Nova Hedwigia Vol. 91 issue 1–2, 1 –31 Stuttgart, August 2010 Article Mycorrhizal macrofungi diversity (Agaricomycetes) from Mediterranean Quercus forests; a compilation for the Iberian Peninsula (Spain and Portugal) Antonio Ortega, Juan Lorite* and Francisco Valle Departamento de Botánica, Facultad de Ciencias, Universidad de Granada. 18071 GRANADA. Spain With 1 figure and 3 tables Ortega, A., J. Lorite & F. Valle (2010): Mycorrhizal macrofungi diversity (Agaricomycetes) from Mediterranean Quercus forests; a compilation for the Iberian Peninsula (Spain and Portugal). - Nova Hedwigia 91: 1–31. Abstract: A compilation study has been made of the mycorrhizal Agaricomycetes from several sclerophyllous and deciduous Mediterranean Quercus woodlands from Iberian Peninsula. Firstly, we selected eight Mediterranean taxa of the genus Quercus, which were well sampled in terms of macrofungi. Afterwards, we performed a database containing a large amount of data about mycorrhizal biota of Quercus. We have defined and/or used a series of indexes (occurrence, affinity, proportionality, heterogeneity, similarity, and taxonomic diversity) in order to establish the differences between the mycorrhizal biota of the selected woodlands. The 605 taxa compiled here represent an important amount of the total mycorrhizal diversity from all the vegetation types of the studied area, estimated at 1,500–1,600 taxa, with Q. ilex subsp. ballota (416 taxa) and Q. suber (411) being the richest. We also analysed their quantitative and qualitative mycorrhizal flora and their relative richness in different ways: woodland types, substrates and species composition. The results highlight the large amount of mycorrhizal macrofungi species occurring in these mediterranean Quercus woodlands, the data are comparable with other woodland types, thought to be the richest forest types in the world. We point out that the presence of genera that are very well adapted to sclerophyllous Mediterranean woodlands with a potential use in afforestation or recovery programs, or being rare species, are listed in the Regional Red List of Endangered Macromycetes. Since, these woodlands suffer heavy environmental pressure, human and climate mediated, we conclude many species are approaching a high extinction risk, and it is urgent to apply legal and management measures, both,of national (Spain and Portugal) and European governments. Key words: mycorrhizal macrofungi, Quercus woodlands, diversity, affinity, conservation. *Corresponding author, e-mail: jlorite@ugr.es © 2010 J. Cramer in Gebr. Borntraeger Verlagsbuchhandlung, Stuttgart, Germany www.borntraeger-cramer.de DOI: 10.1127/0029-5035/2010/0091-0001 0029-5035/2010/0091-0001 $ 7.75 1 Introduction Approximately 20000–25000 fungi species described throughout the world are considered to be ectomycorrhizal (Rinaldi et al. 2008). Mycorrhizas have widespread occurrence among land plants and are increasingly believed to have played an important role in the successful colonization of the land by plants (see Wang & Qiu 2006, for a review), inhabiting healthy root tissues of most terrestrial plants and playing a key role in the maintenance of vegetation, contributing in a decisive way to the equilibrium and ecological stasis of most plant communities worldwide (Trappe 1996). Many ecosystems have received comparatively little attention (Comandini et al. 2006), given the ecological importance of host specificity for plant ectotrophic communities and the associated mycota (Hetrick 1984), mainly with regard to biogeochemical cycles of the major plant nutrients (Kennedy & Smith 1995). In the present work, we studied the genus Quercus (see Table 1) with key species regarding structure and quantitative composition of most woodland types in the western Mediterranean (Quèzel & Barbero 1985), growing in many cases together with several Mediterranean coniferous species, both natural and planted (Pausas et al. 2004). For these important plant habitats there is no compilation available focusing on describing the mycorrhizal component, and establishing comparisons of its diversity within different Quercus species as hosts. The present compilation is made in the Iberian Peninsula (Spain and Portugal), where these forest types are the most widespread, being Q. ilex s.l. the species with the biggest potential area (Blanco et al. 1997). Previous data, regarding the mycobiota of Quercus forests (e.g. Ortega & Lorite 2007, Laganá et al. 2000, 2002), suggest that there are many species of Agaricomycetes that form mycorrhizal associations with Mediterranean Quercus species. On the other hand, throughout the Mediterranean area, these woodland types are affected negatively by climatic change, fire (wild or human-mediated), deforestation, overgrazing, desertification, changes in farming practices, a spread of human settlement for tourism, etc. (Barbero et al. 1990, López-Bermudez & Albadalejo 1990). These environmental changes are associated with reductions in belowground microbial diversity (Ferrol et al. 2004) and, because of the key ecological functions of mycorrhizal symbiosis (Jeffries & Barea 2001), loss or decline of the mycorrhizal potential in degraded areas may limit the successful reestablishment of native plants (Requena et al. 2001). For the reasons above exposed, the aims of the work are: (i) to update the check-list of mycorrhizal macrofungi that fructifying in Quercus forests of Iberian Peninsula (Spain and Portugal); (ii) to analyse mycorrhizal diversity of different woodland types, dominated by Quercus spp. iii) to relate this mycorrhizal diversity with the diversity observed at regional scale. Materials and methods STUDY AREA: The Iberian Peninsula (Spain and Portugal) is located in the south-western edge of Europe, occupying about 581,300 km2. The Peninsula is structured around the high central plateau 2 (meseta in Spanish), surrounded by two main alpine massifs: the Pyrenees and the Baetics, both reaching more than 3,000 m (the highest being Mulhacén peak, 3,482 m). This peninsula can be divided into three general rock types: siliceous (schists, quartzites, granites, etc.), limestones, and marls. The Mediterranean part of the area occupies roughly two thirds of the whole area in the southern, central, and north-central part. It has a Mediterranean climate type with a dry summer period, with an average rainfall ranging between 150 and more than 1,500 mm per year (see Rivas Martínez & Loidi 1999a, for further details) and annual average temperature between 19°C (coastal zones in the southeastern part) and 4°C (summit areas). In phytogeographical terms, two main units have been described (RivasMartínez & Loidi 1999b), the first covering the western part (Portugal and central-western Spain) with predominantly siliceous rocks, and the second one formed by the eastern part (central-eastern Spain) with calcareous rocks predominating. COLLECTING DATA: First, we compiled the information, beginning with the selection of Mediterranean species of the genus Quercus that inhabit the Iberian Peninsula (according Amaral-Franco 1990), discarding the species with a restricted distribution area and/or not sampled in terms of macrofungi, such as Q. humilis and Q. lusitanica. The woodland types selected were: Q. canariensis, Q. faginea, Q. pyrenaica, Q. coccifera, Q. ilex subsp. ballota, Q. ilex subsp. ilex and Q. suber (see Table 1 for further information). Data on the association between Quercus spp. and ectomycorrhiza-forming fungi presented in this paper are based on reports of field observations of sporocarp associations with potential hosts. The data set contains information collected from a variety of published sources, including taxonomic monographs of specific groups of ectomycorrhizal fungal genera (e.g. Amanita, Boletus, Cortinarius, Lactarius, Tricholoma, hypogeous macrofungi, etc.) (Campoamor et al. 2000, Conca & Mahiques 2002, Conca & Tejedor 2005, Conca et al. 2006, Fernández & Undagoitia 2007, García & Pérez 2002, García et al. 1996, García-Alonso 2004, García-Bona 1994, Gutiérrez & Vila 2001, 2002, Heykoop & Esteve-Raventós 1994, Mahiques 1997, 1999a, 1999b, 1999c, 2001, 2002, 2004, 2006, Mahiques & Ballará 2005, Mahiques & Conca 2001, Mahiques & Ortega 1997, 2000, 2001, 2002, Mahiques & Tejedor 1999, 2001, Mahiques et al. 1995, Tejedor & Basso 2003, Tejedor & Mahiques 2001, 2003, Tejedor et al. 2004), the few previous surveys of fungi associated with selected Quercus species (Blanco & Moreno1986, Calonge et al. 2000, García-Bona 1989, Laganá et al. 2000, 2002), a large amount of local check-lists from the Iberian Peninsula (Conca et al. 1997, 2003, 2004, Esteve-Raventós 1987, Fernández et al. 2006, García-Bona 1987, Heykoop 1993, Heykoop & Esteve-Raventós 1994, Heykoop & Moreno 2007, Heykoop et al. 1992, Honrubia & Llimona, 1983, Llimona et al. 1995, 2000, Malençon & Bertault 1970, 1975, Malençon & LLimona 1980, Moreno & Esteve-Raventós 1988, Moreno et al. 1990, 2004a, 2004b, Moreno-Arroyo 2004, Moreno-Arroyo et al. 2005, Pérez de Gregorio 1996, Picón et al. 2004a, 2004b, Suárez et al. 2004, Undagoitia et al. 2007), as well as unpublished private collections and observations. Fungal taxa belonging to genera for which the mycorrhizal status is currently uncertain were not listed. Only records clearly mentioning (potential) Quercus hosts were included in the data matrix. DATA ANALYSIS: Firstly, to compare different features of the mycobiota in the studied woodlands types, different indexes were used: Occurrence-rate index (Ior) = number of species belonging to one genus present in a woodland type/total number of species of this genus inhabiting the Iberian Peninsula. Affinity index (Ia) = number of species belonging to one genus present in a woodland type/total number of species of this genus inhabiting all the Quercus woodlands. The first one (Ior) reflects the affinity of the genus in general terms, taking into account the whole genus, while the second one (Ia) reflects the affinity of the genus only inside the Quercus woodland types. Proportionality index (Ip) = number of the species belonging to one genus present in a woodland type/total number of species that inhabit a woodland type. Heterogeneity index (Ih) = number of species collected in a specific woodland type/number of species collected in all the woodland types. Similarity Jaccard index (see Magurran 2004) (Ij) = c/(a + b - c), where, a = number of species present in the woodland type A; b = number of species present in the woodland type B; c = number of species present, types A and B. Taxonomic diversity index: adapted from Margalef index (Magurran 2004) (Itd = S-1/lnN; where S = number of genera present in a specific woodland type, N = number of species present in this woodland type). Based on the raw table of the mycorrhizal taxa and their potential hosts (see Appendix 1), we performed a presence/absence matrix (available from the authors) of mycorrhizal species (605 rows) by Quercus taxa studied here (7 columns) and 4 additional columns that represent siliceous, indifferent, 3 Table 1. Main characteristics of the studied species of the genus Quercus (according Amaral-Franco 1990, Schwartz 1964, Valle & Lorite 2003). 1Bio. = Biotype (MP = Macrophanerophyte; NP = Nanophanerophyte). 2 L. type = Leaf type (Mar. = Marcescent; Scle. = Sclerophyllous). 3 Subs. = Substrate (Sil. = Siliceous; Ind. = Indifferent). 4Alt. = Altitudinal range. 5Therm. = Thermotype (T = Termomediterranean, M = Mesomediterranean, S = Supramediterranean). 6Ombr. = Ombrotype (Su = Subhumid, Hu = Humid, Hy = Hyperhumid, Sa = Semiarid, D = Dry) (according Rivas-Martínez & Loidi,1999a,1999b). 7 Distribution area. Taxa Bio.1 L. type2 Subs.3 Alt.4 Q. canariensis Willd. MP Mar. Sil. Q. coccifera L. NP Q. faginea Lam. MP Q. ilex L. subsp. ilex MP Scle. Mar. Scle. Ind.. Ind. Ind. Q. ilex subsp. ballota MP (Desf.) Samp. Q. pyrenaica Willd. MP Scle. Ind. Mar. Sil. Q. suber L. Scle. Sil. MP 0–1000 Therm.5 Ombr.6 Distrib. area7 T-M Su-Hu Iberian Peninsula and NW Africa 0–1200 T-M Sa-D W Mediterranean 200–1900 T-M-S Su-Hu Iberian Peninsula 0–1200 T-M D-Su Mediterranean Region 0–2000 T-M-S D-Su Mediterranean Region 400–2100 T-M-S Su-Hy W-SW France, Iberian Peninsula and N Africa (Morocco) 0–1500 T-M Su-Hy W Mediterranean sclerophyllous, and marcescent woodland types, respectively (see Table 1). Afterwards, we performed a matrix of genera by Quercus taxa (Table 2). The relationships between the different fungal species and Quercus species were established by indirect-gradient analysis, namely Detrended Correspondence Analysis (hereafter DCA; Hill & Gauch 1980), using the statistical package CANOCO for Windows v4.1 (ter Braak & Smilauer 1998), with non-transformed data and down-weighting rare-species options. For this analysis Q. coccifera was eliminated, because it acted as an outlier, due to the scarcity of available data, even though data belonging to this species appear in Table 2. Results Analysis of the Mycorrhizal Mycobiota (Agaricomycetes) of Quercus forests in Spain According to Tellería (2002), the Iberian Peninsula (Spain and Portugal) and Balearic Island have over 5000 species of Basidiomycota. There are 2000 catalogued species in Andalusia (Southern Spain) (Moreno-Arroyo et al. 2005). Nevertheless, other authors significantly increase this amount (e.g. Heykoop et al. 2003). Based on our own data (Ortega & Lorite 2007), we estimated that the ratio of mycorrhizal to saprotrophic species is 0.93 in the sclerophyllous woodlands of Andalusia. According to this ratio we expect in the Iberian Peninsula the number of mycorrhizal Basidiomycota to range between 2000 and 2300 taxa, mostly belonging to the class Agaricomycetes. With respect to the genera included here (see Table 2), we estimate that 1,500–1,600 taxa inhabit the Iberian Peninsula, so that the 605 taxa compiled here, corresponding only to the Quercus woodlands, represent a large amount of the total diversity of this genera in the study area, with Q. ilex subsp. ballota (416 taxa) and Q. suber (411) being the richest. 4 According to the data shown in Table 2 (excluding monospecific genera), we can arrange the genera into four categories, according the Affinity index (Ia): GROUP I (Ia = 0.7–1) high affinity to Quercus forests: Amanita (0.80), Boletus (0.78), Cantharellus (0.73), Clavariadelphus (0.75), Gymnomyces (1), Hydnum (0.75), Laccaria (0.80), Scleroderma (0.86) and Xerocomus (1),; GROUP II (Ia = 0.4–0.6) medium affinity to Quercus forests: Hebeloma (0.55), Hygrophorus (0.43), Hymenogaster (0.43), Inocybe (0.40), Lactarius (0.40), Melanogaster (0.60), Ramaria (0.40), Russula (0.45), Sarcodon (0.58), Thelephora (0.57), Tricholoma (0.50); GROUP III (Ia = 0.1–0.3) low affinity to Quercus forests: Albatrellus (0.17), Chalciporus (0.25), Cortinarius (0.25) Gautieria (0.20), Gyroporus (0.30), Hydnellum (0.30), Hysterangium (0.24) Leccinum (0.15), Phellodon (0.20), Pseudocraterellus (0.33), and Zelleromyces (0.25). Table 2 lists the quantitative data of the different woodland types, the most meaningful being: (i) Albatrellus and Leucortinarius are represented by only one species each and they have an acidophilous behaviour; the first one grows in areas under oceanic influence (where Q. suber predominate), while the second predominates in areas with a more continental character (governed by Q. pyrenaica). (ii) Hypogean species are characterized by a high affinity to sclerophyllous woodland types over calcareous substrate, with the exception of Hymenogaster populetorum Tul. and Hysterangium rickenii Soehner, that have been collected in Q. faginea woodlands, as well as Hysterangium cistophilum (Tul. & C.Tul.) Zeller & Dodge, H. clathroides Vittad. and Melanogaster variegatus (Velen.) Tul., both collected in Q. suber siliceous woodlands. This fact shows that hypogean species are specialized in developing in relatively mesic areas with basic pH. (iii) Species that belong to the genera Cortinarius, Hebeloma, and Inocybe have a clear affinity to sclerophyllous forests as opposed to marcescent (Ia = 0.97 vs. 0.31; 1 vs. 57%; 0.94 vs. 0.47). Taxa belonging to Cortinarius and Inocybe are less frequent in siliceous woodlands (Ia = 0.92 vs. 0.61; 0.86 vs., 0.71), whereas Hebeloma appears equally in both types (siliceous and calcareous). Taxa of Amanita, Hygrophorus, and Tricholoma are significantly more frequent in sclerophyllous (Ia = 1) than the marcescent woodlands (Ia = 0.26–0.53). Nevertheless, Laccaria (Ia = 0.88 vs. 0.75), appears in both types due to the high ability of the species to form mycorrhizas in Quercus species (e.g. Tateishi et al 2003, Roy et al. 2008). On the other hand, Hygrophorus species are indifferent to basic pH (Ia = 0.79–0.93), Amanita appears equally in both types (Ia = 0.84 vs. 0.82), while Tricholoma (Ia = 0.75 vs. 0.83) and Laccaria (Ia = 0.88 vs. 1) prefer siliceous soils. (iv) The genera Boletus, and Xerocomus grow equally in all the woodland types studied. Leccinum shows a different behaviour, preferring marcescent and acidic woodland types. The genera Aureoboletus and Gyroporus, represented by only one species each, have a broad ecological range. Chalciporus and Paxillus, despite that data on fruit bodies in marcescent Quercus are not available, numerous records are available on other deciduous forest types. Gasteroid forms such as Pisolithus and Scleroderma form mycorrhizas with a broad range of tree and shrubs species (Calonge 1998), and therefore their presence in Quercus woodland types is not rare, even though Scleroderma appears to have more affinity to sclerophyllous woodlands. The case of S. areolatum is noteworthy, due to its specific ecological requirements, and therefore is reported only in the Q. ilex subsp. ilex woodlands in 5 Table 2. Number of species per genus and degree of representativeness (i.e. n° of species per genera/Total n° of species in the forest type) in forest types studied. (Qball = Quercus ilex subsp. ballota, Qil = Q. ilex subsp. ilex, Qsub = Q. suber, Qpyr = Q. pyrenaica, Qfag = Q. faginea, Qcoc = Q. coccifera, Qcan = Q. canariensis). 