinea – Corticolous on Acer sempervirens, Pyrus spinosa and
Quercus coccifera, 750–1500 m. (5): 12863; (10): 13126, 13184, 13188; (33): Schultz 09434.
*Ramalina fraxinea var. calicariformis Nyl. – On branches of Acer sempervirens and Quercus coccifera, 1000 m. (29): 13630, 13657; (33): Schultz 09439.
**Ramalina panizzei De Not. – On trunk of Quercus ilex, 1000 m. (33): Schultz 09436.
First report for southeastern Europe since it was excluded from the Greek flora by GRONER & LA
GRECA (1997).
*Ramalina subgeniculata Nyl. – Corticolous on Quercus coccifera branches, 1000 m. (29): 13661, 13635.
Rinodina calcarea (Arnold) Arnold – On calcareous rock, locally common, 1050 m. (8): 13042, 13046,
13047 (det. H. Mayrhofer), 13048, 13055.
**Rinodina excrescens Vain. – On wood on scarred Castanea sativa, 500 m. (16): 13401 (ver. H.
Mayrhofer).
A rarely collected species previously known in Eurasia only from the type locality in western Siberia,
two localities in Austria and one site on the Croatian island of Mljet (GIRALT et al. 1995), otherwise
from eastern North America. New to Greece and the eastern Mediterranean.
Rinodina immersa (Körb.) Arnold – On limestone rock in phrygana, sea level to 1000 m. (7): 13012;
(33): Schultz 09418b (with Aspicilia farinosa); (34): Schultz 09457c (with Rinodinella dubyanoides,
Caloplaca variabilis).
*Rinodina oleae Bagl. – On Ceratonia siliqua bark at sea level. (26): 13592 (det. H. Mayrhofer).
*Rinodina plana H. Magn. – On bark of Cupressus sempervirens and Quercus coccifera, 1000–1100 m.
(14): 13361; (29): 13683, 13701 (13701 det. H. Mayrhofer).
Rinodina pyrina (Ach.) Arnold – On Quercus coccifera branches and on shrub branches in phrygana,
500–1000 m. (2): 12840; (29): 13701-B.
Rinodina sophodes (Ach.) A.Massal. – Corticolous on branches and trunks of Acer sempervirens and
Pyrus spinosa, 1000–1500 m. (10): 13139, 13181; (29): 13726.
Rinodinella dubyanoides (Hepp) H.Mayrhofer & Poelt – On exposed limestone near sea level. (34):
Schultz 09457a.
Sarcogyne privigna (Ach.) A.Massal. – On siliceous rock in open meadow-like phrygana, 800 m. (25):
13546.
*Scoliciosporum umbrinum (Ach.) Arnold – On wood of Pinus brutia, 1000 m. (14): 13336 (BG, ver.
S. Ekman).
Solenopsora cesatii (A.Massal.) Zahlbr. var. cesatii – On thin soil over mortared wall and terricolous in
phrygana, 180–500 m. (6): 12987 (sub Solenopsora olivacea); (18): 13439; (30): 13749.
Solenopsora olivacea (Fr.) H.Kilias – On exposed limestone, from near sea level to c. 500 m. (6): 12987
(det. C. Roux); (34): Schultz 09453b, 09454.
Solenopsora vulturiensis A.Massal. – On siliceous rocks in dense macchia, 220 m. (11): 13249 (det. C.
Roux).
Squamarina cartilaginea (With.) P.James – On soil and on soil over rock, c. 1500 m. (10): 13086.
*Staurolemma omphalarioides (Anzi) P.M.Jørg. & Henssen – Epiphytic on bark of Castanea sativa,
Platanus orientalis, Quercus macrolepis and Q. pubescens, 370–560(–1000) m. (13): 13303; (16):
13388, 13403; (19): 13449; (23): 13494, 13497; (33): Schultz 09438b, 09441b; in Quercus-Hain, 500
m, Bezirk Rethimnon, Kloster Arcadi östlich Karoussi südöstlich Rethimnon, 03.10.1982, T. Feuerer
& N. Höhne 12670, det. M. Schultz (HBG); an Quercus, N-Exposition, 1000 m, Bezirk Lasithi, DiktiGebirge, Fahrweg von Kaminaki zum Afendis Hristos, etwa 1 km südlich des Ortes, 20.09.1982, T.
Feuerer & N. Höhne 12543, det. M. Schultz (HBG).
This appears to be a frequent species of humid, mid-elevation woodlands, rarely in higher altitude
woodlands.
Staurothele hymenogonia (Nyl.) Th.Fr. – On rocks in phrygana, 250 m. (7): 13008.
