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Biotop of the fungus moth Scardia boletella with 

Biotop of the fungus moth Scardia boletella with 

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Review of literature data as well as new distributional records of the relict and endangered saproxylic tineid moth Scardia boletella (Fabricius, 1794) in Poland are presented. Unpublished museal data from 1954 to 1963 and own observations from 1988 to 2014, mainly from Bieszczady Mts, East Beskid, Masurian Lake District, Białowieża Forest and Podl...

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... NTRODUCTION The fungus moth Scardia boletella (Fabricius, 1794) is a species belonging to the family Tineidae Latreille, 1810, subfamily Scardiinae Eyer, 1924, and genus Scardia Treitsche, 1830, represented globally by six species (Robinson 2009). S. anatomella (Grote, 1881) occurs in Canada, the United States of America and Venezuela, S. assamensis (Robinson, 1986) is known from Assam province in India, S. amurensis (Zugulajev, 1965) from the Rusian Far East (Amur Region and Primorsky Krai), China and Japan, as well as from the United States of America where the species was introduced, S. alleni (Robinson, 1986) from Brunei and Sulawesi, S. caucasica (Zugulajev, 1965) from the Caucasus and S. boletella (Fabricius, 1794) which has Euro-Siberian distribution (Robinson 1986, 2009, Buszko 2004, Gaedike 2011, Landry et al. 2013). Few fossil forms similar to the genus Scardia were also described by Kuznetzov (1941) from Baltic amber which origin is from ca. 40 million years ago. In Europe, the distribution area of S. boletella covers 21 countries ( Fig. 1) and extends from southern and central parts of Scandinavia and the European part of Russia, through Lithuania, Latvia and Estonia, Belarus, Ukraine, Poland, Germany, Czech Republic, Slovakia, Austria, Hungary, Romania, Slovenia, Croatia, Bosnia and Herzegovina, to the northern part of Italy and Greece (Petersen 1957, 1969, Zagulajev 1973, Jalava 1977, Petersen, Gaedike 1979, Aarvik, Mitdgaard 1982, Robinson 1986, Buszko 2004, Lašt ů vka & Liška 2011, Lesar & Govedi č 2010, Pastoralis 2010, Gaedike 2011). This species was also recorded from Switzerland at the beginning of the last century (Rebel 1901), but since then there is no evidence on its presence in this country. In Asia S. boletella is known from few localities in Siberia and the Russian Far East – in the Minussinsk Region, e.g.: Lake Tiberkul in Krasnoyarsk Krai (Central Siberia), Irkutsk Oblast and the Sayan Mts (Koshantschikov 1923, Zagulajev 1973, Robinson 1986). In Poland S. boletella is rarely recorded and known from scattered localities. A few historical data comes, e.g. from the vicinity of Rytro (Schille 1915, Romaniszyn & Schille 1931) and of Ustro ń (Toll 1950), where the species was recorded before 1950. The species was also found in the vicinity of Kraków, in the Beskid Niski and the Bieszczady Mts, as well as in the Bialowie ż a Forest, the Borecka Forest, the I ł awa Lake District (Sosny Taborskie Nature Reserve), the Augustowska Forest and the Knyszy ń ska Forest (Razowski & Palik 1969, Ś liwi ń ski, 1979, Buszko & Nowacki 2000, Buszko 2004, Paw ł owski 2009, Jaworski et al. 2014). As most of the known locations of S. boletella in Poland are situated in subboreal forests in the north-eastern part of the country or in its south part – in the mountain forests; the distribution pattern of this species is regarded as disjunctive. Due to potential various threats for the species it was included in the Red List of Threatened Animals of Poland (Buszko & Nowacki 2002) with category NT (near threatened species), as well as in the Polish Red Data Book of Animals (Buszko 2004) with category LR (lower-risk species), nevertheless, the species is not protected by law. The aim of our work is to review the current state of knowledge on the distribution and biology of S. boletella in Poland. B IOLOGY The biology of S. boletella is relatively well known. The first data on its ecological characteristics were given by Mitterberger (1910) and Koshantschikov (1923), and supplemented later by Zagulajev (1973). It is currently assumed that in the western part of its distribution the species inhabits mainly deciduous and mixed forests typical for temperate climate. Larvae (Fig. 2) feed primarily on large fruiting bodies (sporocarps) of several species of arboreal fungi: e.g. tinder fungus ( Fomes fomentarius (L.: Fr.) Kick.) or representatives of the two genes Polyporus (P. Micheli ex Adans.) (Polyporaceae Fr. ex Corda) and Ganoderma (P. Karst.) (Ganodermataceae Donk) (Zagulajev 1973, Robinson 1986). Furthermore, they often develop inside decaying wood of deciduous trees, mainly birch ( Betula L.), beech ( Fagus L.), alder ( Alnus L.) and elm ( Ulmus L.) (Buszko 2004). Both, standing dead trunks and fallen trees are inhabited (Fig. 3). Larval development in Central Europe takes one year. Trunks or sporocarps inhabited by larvae can be easily detected by the presence of saw dust and frass removed out of the galleries by larvae. Pupation takes place inside larval feeding galleries (Fig. 4), usually inside fruiting body of a fungus, or less often, in the upper layers of wood. Shortly before the adult moth hatch, the pupa emerges from the gallery. Empty pupal case protrudes from the exit hole for a long time, which may also be an indication of the species presence (Figs 5 & 6). Adults (Fig. 7) are on wings from the beginning of June until end of July. They reach 37-60 mm of wingspan and are active mostly at dusk and night (Robinson 1986, Buszko 2004). M ETHODS Data on the occurrence of S. boletella in Poland were mostly taken from the literature. Besides, we listed data on museal specimens, and new data: our own and those that have been provided to us by other Polish lepidopterologists and come from the years 1988-2014. Most of the specimens were caught with use of the mercury mix-light lamps 250-500W, as well as in barrier traps installed on the sporocarps of bracket fungi. Voucher specimens are held in authors’ collections and museums. Additional data were collected on the basis of the characteristics of larval feeding galleries and the presence of empty pupal cases protruding from bracket fungi, decaying trunks, etc. Names of zoogeographical regions ( ● ) follow the division proposed in Catalogue of Polish fauna (Burakowski et al. 1990), while the names of physico-geographical mezoregions (–) are based on the Regional Geography of Poland (Kondracki 2002). Locations ( ■ ) are assigned to UTM (Universal Transverse Mercator) 10x10 km grid. Abbreviations used in the text are as follows: ISEZ – Museum of Natural History, Institute of Systematics and Evolution of Animals, Polish Academy of Science, Cracow; MIZ – Museum and Institute of Zoology, Polish Academy of Sciences, ...