1Qscl = sclerophyllous Quercus spp. (Q. suber, Q. ilex subsp. ballota, Q. ilex subsp. ilex and Q. coccifera). 2Qmar = marcencent Quercus spp. (Q. canariensis, Q. faginea, Q. pyrenaica). 3Qind = Indifferent/basiphilous Quercus spp. (Q. coccifera, Q. ilex subsp. ballota, Q. ilex subsp. ilex and Q. faginea). 4Qsil = silicicolous Quercus spp. (Q. canariensis, Q. pyrenaica, Q. suber). Qball % Qil % Qsub % Qpyr % 6 Albatrellus 0 0.00 0 0.00 1 0.24 0 0.00 Amanita 43 10.34 15 5.21 42 10.22 15 8.77 Aureoboletus 1 0.24 1 0.35 1 0.24 1 0.58 Boletopsis 1 0.24 0 0.00 1 0.24 1 0.58 Boletus 25 6.01 15 5.21 22 5.35 11 6.43 Cantharellus 5 1.20 4 1.39 7 1.70 4 2.34 Chalciporus 1 0.24 0 0.00 1 0.24 0 0.00 Clavariadelphus 2 0.48 1 0.35 2 0.49 0 0.00 Cortinarius 94 22.60 97 33.68 86 20.92 29 16.96 Craterellus 1 0.24 1 0.35 1 0.24 1 0.58 Gauteria 1 0.24 0 0.00 0 0.00 0 0.00 Gymnomyces 4 0.96 0 0.00 0 0.00 0 0.00 Gyroporus 1 0.24 1 0.35 1 0.24 0 0.00 Hebeloma 12 2.88 4 1.39 11 2.68 6 3.51 Hydnellum 3 0.72 1 0.35 3 0.73 1 0.58 Hydnum 3 0.72 3 1.04 2 0.49 2 1.17 Hygrophorus 13 3.13 11 3.82 10 2.43 4 2.34 Hymenogaster 12 2.88 1 0.35 0 0.00 0 0.00 Hysterangium 4 0.96 0 0.00 2 0.49 0 0.00 Inocybe 44 10.58 32 11.11 42 10.22 19 11.11 Laccaria 7 1.68 2 0.69 7 1.70 6 3.51 Lactarius 22 5.29 21 7.29 27 6.57 15 8.77 Leccinum 2 0.48 2 0.69 2 0.49 2 1.17 Leucocortinarius 0 0.00 0 0.00 0 0.00 1 0.58 Melanogaster 5 1.20 0 0.00 1 0.24 1 0.58 Paxillus 1 0.24 1 0.35 1 0.24 0 0.00 Phellodon 0 0.00 1 0.35 0 0.00 0 0.00 Pisolithus 1 0.24 0 0.00 1 0.24 1 0.58 Pseudocraterellus 0 0.00 1 0.35 0 0.00 0 0.00 Qfag % 0 0.00 17 9.77 1 0.57 0 0.00 17 9.77 1 0.57 0 0.00 2 1.15 30 17.24 1 0.57 0 0.00 0 0.00 0 0.00 8 4.60 1 0.57 1 0.57 4 2.30 1 0.57 1 0.57 18 10.34 5 2.87 17 9.77 2 1.15 0 0.00 0 0.00 0 0.00 0 0.00 0 0.00 0 0.00 Qcoc 0 4 0 0 0 1 0 0 2 0 0 0 0 0 0 1 0 0 1 2 1 4 0 0 0 0 0 1 0 % Qcan % Qscle1 % 0.00 0 0.00 1 0.17 19.05 11 10.28 51 8.85 0.00 1 0.93 1 0.17 0.00 0 0.00 1 0.17 0.00 6 5.61 25 4.34 4.76 1 0.93 8 1.39 0.00 0 0.00 1 0.17 0.00 2 1.87 2 0.35 9.52 11 10.28 149 25.87 0.00 0 0.00 1 0.17 0.00 0 0.00 1 0.17 0.00 0 0.00 4 0.69 0.00 1 0.93 1 0.17 0.00 4 3.74 14 2.43 0.00 1 0.93 3 0.52 4.76 1 0.93 3 0.52 0.00 3 2.80 14 2.43 0.00 0 0.00 12 2.08 4.76 0 0.00 4 0.69 9.52 6 5.61 62 10.76 4.76 2 1.87 7 1.22 19.05 9 8.41 33 5.73 0.00 1 0.93 2 0.35 0.00 0 0.00 0 0.00 0.00 0 0.00 5 0.87 0.00 0 0.00 1 0.17 0.00 0 0.00 1 0.17 4.76 0 0.00 1 0.17 0.00 0 0.00 1 0.17 Qmar2 % Qind3 % Qsil4 % 0 0.00 0 0.00 1 0.22 26 8.84 43 8.37 42 9.38 1 0.34 1 0.19 1 0.22 1 0.34 1 0.19 1 0.22 23 7.82 27 5.25 25 5.58 4 1.36 7 1.36 7 1.56 0 0.00 1 0.19 1 0.22 2 0.68 2 0.39 2 0.45 48 16.33 140 27.24 93 20.76 1 0.34 1 0.19 1 0.22 0 0.00 1 0.19 0 0.00 0 0.00 4 0.78 4 0.89 1 0.34 1 0.19 1 0.22 8 2.72 12 2.33 12 2.68 3 1.02 3 0.58 3 0.67 2 0.68 3 0.58 2 0.45 7 2.38 14 2.72 10 2.23 1 0.34 12 2.33 0 0.00 1 0.34 4 0.78 2 0.45 31 10.54 57 11.09 47 10.49 6 2.04 7 1.36 8 1.79 24 8.16 30 5.84 30 6.70 3 1.02 2 0.39 3 0.67 1 0.34 0 0.00 1 0.22 0 0.00 5 0.97 1 0.22 0 0.00 1 0.19 1 0.22 0 0.00 1 0.19 0 0.00 1 0.34 1 0.19 1 0.22 0 0.00 1 0.19 0 0.00 Table 2 continued. Qball % Qil Ramaria Russula Sarcodon Scleroderma Telephora Tricholoma Wakefieldia Xerocomus Zelleromyces 5 1.20 6 54 12.98 37 3 0.72 2 5 1.20 3 3 0.72 0 24 5.77 18 1 0.24 1 12 2.88 6 1 0.24 0 Total species 416 288 % Qsub % 2.08 12.85 0.69 1.04 0.00 6.25 0.35 2.08 0.00 14 70 5 4 2 29 0 13 0 411 Qpyr % Qfag 3.41 3 1.75 6 17.03 29 16.96 12 1.22 2 1.17 1 0.97 3 1.75 1 0.49 0 0.00 2 7.06 10 5.85 16 0.00 0 0.00 0 3.16 4 2.34 9 0.00 0 0.00 0 171 174 % Qcan % Qscle1 % % Qcoc 3.45 6.90 0.57 0.57 1.15 9.20 0.00 5.17 0.00 0 4 0 0 0 0 0 0 0 0.00 9 8.41 19.05 18 16.82 0.00 0 0.00 0.00 3 2.80 0.00 0 0.00 0.00 10 9.35 0.00 0 0.00 0.00 7 6.54 0.00 0 0.00 21 107 Qmar2 % Qind3 % Qsil4 % 17 2.95 81 14.06 6 1.04 6 1.04 3 0.52 36 6.25 1 0.17 16 2.78 1 0.17 13 4.42 10 1.95 15 3.35 44 14.97 65 12.65 78 17.41 3 1.02 4 0.78 5 1.12 4 1.36 6 1.17 5 1.12 2 0.68 4 0.78 2 0.45 19 6.46 27 5.25 30 6.70 0 0.00 1 0.19 0 0.00 14 4.76 14 2.72 13 2.90 0 0.00 1 0.19 0 0.00 576 294 514 448 7 Italy (Laganá et al. 2002). (v) Taxa belonging to Telephorales (Boletopsis, Hydnellum, Phellodon, Sarcodon, and Telephora) have a broad distribution, because at least 50% of the species are present in marcescent and sclerophyllous types, as well as any soil type. Nevertheless, this group appears to be an efficient symbiont of Quercus s.l (Calonge 1998). The exception are taxa belonging to genus Phellodon, which grow only on Q. ilex subsp. ilex calcareous woodlands in the northern Iberian Peninsula (Basque country). (vi) Cantharellus and Hydnum have a similar behaviour since they clearly prefer sclerophyllous types; nevertheless, with respect to soil type, Hydnum species are more frequent in Q. ilex sensu lato woodlands (basophilous or indifferent to the pH of the soil) against Q. suber (siliceous soils) (Ia = 1 vs. 0.67), while Cantharellus grows in both soil types (calcareous and siliceous) although it is found more frequently in cork-oak woodlands (Ia = 0.88 vs. 0.64). The genera Craterellus and Pseudocraterellus are represented by only one species. The former grows in any woodland type, while the second one only on Q. ilex subsp. ilex (Laganá et al. 2000). (vii) Club fungi (Clavariadelphus) and coral fungi (Ramaria) appear in any Quercus forest, though Ramaria species prefer a high level of oceanicity and siliceous substrates, such as cork-oak forests, where 79% of the species here compiled occur. Some species are typical of Mediterranean environments (e.g. Ramaria mediterranea Schild & Franchi). (viii) Lactarius and Russula have a different ecological profile, even though the former fructifies indifferently on either calcareous or siliceous substrates, and more frequently in sclerophyllous woodlands (Ia = 0.89 vs. 0.65), while Russula taxa have a high level of affinity to these sclerophyllous forests (Ia = 0.91 vs. 0.49), and relatively more affinity to siliceous substrates (Ia = 0.89 vs. 0.78). For this reason, they are highly represented in Q. suber woodlands (70%). Mycorrhizal mycobiota of sclerophyllous vs. deciduous Quercus forests Diversity of mycorrhizal macrofungi of sclerophyllous woodlands (576 taxa, 95.2%) is higher than the marcescent types (294 taxa, 48.6%). On the one hand, sclerophyllous forests have a larger occupation and potential area in the Mediterranean biome of the Iberian Peninsula, in comparison to temperate one and for this reason there are more works regarding sclerophyllous woodland types, even though the sampling effort is similar in both types, given the lower area of the marcescent types. Physiognomic aspects of mycobiota in a given plant community can be expressed depending on the proportionality index (Ip) of each genus that occurs in the mycobiota. With respect to the most diverse genera (in terms of species richness), we can point out the following features: Cortinarius is more represented in sclerophyllous woodlands (Ip = 0.26 vs. 0.16), since Q. ilex subsp. ilex (Ip = 0.34), Q. ilex subsp. ballota and Q. suber (Ip > 0.20) woodlands are quite rich in species belonging to these genera in comparison with marcescent types. Boletus (Ip = 0.43 vs. 0.78), Lactarius (0.57 vs. 0.82), Ramaria (Ip = 0.3 vs. 0.44) and Xerocomus (Ip = 0.28 vs. 0.47) present the opposite, since, despite the number of species being similar in both types, the Ip index is higher in marcescent. The degree of heterogeneity (Ih) of mycorrhizal mycobiota is Ih = 0.51, in sclerophyllous as opposed to Ih = 0.65 in marcescent woodlands. Therefore, Q. canariensis, 8 Q. faginea, and Q. pyrenaica woodlands have a higher degree of heterogeneity, due to a higher diversity of ecological niches occupied by marcescent Quercus, while Q. coccifera, Q. ilex s.l., and Q. suber are more ecologically homogeneous (Sánchez de Dios et al. 2009), and more suitable for the development of Mediterranean mycorrhizal Agaricomycetes. The degree of similarity (in terms of Jaccard‘s similarity index = Ij) is an important feature. The value of the index (Ij = 0.438), shows differences between the mycobiota of marcescent and sclerophyllous forests. Nevertheless, we should take into account that the