SPRIBILLE et al: Notes on the lichens and lichenicolous fungi of western Crete (Greece)
145
Tephromela atra (Huds.) Hafellner – On siliceous rock (phyllite, quartzite), 700–800 m: (5): 12897,
12909, 12910; (24): 13532; (25): 13547, 13548, 13763, 13764, 13773; also epiphytic once on Quercus
coccifera trunks, 1000 m: (29): 13666.
*Thelidium sp. 1 – On compact calcareous soil on and around archaeological excavations, c. 100 m. (1):
12828.
This sample comes from the type locality of Thelidium creticum J.Steiner (STEINER 1917), but does not
conform to the type. The type of T. creticum (at W) has ascospores 21–23 × 10 µm and a thin, epilithic
(!), brownish farinose thallus with partially immersed perithecia. Our new material has ascospores 23–26
x 12.5–13 µm and a grayish thallus on compact soil; it may be allied to T. obscurum (Garov.) Zschacke.
One of us (OB) also had an opportunity to study the only other specimen of T. creticum that has
been reported in the literature (Creta, Monophatsi, Asterusi-Gebirge bei Phurnopharangon, 300 m,
1.VII.1942, K. H. Rechinger fil., W; reported by SZATALA 1943b). The specimen has a white thallus,
larger perithecia with a thicker involucrellum and smaller, 1–3-septate ascospores (15–18 × 6.5–7.5
µm). It is not T. creticum, which is thus known only from the type collection.
*Thelochroa montinii A.Massal. – On steep limestone boulders near sea level. (34): Schultz 09465b
(with Thyrea confusa, Pterygiopsis affinis).
Thallus blackish to dark grey, very thin, powdery, apothecia very small with punctiform discs.
*Thyrea confusa Henssen – On steep limestone boulders near sea level. (34): Schultz 09465a (with
Thelochroa montinii, Pterygiopsis affinis).
Toninia aromatica (Sm.) A.Massal. – On soil in phrygana, c. 200 m. (7): 13010.
Toninia candida (Weber) Th.Fr. – In rock crevices, c. 200 m. (7): 13017 (det. E. Timdal).
Toninia diffracta (A.Massal.) Zahlbr. – On moss over rock, at sea level and 1700 m. (10): 13097; (34):
Schultz 09463. (13097 det. E. Timdal).
Toninia opuntioides (Vill.) Timdal – In rock crevices in shaded canyons, c. 700 m. (6): 12973; (28):
13612. TLC (both specimens): unidentified triterpenoids = ‘chemotype Y’ of TIMDAL (1991).
Toninia sedifolia (Scop.) Timdal – On soil in phrygana and archaeological excavations, 180–1700 m.
(1): 12826; (5): 12875; (7): 12996; (10): 13094; (28): 13602; (30): 13743. TLC: no substances (‘chemotype 0’) or with unknown depside or depsidone (‘chemotype C’ of TIMDAL 1991).
13602 is an anomalous, richly pycnidiate specimen conforming to ‘chemotype C’ of TIMDAL (1991)
(det. and TLC by E. Timdal, O).
Toninia tristis (Th.Fr.) Th.Fr. subsp. thalloedaemiformis (Szatala) Timdal – In rock crevices, 400 m.
(21): 13488.
*Verrucaria calciseda auct. – On periodically moist limestone, 1000 m. (8): 13053 (sub Verrucaria
fuscoatroides).
*Verrucaria fuscoatroides Servít – On periodically moist limestone, 1000 m. (8): 13053.
*Verrucaria geophila Zahlbr. – On reddish mineral soil in phrygana, 200–250 m. (7): 12997; (18): 13428.
Verrucaria macrostoma Dufour ex DC. – On bare mineral soil in open phrygana (f. terrestris de Lesd.)
and walls of amphitheatre in archaeological excavation, 180–200 m. (18): 13437; (30): 13752.
Verrucaria marmorea (Scop.) Arnold – On large exposed limestone boulder, 700–1000 m. (28): 13598;
(33): Schultz 09417a.
*Verrucaria murorum (Arnold) Lindau – On loose soil of bird perch on an altar-like structure in front of
sheepfold used mainly by goats and pigeons, c. 200 m. (18): 13440.
This species is widespread but scattered in central Europe, the Mediterranean and north Africa.
Verrucaria nigrescens Pers. – On vernally moist calcareous rock, sea level to 1000 m. (5): 12896; (8):
13045 (sub Placopyrenium trachyticum), 13063; (34): Schultz 09450a.
**Verrucaria thrombioides A.Massal. – On fine compact soil (dust) on walls of amphitheatre in archaeological excavation, 180 m. (30): 13746.
