Somogyi Múzeumok Közleményei 17/B. - Természettudományi tanulmányok (2006)

Balázs Ildikó: Nagygombák vizsgálata a Kaposvár melletti Tókaji-parkerdőben - Macrofungi examination in Tókaji Park forest near Kaposvár, Southwest Hungary

30 BALÁZS ILDIKÓ KRIEGLSTEINER G. J. 1991-1993: Verbreitungsatlas der Großpielze Deutschlands. Band 1-2. Ulmer, Stuttgart, pp. 97, 459. MOSER M. 1993: Guida alla determinazione dei funghi Vol. 1. (Die Röhrlinge und Blätterpilze). Saturnia, Trento. pp. 565. PÁL-FÁM F. 2001: A Mecsek hegység nagygombái (és néhány mikrogomba). Fungisztikai, ökológiai és cönológiai vizsgálatok. PhD disszertáció, Szent István Egyetem, pp. 174. PÁL-FÁM F. 2002: Mycological characterization and comparison of climax forest associations in the Mecsek Mountains. Acta Microbiologica et Immunologica Hungarica 49/2-3: 177-191. PÁL-FÁM F., RUDOLF К. 1999: Data to the knowledge of macrofungi of some habitats exposed to anthropogenous influence in Belső-Cserehát. Publ. Univ. Horticulturae Industriaeque Alimentariae Vol. LIX.: 183-190. PÁL-FÁM F., RUDOLF К. 2003: Macrofungi as indicators in forest stands stronghly influenced by man in Belső-Cserehát. Erdei Kiadványok Vol. 1: 336-341 RIMÓCZI I., SILLER I., VASAS G., ALBERT I.., VETTER J., BRATEK Z. 1999: Magyarország nagygombáinak javasolt Vörös Listája. Mikológiái Közlemények 38/1-3: 107-132. RUDOLF K., PÁL-FÁM F. 2004: Erős antropogén hatásnak kitett erdők nagygombáinak természetvédelmi értékelése a Belső- Cserehátban. Természetvédelmi Közlemények 11: 175-183. SARNARI M. 1998: Monográfia illustrata del génère Russula in Europa I. AMB, Trento. pp. 784. SILLER I., PÁL-FÁM F., FODOR L.: Erdők állapotának nyomon követése nagygombák segítségével. Természetvédelmi Közlemények 11: 185-194. SILLER I., VASAS G., PÁL-FÁM F, BRATEK Z., ZAGYVA I. In press: Hungarian distribution of macrofungi species suggested for legal protection in Hungary. Studia Botanica. pp. 131, 163. TÓTHMÉRÉSZ В. 1996: NuCoSA. Programcsomag botanikai, zoológiai és ökológiai vizsgálatokhoz. Synbiologia Hungarica 2/1:1-84. VASAS G. 1993: A gombák régi és új konzerválási módja a Magyar Természettudományi Múzeum Növénytárában - Mikológiái Közlemények 32/1-2: 33-42. Macrofungi examination in Tokaji Park forest near Kaposvár, Southwest Hungary ILDIKÓ BALÁZS Present paper concerns the summarisation of the macrofungi investigations in human-influenced habitats in the Tokaji Park forest, near Kaposvár, Southwest Hungary. Aims of the investigations were: exploration of the funga; characterisation of the different habitats based on macrofungi species composition, species number, functional distribution, as well as number and distribution of endangered species; comparison of the different habitats based on fungal communities; mycological comparison of the habitats with similar habitats in Mecsek Mts., submediterranean region; ascertaining indicative species; characterisation of the habitats from the point of view of nature conservation. The investigations lasted two years in three sample areas: alder forest, hornbeam-oak forest and spruce plantation. Totally 13 samplings were effectuated. The macrofungi species collected were documented (near the basic data) with fungaria and photo. As result a number of 159 macrofungi species were documented, from these 54 endangered. The native hornbeam-oak forest was the most valuable from the point of view of nature conservation with two „critically endangered" and 26 „endangered" species. Three different functional groups were dominant in the three different habitats: wood inhabiting saprotrophs in the alder forest; mycorrhizals in the hornbeam-oak forest; and soil inhabiting saprotrophs in the spruce plantation. According to number and proportion of the necrotrophic parasites the alder forest was the most undisturbed. Similarity between the hornbeam-oak forest and spruce plantation was established according to soil inhabiting macrofungi communities; similarity between the hornbeam-oak forest and alder forest was established according to wood inhabiting macrofungi communities. A number of 9 species with indicative value were ascertain, 4 of these indicating natural conditions (initial and optimal phases of wood decomposition, lack of forestry management), 5 indicating different human influences (soil nitrogen increase, disturbing etc.).