number of collected species in each type is very different (576 vs. 294), causing a low Ij value. Mycobiota of siliceous vs. indifferent-basophilous Quercus forests The entire number of species reported in siliceous woodland types (448 taxa, 74.05%) is lower than the basophilous (514, 84.96%). The Proportionality index is very similar in Cortinarius (Ip = 0.21 vs. 0.27) and higher in siliceous woodlands for Russula (Ip = 0.17 vs. 0.13), due to the the high richness in these forest types (Q. suber: 70 taxa, 17.03% and Q. pyrenaica: 29 taxa, 16.96%). The degree of heterogeneity is higher (Ih = 0.65) in woodlands dominated by species preferring siliceous soils than in woodlands where key species are indifferent in any preference of soil types. (Ih = 0.57). The explanation is the higher ecological heterogeneity within this second type (i.e. between Q. canariensis-Q. suber or -Q. pyrenaica; see Table 1) (Sánchez de Dios et al. 2009). The similarity index (between siliceous and indifferent-basophilous; Ij = 0.577) has an important analytic value, since a high number of species have been collected in both types (448 siliceous vs. 524 indifferent-basophilous). The most significant differences refer to the genus Cortinarius (140 species vs. 93 species), Hygrophorus (14 vs. 10), Hymenogaster (12 vs. 0) or Inocybe (57 vs. 47). Hence, the majority of the taxa belonging these genera fructify on Q. ilex s.l., because they are basophilous or indifferent with respect to the substrate, contrary the genera Ramaria (10 vs. 15) or Russula (65 vs. 78) are more frequent over Q. suber, therefore they are silicicolous (Ortega & Lorite 2007, Moreno et al. 2004) Comparative study of different types of Quercus forests DCA establishes a preliminary separation between the mycobiota of sclerophyllous and marcescent woodlands (Fig. 1) in the first axis (44,8% of the variance), while siliceous and indifferent-basophilous showed less distance. Consequently the results show that the factor related with leaf character (related with the more or less mesophilous character) is the main explanatory feature. We also point out the considerable distance between Quercus ilex subsp. ballota and Quercus ilex subsp. ilex, despite they are closely taxonomically related taxa. To show the diversity of each woodland type, we note the degree of mycological diversity, based in the Margalef taxonomic-diversity index (Itd), as well as the number of species and genera specific of each woodland type compared with the total number 9 Fig. 1. Biplot showing the DCA ordination of the Quercus forests studied here, based on the presence-absence data of the micorrhizal taxa. Qrot = Quercus rotundifolia(= Q. ilex subsp. ballota), Qil = Q. ilex subsp. ilex, Qsub = Q. suber, Qpyr = Q. pyrenaica, Qfag = Q. faginea, Qcan = Q. canariensis). Qsclero = sclerophyllous Quercus spp. (Q. suber, Q. ilex subsp. ballota, Q. ilex subsp. ilex). Qmarces = marcencent Quercus spp. (Q. canariensis, Q. faginea, Q. pyrenaica). Qind = Indiferent/basiphilous Quercus spp. (Q. ilex subsp. ballota, Q. ilex subsp. ilex and Q. faginea). Qsil = silicicolous Quercus spp. (Q. canariensis, Q. pyrenaica, Q. suber).(see table 1 for further information on the taxa). (all the Quercus woodland types together). The data gathered in the Table 3 reflect that the taxonomic diversity of the Quercus woodlands analysed here is Itd = 5.63. This is close to the value of the sclerophyllous (Itd = 5.67) and siliceous woodlands (Itd = 5.61). Since this index is strongly influenced by the number of genera and species in each woodland type, and three different woodland types have different sampling effort, we corrected the index by calculating and comparing the index with the value of the index for all the Quercus woodlands studied here (Table 3). The most remarkable results are: (i) sclerophyllous (Itd/Itdt) = 1.01), siliceous (Itd/Itd = 1) and holm-oak woodlands (Q. ilex subsp. ballota) (Itd/Itdt = 1.03) are the most diverse, especially in woodlands over siliceous substrates, since these woodland types have a lower number of species than the woodlands over calcareous substrates. (ii) The Q. ilex subsp. ilex woodlands present a relative high diversity (Itd = 4.74), comparable with other woodland types with a higher number of species (e.g. Q. suber). One explanation is the importance of some genera, especially rich, such as Cortinarius in these types. (iii) Marcescent woodlands are highly diverse, given the lower number of species reported, due to the major differences between the ecological features of the species included in this group, and the most suitable habitat for the macrofungi that they constitute. 10 Table 3. Margalef taxonomic-diversity index (Itd) for the different forest types. Itd/Itdt = quotient between the values of Margalef index for the woodland type and for the total data, respectively. Nsp/ Nspt = quotient between species in the particular woodland type/species of the all woodland types studied. Ng/Ngt = quotient between genera in the particular woodland type/genera of the all woodland types studied. Type Q. canariensis Q. coccifera Q. faginea Q. ilex subsp. ilex Q. ilex subsp. ballota Q. pyrenaica Q. suber sclerophyllous indifferent siliceous Quercus (all the types) Itd Itd/Itdt 4.07 3.29 4.26 4.74 5.47 4.47 4.82 5.67 5.08 5.61 5.63 0.72 0.58 0.76 0.84 0.97 0.79 0.86 1.01 0.90 1.00 1.00 Nsp/Nspt Ng/Ngt 0.18 0.03 0.29 0.48 0.69 0.28 0.68 0.95 0.85 0.74 1.00 0.54 0.27 0.62 0.73 0.92 0.65 0.81 1.00 0.97 0.86 1.00 Discussion The considerable number of mycorrhizal macrofungi species reported in the present work (605 taxa) highlight that Quercus woodlands of the study area have surprising richness, comparable with data recorded for Eucalyptus in natural environments of Australia (Castellano & Bougher 1994), estimated at some 660 fungal associates and believed to have the potential to associate with the richest flora of host genus-specific ectomycorrhizal fungi in the world (Molina et al. 1992). The mycobiota have a medium affinity to the Quercus species, so that, together with macrofungi specific to these woodland types, such as Amanita spp., Boletus spp., hypogeous species, and some species of Cortinarius and Hygrophorus, there is a significant number of taxa with a broad distribution (e.g. some Cortinarius species, Pisolithus arhizus, Scleroderma spp. Gyroporus castaneus, Phellodon spp.). The main factor determining the mycorrhizal mybiota is the woodland type (sclerophyllous vs. deciduous), while the pH of the soil plays a secondary role. This is reasonable, because in woodland types many underlying ecological factors determine the appearance of the mycobiota, and these results agree with the data gathered for macrofungi (both mycorrhizal and saprophytic) for the southern Spain (Ortega & Lorite 2007). According the results, sclerophyllous woodlands are taxonomically more diverse than are the marcescent ones, whereas fungi preferring siliceous soils are more diverse than than those preferring calcareous or indifferent soils (see Results section). These results also follow the trend found for the the whole of macrofungi (Ortega & Lorite 2007). From the detailed list of mycorrhizal taxa compiled here, we emphasize the presence of genera that are very well-adapted to the sclerophyllous Mediterranean woodlands, 11 such as Amanita, Boletus, Xerocomus, Hygrophorus, hypogeous species, Scleroderma, and Pisolithus (see appendix 1 to check the species of these genera). Therefore, many species are appear as suitable for inoculating plants in afforestation or recovery programs, since it is well known that they significantly improve both survival and growth (e.g. Jeffries & Barea 2001). Another aspect to highlight is the considerable number of rare species that appears in the Iberian Quercus woodlands. In this sense, many species included in the present compilation are present in regional Red List of Endangered Macromycetes (Brandrud et al. 2006, Gyosheva et al. 2006, Holec & Beran 2006, Lizon et al. 2001, Senn-Irlet et al. 2007), such as: Amanita caesarea, A. franchetii, A. ovoidea, A. verna, Boletopsis leucomelaena, Boletus fechtneri, B. regius, B. rhodopurpureus, B. rhodoxanthus, B. satanas, Cantharellus melanoxeros, Clavariadelphus pistillaris, Cortinarius bulliardi, C. caerulescens, C. cagei, C. ionochlorus, C. prasinus, C. salor, C. xanthophyllus, Gyroporus castaneus, Hydnellum concrescens, H. scrobiculatum, Hydnum albidum, Hygrophorus arbustivus, Inocybe adaequata, I. bresadolae, I. corydalina, Lactarius acerrimus, L. acris, L. evosmus, L. luridus, Phellodon niger, Ramaria aurea, R. botrytis, R. flavescens, R. flavobrunescens, Russula albonigra, R. maculata, R. roseipes, Sarcodon leucopus, S. scabrosus, Tricholoma acerbum, T. sulphurescens, T. ustaloides, Xerocomus armeniacus, and X. moravicus. 