The studied amphitheatre walls were only laid bare c. 70 years ago by an Italian archaeological team,
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Herzogia 19 (2006)
but are already richly colonized by various macro- and microlichens. V. thrombioides is known with
certainty only from a few collections in the Mediterranean area. Most characteristic is the development
of the involucrellum, which envelops the entire perithecium, whereby only a thin outer zone contains
dark pigments. The involucrellum forms a thin, black, concentric line around the entire perithecium at
a short distance to the excipulum, which is also black.
*Verrucaria viridula (Schrad.) Ach. – On limestone rock wall, c. 400–800 m. (6): 12982.
**Verrucaria werneri Breuss – On upper surface of low concrete wall surrounding a giant Platanus
orientalis tree on the grounds of a former agricultural school, c. 350 m. (22): 13489.
This species is otherwise known only from the type locality at 1600 m in the Atlas Mountains of
Morocco. It was treated by BREUSS (1994a) as Verrucaria macrospora (Werner) Breuss, but this turned
out to be a later homonym of Verrucaria macrospora Hepp in Zoll.; a new name was provided for it
in BREUSS (1994b). The species resembles V. geophila but differs in having pyriform perithecia with
walls consisting only of the excipulum, whereas in V. geophila the perithecial wall is globose and consists of the dark excipulum and the complete involucrellum, with which it is unified, and thus thicker.
It is new to Europe.
Xanthoparmelia tinctina (Maheu & Gillet) Hale – On siliceous rock of shepherd’s hut in open field, 800
m. (25): 13564.
Xanthoria parietina (L.) Th.Fr. – On trunks and branches of Acer sempervirens, Olea europaea, Phillyrea
latifolia, Pyrus spinosa, Quercus coccifera, Q. macrolepis and on bases of phrygana shrubs, 100–1700
m. (2): 12835; (4): 12849; (5): 12861, 12862; (7): Gradstein s.n. (GOET); (10): 13113; (11): 13261,
13276; (14): 13381; (19): 13471; (29): 13686.
Non-lichenized, lichenicolous ascomycetes
*Arthonia varians (Davies) Nyl. – Parasitic on apothecia of Lecanora sp. and Lecidella elaeochroma
(‘A. intexta’), on bark of Acer sempervirens and Quercus coccifera branches, 1000–1500 m. (10):
13124 (sub Caloplaca cerina); (29): 13701-B (sub Rinodina pyrina).
*Sphinctrina turbinata (Pers. ex Fr.) De Not. – On Pertusaria sp. on Cupressus sempervirens bark, c.
1400 m. (14): 13204 (sub Pertusaria sp. 1).
Previously reported from Greece from Rhodos (LÖFGREN & TIBELL 1979).
*Toninia episema (Nyl.) Timdal – Parasitic on Aspicilia calcarea var. reagens on calcareous rock, 100
m. (7): 13014 (ver. C. Roux).
Toninia verrucariae (Nyl.) Timdal – Parasitic on endolithic Verrucaria on exposed limestone boulder
near sea level. (34): Schultz 09455a (with Caloplaca aquensis).
Acknowledgments
Special thanks are extended to Bernhard Goffinet for molecular analysis of the dendriscocauloid Lobaria amplissima
specimen. Assistance with collecting in the field was provided by Viktoria Wagner and Stefan Abrahamczyk. Special
thanks to them and Tassilo Feuerer for allowing us to cite some of their new records. The first author thanks Brian J.
Coppins, Stefan Ekman, Per Magnus Jørgensen, Claude Roux, Einar Timdal and Tor Tønsberg for helping him learn
various taxonomic groups and for naming critical material, as well as Helmut Mayrhofer and Harrie Sipman for examining specimens and providing helpful comments on the manuscript. Financial support for the Crete excursion by
the Universitätsbund Göttingen is gratefully acknowledged.
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Manuscript accepted: 5 April 2006.
Addresses of the authors
Toby Spribille* & Erwin Bergmeier, Department of Vegetation Analysis and Plant Diversity,
Albrecht von Haller Institute of Plant Sciences, Untere Karspüle 2, D-37073 Göttingen,
Germany. E-mail: tspribi@uni-goettingen.de*, erwin.bergmeier@bio.uni-goettingen.de
Matthias Schultz, Biozentrum Klein Flottbek und Botanischer Garten der Universität Hamburg,
Systematik der Pflanzen, Ohnhorststr. 18, D-22609 Hamburg, Germany.
E-mail: schultzm@botanik.uni-hamburg.de
Othmar Breuß, Naturhistorisches Museum, Burgring 7, A-1010 Wien, Austria.
E-mail: obreuss@bg9.at
*) corresponding author