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... Just like in the whole subfamily, this feeding habit is also observed in other genera of Scardiinae, including Holarctic Scardia Treitschke and Montescardia Amsel, with nearly ten and three species known, respectively. The biology of the red-listed species Scardia boletella F. has been especially well documented (e.g., Bury et al. 2014), and ecological studies on this species have been also carried out (Jonsell et al. 1998;Jonsell and Nordlander 2002;Fritz 2004). The Scardiinae comprise another saproxylic species-Vespitinea gurkharum Robinson and Carter, from Brunei, where a remarkable example of wasp mimicry was recorded (Robinson and Carter 1989). ...
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Larvae of surprisingly many Lepidoptera species depend on dead wood and wood-decay fungi and are thus considered saproxylic insects. This interesting group has been scientifically neglected for many years, and few studies have been conducted concerning its biology, taxonomy, distribution, and ecology. Merely several dozen species of saproxylic Lepidoptera are known from North European countries; however, the highest species diversity is observed in tropical forests, where only some studies on this group have been so far conducted. This chapter provides an overview of knowledge about the diversity of saproxylic Lepidoptera, based on the world subject literature published over the last century. The greatest species richness of saproxylic Lepidoptera has been identified within two families: Tineidae and Oecophoridae, but a number of other lineages of Lepidoptera also include saproxylic taxa. All Lepidoptera families known to contain saproxylic species are described here in systematic order. Examples of saproxylic species and genera are presented, and some aspects of their biology and ecology are discussed. Major threats to these insects, related to forest management, are briefly outlined. The needs and directions for further research on saproxylic Lepidoptera are highlighted.
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Area of the Beskid Niski Landscape Park is a unique place in terms of the occurrence of rare and protected fungi. To the most valuable species found in this area belongs Hericium erinaceus and Hydnellum concrescens – fungi under strict protection, also considered as endangered species in country and in Polish Carpathians. Valuable are also considered as extinct Phellodon confluens, and endangered Bankera violascens, Cyphella digitalis, Mucronella calva and very rare in Poland Pluteus pellitus. In total, in Beskid Niski Landscape Park 108 species under protection, rare and endangered were found. The vast and varied area of described Park probably hides many interesting taxons. It is estimated that 426 species, which have been found to this day in Beskid Niski Landscape Park is about 50% of the actual state. Therefore, further research are necessary in terms of frequency of observations, other terms and systematic groups which have not been studied yet, for example Agaricus, Collybia, Cortinarius, Entoloma, Hygrocybe, Inocybe and Tricholoma.
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Opracowanie wykonano na potrzeby dokumentacji projektowej Parku Krajobrazowego Beskidu Niskiego wykonanej przez: Fundacja Dziedzictwo Przyrodnicze, ul. Mickiewicza 44/5, 37-700 Przemyśl, tel. 88103558. Projekt współfinansowany ze środków: Fundacja WWF Polska, ul. Mahatmy Gandhiego 3, 02-645 Warszawa, tel. (22) 849 84 69 / 848 73 64.