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SUÁREZ (2004): Adiciones al catálogo corológico de los Macromicetos de la provincia de Teruel. - Bol. Soc. Micol. Madrid 28: 187–196. SCHWARTZ, O. (1964): Quercus. - In: TUTIN, T.G., V.H. HEYWOOD, N.A. BURGES, D.H. VALENTINE, S.M. WALTERS & D.A. WEBB (eds.): Flora Europaea, vol. I: 61–64. - Cambridge University Press, Cambridge. TATEISHI, T., K. YOKOYAMA, N. KOHNO, H. OKABE & T. MARUMOTO (2003): Estimation of mycorrhizal colonization of the roots of oak seedlings inoculated with an ectomycorrhizal fungus, Laccaria amethystea. - Soil Sci. Plant Nutr. 49(4): 641–645. TEJEDOR, F. & M.T. BASSO (2003): El género Lactarius Pers., en la Comunidad Valenciana. I. - Butl. Soc. Micol. Valenciana 8: 103–152. TEJEDOR, F. & R. MAHIQUES (2001): Estudio sobre Cortinarius de Castelló (III). - Butl. Soc. Micol. Valenciana 6: 71–86. TEJEDOR, F. & R. MAHIQUES (2003): Amanitas de la Comunidad Valenciana. (II). - Butl. Soc. Micol. Valenciana 8: 153–172. TEJEDOR, F., A. CONCA & R. 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(2003): Datos Botánicos aplicados a la gestión del medio natural Andaluz III: Modelos de gestión. - Junta de Andalucía, Consejería de Medio Ambiente, Sevilla. WANG, B. & Y.L. QIU (2006): Phylogenetic distribution and evolution of mycorrhizas in land plants. - Mycorrhiza 16: 299–363. Received 27 February 2009, accepted in revised form 6 November 2009. 17 Appendix 1. Presence/absence matrix of the compiled taxa by Quercus forest types. (Qball = Quercus ilex subsp. ballota, Qil = Q. ilex subsp. ilex, Qsub = Q. suber, Qpyr = Q. pyrenaica, Qfag = Q. faginea, Qcoc = Q. coccifera, Qcan = Q. canariensis). Qball Albatrellus subrubescens (Murrill) Pouzar Amanita baccata (Fr.) Gillet Amanita battarrae (Boud.) Bon Amanita beillei (Beauseign.) Bon & Contu Amanita caesarea (Scop.) Fr. Amanita citrina var. citrina (Schaeff.) Pers. Amanita citrina var. alba (Gillet) E.-J.Gilbert Amanita codinae (Maire) Bertault Amanita crocea (Quél.) Singer 1 Amanita curtipes E.-J.Gilbert Amanita decipiens (Trimbach) Jacquet. Amanita echinocephala (Vittad.) Quél. Amanita eliae Quél. Amanita franchetii (Boud.) Fayod Amanita fulva (Schaeff.) Fr. Amanita gemmata (Fr.) Bertill. Amanita gemmata fo. amici (Gillet) E.-J.Gilbert Amanita gilbertii Beauseign. Amanita gracilior Bas & Honrubia Amanita lactea Malençon, Romagn. & D.A.Reid Amanita lepiotoides Barla Amanita lividopallescens (Secr. ex Boud.) . Kühner & Romagn Amanita magnivolvata Aalto Amanita mairei Foley Amanita malleata (Piane ex Bon) Contu Amanita muscaria (L.) Lam. Amanita ovoidea (Bull.) Link Amanita ovoidea var. proxima (Dumée) Bon & Courtec. Amanita pachyvolvata (Bon) Krieglst. Amanita pantherina (DC.) Krombh. Amanita phalloides (Vaill.) Link Amanita asteropus Sabo Amanita ponderosa Malençon & R. Heim Amanita porphyria Alb. & Schwein. Amanita oblongospora Contu Amanita rubescens Pers. Amanita separata Contu Amanita singeri Bas Amanita spissa (Fr.) P.Kumm. Amanita spissa var. excelsa (Fr.) Dörfelt & I.I.Roth Amanita spissa var. valida (Fr.) E.-J.Gilbert Amanita spreta (Peck) Sacc. 2 Amanita strangulata (Fr.) Quél. Amanita strobiliformis (Paulet ex Vittard.) Bertill. Amanita submembranacea var. griseoargentea Contu Qil Qsub Qpyr Qfag Qcoc Qcan 0 1 1 1 1 1 0 1 1 1 1 1 1 1 0 1 1 0 0 1 0 1 1 0 0 1 0 0 0 0 0 0 1 0 1 1 1 0 1 1 1 1 1 1 1 0 1 1 1 1 1 0 1 0 0 1 1 0 0 0 0 0 0 0 1 1 1 0 0 0 1 0 1 1 0 0 1 0 0 1 0 1 0 1 0 0 1 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 1 0 0 0 0 1 0 0 0 1 1 1 0 0 0 1 1 1 0 0 0 0 1 0 0 0 1 0 0 0 1 1 0 0 0 1 0 0 0 1 0 0 0 0 0 1 1 1 1 1 0 0 1 0 1 0 1 1 1 1 0 1 0 0 0 1 0 0 0 1 1 1 1 0 0 1 0 0 0 0 0 0 1 0 0 0 1 1 1 1 1 1 1 1 1 1 0 1 1 1 1 0 0 0 0 1 0 0 0 1 1 1 1 1 1 0 0 1 0 1 1 1 0 1 1 0 0 0 0 1 0 0 1 1 0 1 1 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 0 0 1 0 0 0 1 1 0 0 0 0 1 0 1 1 1 1 1 0 0 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 1 0 0 18 Amanita supravolvata Lanne 3 Amanita umbrinolutea (Secr. ex Gillet) Bertill Amanita vaginata (Bull.) Lam. Amanita vaginata var. alba Gillet 4 Amanita valens (E.-J.Gilbert) Bertault Amanita verna (Bull.) Lam. Amanita vittadini (Moretti) Sacc. Aureoboletus gentilis (Quél.) Pouzar Boletopsis leucomelaena Pers. Boletus aereus Bull. 5 Boletus aestivalis (Paulet) Fr. Boletus apendiculatus Schaeff. Boletus calopus Pers. Boletus edulis Bull. Boletus erythropus Pers. Boletus fetchneri Velen. Boletus fragrans Vittad. Boletus impolitus Fr. Boletus legaliae Pilát Boletus lupinus Fr. Boletus luridus Schaeff. Boletus luteocupreus Bertéa & Estadés Boletus piperatus Bull. Boletus permagnificus Pöder Boletus pseudoregius (Heinr. Hubert) Estades Boletus pulchrotinctus Alessio Boletus pulverulentus Opat. Boletus queletii Schulzer 6 Boletus queletii var. lateritius (Bres. & Schulz.) E.-J.Gilbert Boletus radicans Pers. Boletus regius Krombh. Boletus rhodopurpureus Smotl. Boletus rhodoxanthus (Krombh.) Kallenb. Boletus satanas Lenz Boletus spretus Bertéa Boletus venturii Bon Cantharellus cibarius Pers. Cantharellus cibarius var. alborufescens Malençon Cantharellus cinereus Fr. 7 Cantharellus ferruginascens P.D.Orton Cantharellus lutescens Fr. Cantharellus melanoxeros Desm. Cantharellus subpruinosus Eyssart. & Buyk Cantharellus tubaeformis Fr. Chalciporus piperatus (Bull.) Bataille Clavariadelphus flavoinmaturus R.H.Petersen Clavariadelphus pistillaris (L.) Donk Cortinarius albidodiscus Bidaud & Fillion Cortinarius acetosus (Velen.) Melot Cortinarius acutus (Pers.) Fr. Cortinarius alboviolaceus (Pers.) Fr. 8 Cortinarius alcalinophilus Rob.Henry Cortinarius aleuriosmus Maire Cortinarius ammoniacosplendens Chevassut & Rob.Henry 1 1 1 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 0 1 1 1 1 1 0 0 0 1 0 0 1 0 1 0 1 0 1 1 1 1 1 0 0 0 1 1 0 0 0 0 1 1 1 0 0 1 1 1 1 0 1 1 1 1 1 1 0 1 1 0 1 1 1 1 1 0 0 1 1 0 1 1 1 0 1 0 0 1 0 0 1 1 1 1 1 0 0 1 0 0 0 0 0 1 0 1 1 0 0 1 0 1 0 0 0 0 0 0 0 1 0 1 1 1 1 1 1 0 0 1 0 1 1 1 0 0 1 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 1 0 0 0 0 0 1 0 0 1 0 0 0 1 0 0 0 0 0 1 1 0 1 1 1 1 1 1 1 1 1 1 1 0 1 1 0 0 1 0 1 1 0 1 1 1 1 1 1 0 0 1 0 0 0 0 1 0 1 1 1 1 1 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 0 0 1 1 1 1 1 0 0 0 1 1 1 1 1 0 1 0 0 1 0 1 0 1 1 1 0 1 1 0 1 0 1 1 1 1 1 1 1 0 0 0 0 1 1 0 0 0 1 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 0 1 1 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 0 0 0 1 0 0 19 Qball Qil 0 0 1 0 0 1 0 1 0 1 1 1 1 1 1 0 1 0 1 Cortinarius amoenolens Rob.Henry & P.D.Orton Cortinarius anfractoides Rob. Henry & Trescol Cortinarius anomalus (Fr.) Fr. 9 Cortinarius anserinus (Velen.) Rob. Henry Cortinarius aprinus Melot Cortinarius assiduus Mahiques, A.Ortega & Bidaud 10 Cortinarius atrovirens Kalchbr. 11 Cortinarius aurilicis Chevassut & Rob.Henry Cortinarius aurantioturbinatus J.E.Lange Cortinarius balteatocumatilis Rob.Henry ex P.D.Orton Cortinarius balteatocumatilis var. laetus (M.M.Moser) Quadr. 12 Cortinarius boudieri Rob.Henry Cortinarius bovinus Fr. 13 Cortinarius brunneus Pers. sensu J.E.Lange Cortinarius bulliardi (Pers.) Fr. Cortinarius caerulescens (Schaeff.) Fr. 14 Cortinarius coerulescentium Rob.Henry Cortinarius caesiocortinatus subsp. bulbolatens (Chevassut & Rob. Henry) Melot Cortinarius caesiostramineus Rob.Henry Cortinarius caesiostramineus var. gentianeus (Bidaud) A.Ortega & Mahiques Corinarius cagei Melot Cortinarius caligatus Malençon Cortinarius calochrous (Pers.) Gray sensu lato Cortinarius candelaris Fr. Cortinarius caninus (Fr.) Fr. Cortinarius caperatus (Pers.) Fr. 15 Cortinarius caroviolaceus P.D.Orton Cortinarius catharinae Cons. Cortinarius causticus Fr. Cortinarius cedretorum Maire Cortinarius cephalixus Secr. ex Fr. Cortinarius chevassutii Rob.Henry Cortinarius cinnabarinus Fr. Cortinarius cinnamomeus (L.) Fr. Cortinarius cistoadelphus (G.Moreno & al.) G.Moreno Cortinarius claroflavus Rob.Henry Cortinarius claricolor (Fr.) Fr. Cortinarius colus Fr. Cortinarius cotoneus Fr. Cortinarius croceocoeruleus (Pers.) Fr. Cortinarius croceus (Schaeff.) Gray Cortinarius crystalinus Fr. Cortinarius cumatilis Fr. Cortinarius damascenus Fr. Cortinarius decipiens (Pers.) Fr. 16 Cortinarius decipiens var. subturibulosus (Kizlik & Trescol) A.Ortega & Mahiques Qcoc Qcan 0 0 0 0 0 0 0 1 0 1 0 1 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 0 1 0 0 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 1 0 1 1 1 1 0 0 1 1 1 1 0 1 1 0 1 1 0 0 0 0 0 0 1 0 0 1 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 0 1 1 0 1 0 0 1 0 1 0 1 0 1 1 1 1 1 1 0 0 1 1 1 1 0 1 0 1 0 1 1 1 0 1 0 0 0 1 1 1 0 0 1 1 1 1 0 0 0 1 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 1 1 1 0 0 1 1 1 0 0 0 1 1 0 1 1 0 1 0 0 0 1 1 1 1 0 1 1 1 0 0 0 0 0 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 20 Qsub Qpyr Qfag Cortinarius delaportei Rob.Henry Cortinarius delibutus Fr. Cortinarius depallens (M.M.Moser) Bidaud, Moënne-Locc. & Reumaux Cortinarius diabolicoides Moënne-Locc. & Reumaux Cortinarius diabolicus (Fr.) Fr. Cortinarius dibaphus Fr. Cortinarius dionysae Rob.Henry Cortinarius diosmus Kühner Cortinarius diosmus var. araneosovolvatus Bon & Gaugé 17 Cortinarius duracinus Fr. 18 Cortinarius elegantior var. quercus-ilicis Chevassut & Rob.Henry Cortinarius elegantissimus Rob.Henry Cortinarius emollitus Fr. Cortinarius eufulmineus Rob.Henry Cortinarius evernius (Fr.) Fr. Cortinarius flavescentium Rob.Henry Cortinarius flexipes (Fr.) Fr. Cortinarius conico-obtusarum A.Ortega & Chevassut Cortinarius fulgens sensu Lange Cortinarius fulmineus (Fr.) Fr. Cortinarius glandicolor (Fr.) Fr. Cortinarius glaucopus (Schaeff.) Fr. Cortinarius hillieri Rob.Henry Cortinarius hinnuleus Fr. Cortinarius humolens Brandrud Cortinarius infractemmatus Chevassut & Rob.Henry Cortinarius infractus (Berk.) Fr. Cortinarius ionochlorus Maire Cortinarius joguetii Melot Cortinarius lebretoni Quél. Cortinarius lividoochraceus (Berk.) Berk. Cortinarius maculosus (Pers.) Fr. Cortinarius majusculus Kühner Cortinarius maxistriatulus Rob.Henry Cortinarius melanotus Kalchbr. Cortinarius moënne-loccozii Bidaud Cortinarius mucifluus Fr. Cortinarius mucosus (Bull.) Cooke Cortinarius nanceiensis Maire Cortinarius nanceiensis var. bulbopodius Chevassut & Rob.Henry Cortinarius nemorensis (Fr.) J.E.Lange Cortinarius obtusus (Fr.) Fr. Cortinarius olearioides Rob.Henry Cortinarius olidivolvatus Bon & Trescol Cortinarius olidus J.E.Lange Cortinarius olivascentium Rob.Henry Cortinarius olivellus Rob.Henry 19 Cortinarius orellanoides Rob.Henry Cortinarius orellanus Fr. Cortinarius orichalceus (Batsch) Fr. 0 1 0 1 1 1 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 0 1 1 1 1 1 0 1 1 1 1 1 0 1 1 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 1 0 0 1 0 0 1 0 1 1 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 0 1 1 1 1 1 1 1 1 1 0 0 0 1 0 1 0 1 1 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 1 1 0 0 1 0 1 1 1 0 0 1 1 1 0 1 1 1 0 1 1 0 1 1 1 1 0 0 0 1 0 0 1 0 0 1 0 0 0 1 1 0 0 1 0 0 0 0 0 0 0 0 0 1 1 0 0 1 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 0 0 0 0 0 0 0 0 0 1 1 1 0 0 0 0 0 0 1 1 1 0 1 1 1 1 1 0 0 1 1 1 1 1 1 0 0 1 1 1 0 0 0 1 0 0 0 0 0 0 0 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 21 Qball Cortinarius pachypus M.M.Moser Cortinarius parafulmineus Rob.Henry Cortinarius parasuaveolens (Bon & Trescol) Bidaud, Moënne-Locc. & Reumaux Cortinarius petroselineus Chevassut & Rob.Henry Cortinarius porphyropus (Alb. & Schwein.) Fr. Cortinarius prasinus (Schaeff.) Fr. Cortinarius purpurascens Fr. Cortinarius rigens (Pers.) Fr. Cortinarius roberti-henrici Contu Cortinarius rubicundulus (Rea) A.Pearson Cortinarius rubricosus (Fr.) Fr. Cortinarius rufoolivaceus (Pers.) Fr. Cortinarius rugosus Rob.Henry Cortinarius safranopes Rob.Henry Cortinarius salor Fr. Cortinarius saporatus Britzelm. Cortinarius scobinaceus Malençon & Bertault Cortinarius sciophyllus Fr. Cortinarius sertipes Kühner sensu A.Ortega & Mahiques Cortinarius sodagnitus Rob.Henry sensu lato Cortinarius sordescens Rob.Henry Cortinarius splendens var. meinhardii (Bon) Melot Cortinarius splendens var. splendens Rob.Henry Cortinarius splendificus Chevassut & Rob. Henry Cortinarius stillatitius Fr. Cortinarius strenuipes var. subacuminatus Rob.Henry ex Reumaux Cortinarius strenuisposus Bidaud, Cors. Gut. & Vila Cortinarius suaveolens Bataille & Joachim Cortinarius subferrugineus (Batsch) Fr. Cortinarius suillus Fr. Cortinarius sulphurinus Quél. Cortinarius talus Fr. Cortinarius terpsichores var. calosporus Melot Cortinarius terpsichores var. meridionalis (Bidaud, Moënne-Locc. & Reumaux) A.Ortega Cortinarius terpsichores var. terpsichores Melot Cortinarius tomentosus Rob.Henry Cortinarius torvus (Fr.) Fr. Cortinarius trivialis J.E.Lange Cortinarius turbinatorum Cor. Gut. & Vila Cortinarius turgidus Fr. Cortinarius umbrinoclarus Rob.Henry Cortinarius umbrinolens P.D.Orton Cortinarius uraceus Fr. Cortinarius variiformis Malençon 20 Cortinarius varius (Schaeff.) Fr. Cortinarius veneris Bidaud, Moënne-Locc. & Reumaux Cortinarius venetus (Fr.) Fr. Qil Qsub Qpyr Qfag Qcoc Qcan 1 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 0 0 0 1 1 1 1 0 0 0 1 0 0 1 1 1 1 1 0 0 1 1 0 1 0 1 1 1 1 0 0 0 0 1 0 1 1 1 0 1 1 1 0 1 1 1 0 1 0 0 0 1 0 0 0 1 0 0 0 1 1 0 0 0 0 1 0 0 0 0 1 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 0 1 0 0 0 0 0 0 0 1 0 1 0 1 0 0 0 1 1 0 0 1 0 0 0 0 0 0 0 0 1 0 1 0 1 1 0 0 1 0 1 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 0 1 0 1 0 1 1 1 1 0 0 0 0 1 1 0 0 1 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 1 1 1 0 1 1 1 1 0 0 1 1 1 1 0 1 1 1 1 0 0 0 0 1 1 0 0 1 1 0 1 1 0 1 0 0 1 0 0 0 0 1 0 1 0 0 0 1 1 0 0 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 0 0 1 0 0 0 0 1 1 1 0 1 1 0 22 Cortinarius veraprilis Chevassut, Rob.Henry & G.Riousset Cortinarius viridocaeruleus Chevassut & Rob.Henry Cortinarius xanthophyllus (Cooke) Rob.Henry Craterellus cornucopioides (L.) Pers. Gauteria morchelliformis Vittad. Gymnomyces dominguezii Mor.-Arr., J.Gómez & Calonge Gynomyces ferruginascens Singer & A.H.Sm. Gynomyces sublevisporus Mor.-Arr., Llistos & L.Romero Gymnomyces xanthosporus (Hawker) A.H.Smith Gyroporus castaneus (Bull.) Quél. Hebeloma album Peck Hebeloma anthracophilum Maire Hebeloma crustuliniforme (Bull.) Quél. 21 Hebeloma eburneum Malençon Hebeloma edurum Métrod ex Bon Hebeloma hiemale Bres. Hebeloma leucosarx P.D.Orton Hebeloma mesophaeum (Pers.) Quél. Hebeloma radicosum (Bull.) Ricken Hebeloma sacchariolens var. pallidoluctuosum (Gröger & Zschiesch.) Quadr. Hebeloma sarcophyllum (Peck) Sacc. Hebeloma sinapizans (Fr.) Sacc. Hebeloma sordescens Vesterh. Hebeloma sordidum Maire Hydnellum concrescens (Pers.) Banker Hydnellum ferrugineum (Fr.) P.Karst. Hydnellum scrobiculatum (Fr.) P.Karst. Hydnum albidum Peck Hydnum repandum L. Hydnum rufescens Pers. Hygrophorus arbustivus Fr. Hygrophorus chrysodon (Batsch) Fr. 22 Hygrophorus cossus (Sowerby) Fr. Hygrophorus discoxanthus Rea Hygrophorus eburneus (Bull.) Fr. Hygrophorus leucophaeo-ilicis Bon & Chevassut Hygrophorus lindtneri M.M.Moser Hygrophorus melizeus Fr. Hygrophorus penarius Fr. Hygrophorus persoonii Arnolds Hygrophorus persoonii var. fuscovinosus (Bon) Bon Hygrophorus pseudodiscoideus (Maire) Malençon & Bertault Hygrophorus roseodiscoideus Bon & Chevassut Hygrophorus russula (Schaeff.) Kauffman Hymenogaster arenarius Tul. & C.Tul. Hymenogaster bulliardi Vittad. Hymenogaster citrinus Vittad. Hymenogaster decorus Tul. & C.Tul. Hymenogaster griseus Vittad. Hymenogaster luteus Vittad. 1 0 0 0 0 0 0 1 1 1 0 0 0 0 1 1 1 1 1 1 0 0 1 1 0 0 0 1 0 0 0 1 0 0 0 0 0 0 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 0 1 1 1 1 1 1 0 1 0 1 0 0 1 0 0 1 0 0 0 1 0 1 1 1 1 0 1 0 1 1 1 1 0 0 0 0 1 0 1 1 1 0 0 0 0 0 0 0 1 0 1 1 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 0 1 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 1 1 1 1 0 1 0 0 1 0 0 1 1 1 1 0 1 1 1 1 1 0 1 1 1 1 1 0 1 1 1 1 0 1 1 1 1 1 1 1 1 0 0 1 1 0 0 1 0 1 0 1 0 0 1 1 0 1 1 0 1 0 0 0 0 1 0 1 1 0 1 1 0 0 0 0 1 0 0 1 0 0 1 0 0 0 1 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 0 0 1 0 0 1 0 0 1 0 0 0 0 0 1 1 0 1 0 1 0 0 0 0 1 1 1 1 1 1 1 1 1 1 0 0 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23 Hymenogaster lycoperdineus Vittad. Hymenogaster niveus Vittad. Hymenogaster olivaceus Vittad. Hymenogaster populetorum Tul. Hymenogaster thwaitesii Berk & Broome Hymenogaster vulgaris Tul. apud Berk. & Br. Hysterangium cistophilum Tul. & C.Tul. Hysterangium clathroides Vittad. Hysterangium rickenii Soehner Hysterangium stoloniferum Tul. & C.Tul. Inocybe abjecta P.Karst. Inocybe adaequata (Britzelm.) Sacc. Inocybe albomarginata Velen. Inocybe amethystina Kuyper Inocybe asterospora Quél. Inocybe bongardii (Weinm.) Quél. Inocybe bongardii var. pisciodora (Donadini & Riousset) Kuyper Inocybe bresadolae Massee Inocybe brevicystis Métrod ex Kuyper Inocybe brunneorufa Stangl & J.Veselsky Inocybe cervicolor (Pers.) Quél. Inocybe cincinnata (Fr.) Quél. Inocybe cincinnata var. major (S.Petersen) Kuyper Inocybe cookei Bres. Inocybe corydalina Quél. Inocybe curvipes P.Karst. Inocybe dulcamara (Alb. & Schwein.) P.Kumm. Inocybe erubescens A.Blytt Inocybe flavella P.Karst. Inocybe flocculosa (Berk.) Sacc. Inocybe fraudans (Britzelm) Sacc. Inocybe furfurea Kühner Inocybe fuscidula Velen. Inocybe geophylla/(Pers.) P.Kumm. Inocybe geophylla var. lilacina Gillet Inocybe glabrodisca P.D.Orton Inocybe glabrescens Velen. Inocybe glabripes Ricken Inocybe godeyi Gillet Inocybe griseolilacina J.E.Lange Inocybe haemacta (Berk. & Cooke) Sacc. Inocybe heimii Bon Inocybe hirtella Bres. Inocybe jacobii Kühner Inocybe lacera (Fr.) P.Kumm. Inocybe lanuginosa var. ovatocystis (Boursier & Kühner) Stangl Inocybe maculata Boud. Inocybe malençonii R.Heim Inocybe margaritispora (Berk.) Sacc. Inocybe mixtilis (Britzelm.) Sacc. Inocybe muricellata Bres. Inocybe nitidiuscula (Britzelm.) Lapl. 23 Qball Qil 1 1 1 1 1 1 1 1 1 1 1 1 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 0 1 0 0 0 0 0 0 1 1 0 0 0 1 1 1 1 1 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 1 0 0 0 1 1 1 1 0 0 0 1 1 1 1 0 0 1 1 1 1 1 1 1 1 0 1 1 0 1 1 1 0 0 0 1 1 0 0 1 0 0 0 1 0 0 0 0 1 1 1 1 1 1 1 0 0 1 1 1 0 1 0 0 1 0 1 1 0 1 1 1 1 1 0 1 0 0 24 Qsub Qpyr Qfag Qcoc Qcan 0 0 0 1 0 0 0 0 1 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 1 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 0 1 1 1 0 1 1 1 1 0 0 1 1 1 0 0 0 0 1 0 0 1 1 0 1 0 0 0 0 0 1 0 0 0 0 1 0 0 0 1 1 0 0 0 0 1 0 1 1 0 0 0 0 1 0 1 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 1 1 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 0 1 0 1 0 1 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 1 0 0 0 0 0 Inocybe oblectabilis (Britzelm.) Sacc. Inocybe obscurobadia (J.Favre) Grund & Stuntz Inocybe obscuroides P.D.Orton Inocybe olida Maire Inocybe pelargonium Kühner Inocybe posterula (Britzelm.) Sacc. Inocybe praetervisa Quél. Inocybe pseudoestricta Stangl & J.Veselsky Inocybe pudica Kühner Inocybe pusio P.Karst. Inocybe quietiodor Bon Inocybe rimosa (Bull.) P.Kumm. Inocybe similis Bres. Inocybe sindonia (Fr.) P.Karst. Inocybe splendens R.Heim Inocybe splendens var. phaeoleuca (Kühner) Kuyper Inocybe subporospora Kuyper Inocybe subtrivialis Esteve-Rav., Villarreal & Heykoop Inocybe tarda Kühner Inocybe tenebrosa Quél. Inocybe tenuicystidiata E.Horak & Stangl Inocybe terrigena (Fr.) Kühner Inocybe tjallingiorum Kuyper Inocybe xanthomelas Boursier & Kühner 24 Laccaria affinis (Singer) Bon Laccaria amethystina Cooke Laccaria bicolor (Maire) P.D.Orton Laccaria fraterna (Cooke & Massee) Pegler Laccaria laccata var. laccata (Scop.) Cooke 25 Laccaria laccata var. pallidifolia (Peck) Peck Laccaria laccata var. pseudobicolor Bon Laccaria proxima (Boud.) Pat. Lactarius acerrimus Britzelm. Lactarius acris (Bolton) Gray Lactarius atlanticus Bon Lactarius azonites (Bull.) Fr. Lactarius blennius (Fr.) Fr. Lactarius camphoratus (Bull.) Fr. Lactarius chrysorrheus Fr. Lactarius circellatus Fr. 26 Lactarius decipiens Quél. Lactarius evosmus Kühner & Romagn. Lactarius fuliginosus (Fr.) Fr. Latarius ilicis Sarnari Lactarius lacunarum Romagn. ex Hora Lactarius luridus (Pers.) Gray Lactarius luteolus Peck Lactarius mairei Malençon Lactarius mediterranensis Llistos & Bellu 27 Lactarius mitissimus Fr. Lactarius pallidus Pers. Lactarius pergameus (Sw) Fr. Lactarius piperatus (L.) Pers. Lactarius pterosporus Romagn. Lactarius pyrogalus (Bull.) Fr. 1 1 0 0 1 1 1 1 1 1 1 1 0 1 1 1 0 1 1 1 0 0 0 0 0 1 0 1 1 1 1 0 1 1 0 1 1 1 1 0 1 1 1 1 0 1 0 1 0 0 0 0 0 0 0 1 1 0 0 1 0 1 0 0 0 0 0 0 1 0 0 0 0 1 0 1 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 1 0 1 0 1 1 1 1 1 1 1 1 0 1 1 0 1 1 0 1 1 1 0 0 0 0 1 1 0 1 0 0 0 0 1 1 0 0 0 0 0 1 0 0 1 0 0 0 1 1 1 1 1 1 1 0 1 0 1 1 0 0 0 1 0 0 1 0 0 1 1 0 1 1 0 0 1 0 1 1 1 1 1 1 1 1 0 1 1 0 1 1 1 1 1 1 1 0 1 1 1 0 0 0 1 1 0 1 0 1 0 0 0 0 1 1 1 0 1 1 0 1 1 0 0 1 0 1 1 0 1 0 0 0 1 1 0 0 0 1 0 0 0 0 0 0 0 0 0 1 1 0 1 1 0 1 1 0 1 1 0 1 1 0 1 1 0 0 1 0 1 1 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 0 0 0 0 0 0 0 0 1 0 1 0 1 0 0 1 0 0 0 0 0 0 1 0 0 25 Qball Lactarius pseudoscrobiculatus Basso, Neville & Poumarat Lactarius quietus (Fr.) Fr. Lactarius romagnesii Bon Lactarius rufus (Scop.) Fr. Lactarius rugatus Kühner & Romagn. Lactarius serifluus (DC.) Fr. Lactarius subdulcis (Pers.) Gray Lactarius subumbonatus Lindgr. Lactarius tesquorum Malençon Lactarius uvidus (Fr.) Fr. Lactarius vellereus (Fr.) Fr. Lactarius violascens (J.Otto) Fr. Lactarius zonarius (Bull.) Fr. Lactarius zugazae G.Moreno, Montoya, Bandala & Heykoop Leccinum crocipodium (Letell.) Watling Leccinum lepidum (H.Bouchet ex Essette) Bon & Contu Leccinum quercinum (Pilát) E.E.Green & Watling Leucocortinarius bulbiger (Alb. & Schwein.) Singer Melanogaster ambiguus (Vittad.) Tul. & C.Tul. Melanogaster broomeianus Berk. Melanogaster macrosporus Zeller Melanogaster tuberiformis Corda Melanogaster variegatus (Vittad.) Tul. & C.Tul. Paxillus involutus (Batsch) Fr. Phellodon niger (Fr.) P.Karst. Pisolithus arhizus (Scop.) Rauschert 28 Pseudocraterellus undulatus (Pers.) Rauschert Ramaria aurea (Schaeff.) Quél. Ramaria botrytis (Pers.) Ricken Ramaria broomei (Cotton & Wakef.) R.H.Petersen Ramaria decurrens (Pers.) R.H.Petersen Ramaria fennica (P.Karst.) Ricken Ramaria fennica var. olivacea Schild Ramaria flava (Schaeff.) Quél. Ramaria flavescens (Schaeff.) R.H.Petersen Ramaria flavigelatinosa Marr & D. E.Stuntz Ramaria flavobrunnescens (G.F./A+K.) Corner Ramaria flavosalmonicolor Schild Ramaria formosa (Pers.) Quél. Ramaria gracilis (Pers.) Quél. Ramaria mediterranea Schild & Franchi Ramaria pallida (Schaeff.) Ricken Ramaria quercus-ilicis Schild Ramaria rubripermanens Marr & D.E.Stuntz Ramaria stricta (Pers.) Quél. Ramaria subtilis (Coker) Schild Russula acetolens Rauschert Russula acrifolia Romagn. Russula adusta (Pers.) Fr. Russula aeruginea Fr. Qil Qsub Qpyr Qfag Qcoc Qcan 0 0 0 0 1 0 0 1 1 0 1 1 1 1 1 0 1 1 1 1 0 0 0 1 1 1 1 0 1 0 1 1 0 1 0 0 1 1 1 1 1 1 1 1 1 1 1 0 1 1 0 1 1 0 0 1 0 1 0 1 0 0 1 1 1 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 1 0 0 1 0 0 0 0 1 0 1 1 1 1 1 1 1 0 1 1 0 0 0 1 0 0 0 0 0 0 1 1 0 0 0 0 0 0 1 1 1 1 1 1 0 1 0 0 0 0 0 0 0 0 0 1 1 0 1 1 1 0 0 0 0 0 1 1 0 1 0 1 1 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 0 0 0 0 1 0 0 0 1 0 1 1 0 1 0 1 1 0 0 1 0 0 0 0 1 1 0 0 0 0 0 0 0 1 0 0 0 1 1 1 1 1 1 0 1 1 1 1 0 1 1 0 1 1 1 1 0 0 0 1 0 0 0 0 1 0 1 0 0 0 0 0 1 1 0 0 0 0 0 1 0 0 0 0 1 0 0 0 0 0 1 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 0 1 1 0 0 0 0 1 1 0 0 0 0 0 26 Russula albonigra (Krombh.) Fr. Russula albonigra fo. pseudonigricans (Romagn.) Bon Russula alutacea (Fr.) Fr. Russula amoena Quél. Russula amoenicolor fo. nigrosanguinea Romagn. Russula amoenicolor fo. olivacea Maire Russula amoenicolor Romagn. Russula amoenolens Romagn. Russula anatina Romagn. Russula anthracina Romagn. Russula monspeliensis Sarnari Russula aurea Pers. Russula aurora (Krombh.) Bres. Russula clariana R.Heim ex Kuyper & V.Uure Russula chloroides (Krombh.) Bres. Russula cicatricata Romagn. ex Bon Russula cyanoxantha (Schaeff.) Fr. 29 Russula cyanoxantha var. cutrefacta (Cooke) Sarnari 30 Russula cyanoxantha var. peltereaui Singer Russula decipiens (Singer) Kühner & Romagn. Russula delica Fr. Russula densifolia Secr. ex Gillet Russula fellea (Fr.) Fr. Russula foetens (Pers.) Pers. Russula fragilis Fr. Russula fragrantissima Romagn. Russula galochroa (Fr.) Fr. Russula globispora (J. Blum) Bon Russula graveolens fo. purpurata (Crawshay) P.-I.Keizer & Arnolds Russula graveolens Romell 31 Russula graveolens var. megacantha Bon Russula grisea (Batsch) Fr. Russula heterophylla (Fr.) Fr. Russula ilicis Romagn., Chevassut & Privat Russula illota Romagn. Russula integra (L.) Fr. sensu Maire Russula insignis Quél. 32 Russula krombholzii Schaeff. 33 Russula laurocerasi Melzer 34 Russula lepida Fr. Russula lilacea Quél. 35 Russula lundellii Singer Russula lutea (Huds.) Gray Russula luteotacta Rea Russula maculata Quél. & Roze Russula maculata var. bresadolana (Singer) Romagn. 36 Russula mairei Singer Russula melliolens Quél. Russula melzeri Zvára Russula minutula Velen. Russula multicolor J.Blum Russula nigricans (Bull.) Fr. Russula ochroleuca (Pers.) Fr. 1 1 1 0 1 1 0 0 0 0 0 0 0 0 1 0 0 0 1 1 0 1 1 1 0 0 1 0 1 1 1 0 0 0 1 0 1 0 0 1 0 0 1 0 1 0 1 1 1 1 1 1 0 1 1 1 1 0 1 1 1 1 0 1 0 0 0 0 0 0 0 1 0 1 1 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 1 0 1 0 1 1 1 0 0 1 1 0 1 1 0 0 1 1 1 0 1 1 0 0 0 0 1 1 1 1 1 1 1 1 1 0 1 0 1 1 0 0 1 0 0 0 0 0 1 0 1 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 0 1 1 1 0 0 1 1 1 1 1 1 0 0 1 0 0 0 1 0 0 1 1 0 0 0 0 0 1 0 1 0 0 1 1 1 0 0 1 1 0 1 1 1 1 0 1 0 1 1 1 1 1 1 0 1 1 1 1 0 0 1 0 0 0 0 1 1 1 1 0 1 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 1 0 1 0 0 0 1 0 1 1 0 1 0 0 0 1 1 0 0 0 1 1 1 0 1 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 27 Qball Russula odorata Romagn. Russula olivacea (Schaeff.) Pers. Russula olivacea var. pavonina (Bres.) Reumaux Russula pallidospora J.Blum ex Romagn. Russula parazurea Jul.Schäff. Russula pectinata (Bull.) Fr. Russula pectinatoides Peck Russula persicina Krombh. Russula pseudoaeruginea (Romagn.) Kuyper & Van Vuure Russula pseudointegra Arnoult & Goris Russula puellaris Fr. Russula raoultii Quél. Russula risigallina (Batsch) Sacc. Russula risigallina fo. luteorosella (Brizelm.) Bon Russula romellii Maire Russula rosea Pers. Russula roseipes Secr. ex Bres. Russula rubroalba (Singer) Romagn. Russula rubroalba var. albocretacea Sarnari Russula seperina Dupain Russula silvestris (Singer) Reumaux Russula sororia Fr. 37 Russula sororia var. pseudoaffinis (Migl. & Nicolaj) Sarnari Russula straminea Malençon Russula subazurea Bon Russula subfoetens Wm.G.Sm. Russula vesca Fr. Russula vinosobrunnea (Bres.) Romagn. Russula vinosopurpurea Jul.Schäff. Russula violeipes Quél. Russula werneri Maire Russula virescens (Schaeff.) Fr. Sarcodon fennicus (P.Karst.) P.Karst. Sarcodon cyrneus Maas Geest. Sarcodon imbricatus (L.) P.Karst. Sarcodon joeides (Pass.) Bat. Sarcodon leucopus (Pers.) Maas Geest. & Nannf. Sarcodon scabrosus (Fr.) P.Karsten Scleroderma areolatum Ehrenb. Scleroderma cepa Pers. Scleroderma citrinum Pers. Scleroderma meridionale Demoulin & Malençon Scleroderma polyrhizun (J.F.Gmel.) Pers. Scleroderma verrucosum Bull. Thelephora anthocephala (Bull.) Fr. Thelephora caryophyllea (Schaeff.) Pers. Thelephora palmata (Scop.) Fr. Thelephora terrestris Ehrenb. Tricholoma acerbum (Bull.) Vent. Tricholoma albidum Bon Qil Qsub Qpyr Qfag Qcoc Qcan 1 1 1 0 1 1 1 1 1 0 1 0 1 0 0 1 1 0 1 1 1 0 1 0 1 1 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 1 0 1 0 0 0 0 1 1 1 1 1 0 0 1 0 1 0 1 1 0 1 0 1 0 1 0 1 1 1 1 0 0 0 0 1 1 0 1 1 1 0 0 0 1 1 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 0 0 0 1 0 1 1 1 1 1 0 1 0 1 0 1 0 0 1 1 0 1 1 1 1 1 0 1 1 1 1 0 0 0 0 1 1 0 1 0 0 0 0 0 1 1 0 1 0 0 0 1 1 0 0 0 0 1 0 1 1 1 1 1 0 1 0 1 1 1 1 0 1 1 0 1 0 1 1 1 0 1 0 1 1 1 0 0 1 0 0 1 0 1 0 0 1 1 0 0 0 0 0 1 0 1 1 0 0 0 0 1 0 0 0 1 1 1 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 1 1 1 0 0 1 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 1 1 1 0 0 0 0 0 0 28 Tricholoma album (Schaeff.) P.Kumm. Tricholoma album var. thalliophilum Bon Tricholoma argyraceum (Bull.) Gillet Tricholoma atrosquamosum (Chevall.) Sacc. 38 Tricholoma atrosquamosum var. squamulosum (Bres.) Mort. Chr. & Noordel. Tricholoma aurantium (Schaeff.) Ricken Tricholoma bresadolanum Clemençon Tricholoma bufonium (Pers.) Gillet Tricholoma caligatum (Viv.) Ricken Tricholoma cingulatum (Ahnfelt) Jacobasch Tricholoma columbetta (Fr.) P.Kumm. Tricholoma coryphaeum (Fr.) Gillet Tricholoma lascivum (Fr.) Gillet Tricholoma myomyces (Pers.) J.E.Lange Tricholoma orirubens var. basirubens Bon Tricholoma orirubens var. orirubens Quel. Tricholoma pardalotum Herink & Kotl. Tricholoma portentosum (Fr.) Quél. Tricholoma psammopus (Kalchbr.) Quél. Tricholoma ramentaceum var. quercus-ilicis Bon, Narducci & Petrucci Tricholoma saponaceum (Fr.) P.Kumm. 39 Tricholoma saponaceum var. boudieri (Barla) Barla Tricholoma saponaceum var. squamosum (Cooke) Rea Tricholoma scalpturatum (Fr.) Quél. Tricholoma scioides (Pers.) C.Martin Tricholoma sejunctum (Sowerby) Quél. Tricholoma stiparophyllum Fr. & N.Lund Tricholoma sulphurescens Bres. Tricholoma sulphureum (Bull.) P.Kumm. Tricholoma triste (Scop.) Quél. Tricholoma ustale (Fr.) P.Kumm. Tricholoma ustale var. rufoaurantiacum Bon Tricholoma ustaloides Romagn. Tricholoma viridilutescens M.M.Moser Wakefieldia macrospora (Hawker) Hawker Xerocomus armeniacus (Quél.) Quél. Xerocomus badius (Fr.) Kühner Xerocomus chrysenteron (Bull.) Quél. 40 Xerocomus communis (Bull.) Bon Xerocomus dryophilus (Thiers) Singer Xerocomus ichnusanus Alessio, Galli & Littini Xerocomus moravicus (Vacek) Herink Xerocomus persicolor H.Engel, Klofac, H.Grünert & R.Grünert Xerocomus porosporus Imler 41 Xerocomus roseoalbidus Alessio & Littini Xerocomus rubellus (Krombh.) Quél. 42 Xerocomus spadiceus (Fr.) Quél. Xerocomus subtomentosus (L.) Quél. 43 Xerocomus subtomentosus var. ferrugineus 1 0 1 1 1 1 1 1 1 1 1 0 1 1 1 1 0 0 0 0 1 0 0 1 1 0 0 0 0 0 1 0 0 1 0 1 0 1 1 0 0 0 1 1 1 1 1 1 1 0 1 1 0 0 0 1 0 0 1 0 1 0 0 0 0 0 1 1 1 1 1 1 1 1 0 0 0 1 1 1 0 0 1 0 0 1 0 0 0 1 0 0 0 0 0 0 0 0 1 0 0 0 1 1 1 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 0 0 0 0 0 0 1 0 1 0 1 1 1 0 1 0 0 0 1 0 0 0 1 0 0 0 0 1 0 1 1 1 1 1 1 0 1 0 1 1 0 1 1 0 1 0 1 1 0 1 0 1 1 0 1 0 1 0 1 0 0 1 0 0 0 1 0 1 1 1 1 0 1 0 1 1 1 1 0 1 1 1 0 0 0 1 1 1 0 0 0 0 1 0 1 0 1 0 0 0 1 0 0 0 0 0 0 1 0 1 0 0 1 1 1 0 1 0 0 1 0 1 1 1 1 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 0 0 1 0 1 0 1 0 0 0 1 1 0 0 0 1 0 1 0 1 1 1 1 0 0 1 1 1 1 1 1 1 0 1 1 0 1 0 0 1 1 0 0 0 0 1 1 0 0 0 0 0 0 0 0 1 0 0 1 29 Qball Qil 1 0 1 0 0 0 1 1 1 0 0 416 288 (Schaeff.) Krieglst. Xerocomus subtomentosus var. lanatus (Rostk.) Smotl. 45 Xerocomus subtomentous var. leguei (Boud.) Maire Xerocomus tumidus (Fr.) E.-J.Gilbert Zelleromyces meridionalis Calonge, Mor.-Arr. & J.Gómez 44 Qsub Qpyr Qfag Qcoc Qcan 0 0 1 0 0 0 1 1 0 0 0 0 0 0 0 0 0 411 171 174 21 107 Remarks on the current nomenclatural status of macrofungus taxa compiled for Quercus spp. forests. Include Amanita valens (E.-J.Gilbert) Bertault. 2Corresponds to Amanita ceciliae (Berk. & Broome) Bas. 3Corresponds to Amanita battarrae (Boud.) Bon. 4Corresponds to Amanita curtipes (E.-J.Gilbert). 5 Corresponds to Boletus reticulatus Schaeff. 6Corresponds to Boletus queletii Schulzer. 7Corresponds to Cantharellus cibarius var. ferruginascens (P.D.Orton) Courtec. 8Corresponds to Cortinarius majusculus Kühner. 9Corresponds to Cortinarius amaoenolens Rob.Henry & P.D.Orton. 10Doubtful species (strongly linked to montane coniferous forests). 11Corresponds to Cortinarius nanceiensis var. bulbipodius Chevassut & Rob.Henry. 12Include Cortinarius coerulescentium Rob.Henry. 13Match to the sensu of Malençon & Bertault (1970). 14Corresponds to Cortinarius boudieri Rob.Henry. 15 Corresponds to Cortinarius aleuriosmus Maire. 16Corresponds to Cortinarius subturibulosus Kizlik & Trecol. 17Corresponds to Cortinarius rigens (Pers.) Fr. 18Corresponds to Cortinarius eufulmineus Rob.Henry. 19Corresponds to Cortinarius rubellus Cooke. 20Possibly Corresponds to Cortinarius variiformis Malençon. 21Doubtful species (it is thought to grow only over Cedrus). 22Corresponds to Hygrophorus eburneus var. cossus (Sowerby) Quél. 23Corresponds to Protoglossum niveum (Vittad.) T.M.May. 24Corresponds to Laccaria laccata (Scop.) Cooke. 25Corresponds to Laccaria laccata (Scop.) Cooke. 26Corresponds to Lactarius lacunarum Romagn. ex Hora. 27Corresponds to Lactarius aurantiacus (Pers.) Gray. 28Corresponds to Pseudocraterellus sinuosus (Fr.) Corner. 29Corresponds to Russula cyanoxantha (Schaeff.) Fr. 30Corresponds to Russula cyanoxantha (Schaeff.) Fr. 31 Corresponds to Russula graveolens Romell. 32Corresponds to Russula atropurpurea (Krombhol.) Britzelm. 33Corresponds to Russula grata Britzelm. 34Corresponds to Russula rosea Pers. 35Corresponds to Russula intermedia P.Karst. 36Corresponds to Russula nobilis Velen. 37Corresponds to Russula pseudoaffinis Migl. & Nicolaj. 38Corresponds to Tricholoma squarrulosum Bres. 39Corresponds to Tricholoma saponaceum var. lavedanum Rolland. 40Corresponds to Xerocomus chrysenteron (Bull.) Quél. 41Corresponds to Rubinoboletus roseoalbidus (Alessio & Littini) De Kesel. 42Corresponds to Xerocomus ferrugineus Fr. 43Corresponds to Xerocomus ferrugineus Fr. 44Corresponds to Xerocomus subtomentosus L. 45Corresponds to Xerocomus subtomentosus L. 1 NOTE: Despite that the majority of the Xerocomus species have been included in the genus Boletus (www.speciesfungorum.com), recent phylogenetic studies (Bindez & Hibbett 2006), demonstrate that they constitute an independent genus. Appendix 2. Approximated number of total taxa currently described for the genera here compiled. (Source: Kirk et al. 2001, Mycobank; www.mycobank.org) (order of the genera in brackets). Albatrellus (Polyporales) Amanita (Agaricales) Aureoboletus (Boletales) Boletopsis (Thelephorales) Boletus (Boletales) Cantharellus (Cantharellales) Chalciporus (Boletales) Clavariadelphus (Phallales) 12 taxa 500 5 5 300 65 15 18 30 Cortinarius (Agaricales) Craterellus (Cantharellales) Gauteria (Phallales) Gymnomyces (Russulales) Gyroporus (Boletales) Hebeloma (Agaricales) Hydnellum (Thelephorales) Hydnum (Cantharellales) Hygrophorus (Agaricales) Hymenogaster (Boletales) Hysterangium (Phallales) Inocybe (Agaricales) Laccaria (Agaricales) Lactarius (Russulales) Leccinum (Boletales) Leucortinarius (Agaricales) Melanogaster (Boletales) Paxillus (Boletales) Phellodon (Thelephorales) Pisolithus (Boletales) Protoglossum (Boletales) Pseudocraterellus (Cantharellales) Ramaria (Phallales) Rubinoboletus (Boletales) Russula (Russulales) Sarcodon (Thelephorales) Scleroderma (Boletales) Thelephora (Thelephorales) Tricholoma (Agaricales) Wakefieldia (Boletales) Xerocomus (Boletales) Zelleromyces (Russulales) 2000 20 25 15 10 150 38 120 100 100 50 500 25 400 75 1 25 15 16 5 8 22 220 11 750 36 25 49 200 2 170 17 31