Snout-beetles (Coleoptera, Curculionoidea) from the Ocna Mureş
Transcription
Snout-beetles (Coleoptera, Curculionoidea) from the Ocna Mureş
Bul.inf. Soc.lepid.rom., 20: 71-94, 2009ISSN 1842 - 2144 Snout-beetles (Coleoptera, Curculionoidea) from the Ocna Mureş city area (Romania) Lucian Alexandru Teodor & Dragomir Cosmin David Summary We recorded 80 species belonging to 51 genera, 10 subfamilies and 4 families of Curculionoidea in the studied area (tab. 1). We have reported the rare species Ceutorhynchus turbatus Schltz. again in the area and also reported the presence of the Romanian endemic and rare subspecies Plinthus squalidus elekesi (Ormay). The Palearctic spread species were predominant, followed by the Eurosiberian, European-western and central Asian, and European ones. Dominant species was Nedyus quadrimaculatus (L.), which also had the greatest abundance in pastures and in willow riverine forests. Taeniapion urticarium (Hbst.) and Parethelcus pollinarius (Forst.) were codominant. The highest snout-beetles biodiversity was reported in the Banţa Hill pasture (0.671), followed by Ocna Mureş willow riverine forest (0.666). Uioara de Jos pasture has the lowest biodiversity index value (0.251). Keywords: snout-beetles, Ocna Mureş area, faunistical studies, zoogeografy, ecology, Romania Introduction One of the areas in Romania where almost no investigations regarding the Curculionoidea fauna have been made is Ocna Mureş. Only the species Ceutorhynchus turbatus Schultze, 1903 (Petri 1925/’26) has been reported in the area, until present. Ocna Mureş city (265 m altitudie above sea level) is situated in the central part of Romania, north-east of Alba district (58 km from Alba Iulia), on the left bank of the Mures river middle course, in the hill zone of the Subcarpathians, between the Transylvanian Plain and Târnavelor Plateau, 46º23′53″ degrees north latitude and 23º51′22″ east longitude from Greenwich. In the western side the city is bordered by the meadows of the AlbaIulia-Turda passage, while the northern border of the city is represented by the anfractuosities of the Mureş Valley. The south-western boundary is limited by the Ciunga Hills (Nejoapa Hill) and in the southern part by the Banţa Hill. 71 Ocna Mureş is the neighbouring city of: Noşlac (to the north-east), Silivaş (to the south), Cisteiul de Mureş (to the west), Unirea (to the northwest) and Războieni-Cetate (to the north). In 1933 Uioara de Jos (Ciunga) situated at about 1 km south-west of Ocna Mureş and Uioara de Sus, at aproximately 500 m, on a terrace of a 50 m hillock, joined the city of Ocna Mureş. Matherial and methods The biological matherial has been sampled from the Ocna Mureş area between 2004-2006, by sweeping the vegetation with the aid of entomological nets and through direct collecting from the host plant. Other samplings involved shaking the top of the trees and shrubs and gatherig the matherial using the umbrella net. The species identification has been done in the laboratory using the binocular magnifier along with specific references (Endrödi 1963, Dieckmann 1988, Freude, Harde & Lohse 1981, 1983, Colonnelli 1994, Behne 1994, 1998). Determination of the species has been made based upon specific morphological characters as well as by studing the male genitalia. We have calculated and used the following ecological indices: relative abundance, dominance, ecological diversity index and evenness. The Palaeontological Statistics (PAST `94) programme was used in order to calculate these indices. For sampling the biological matherial 8 stations (fig. 1) which are comprised in 6 types of habitats have been chosen: mixed coniferous and deciduous forest, willow riverine forest, forest gap, pasture, wet meadow and ruderal vegetation. Description of the sampling stations (fig. 1): 1. Mixed coniferous and deciduous forest – on the Banţa hill - Ocna Mureş, characterised by the presence of scots pine (planted) (Pinus sylvestris) as a dominant species mixed with norway spruce (Picea abies), oak (Quercus sp.) and european beech (Fagus sylvatica). The arbustiv layer is less represented, being edified by common hawthorn (Prunus spinosa), dog rose (Rosa canina) etc. 2. Forest gap - Ocna Mureş - characterised by the presence of shrubs which replace the trees that have been chopped down and by the presence of some ruderal herbal species. In this way, shrubs of danewort (Sambucus ebulus), dog rose (Rosa canina), common hawthorn (Prunus spinosa) and species of Arctium, Taraxacum, Urtica appear. 3. Willow riverine forest from Ocna Mureş, situated along of the river Mureş Valley on the water banks. The dominant species of this ecosystem is the willow tree (Salix alba) followed by the white poplar (Populus alba). The grass-layer is represented by genus Urtica, Mentha, Phragmites, etc. 72 4. Pasture - Banţa Hill – Ocna Mureş – characterised by the presence of thermophile vegetation out of which the next species are very common: Poa pratensis, Dactylis glomerata, Alopecurus pratensis, Leontodon autumnalis, Euphorbia cyparissias, Anthriscus sylvestris and others. 5. Pasture – located in the Uioara de Sus village, it is represented by melliferous and fodder plants of economic importance. 6. Pasture – located in the Uioara de Jos (Ciunga) village, has a floristic composition that resembles the one in the Uioara de Sus village. 7. Wet meadow, Ocna Mureş – it is characteristic for the wet zones and in consequence there are many higrophile and mezo-higrophile species. These species show an affinity for a relatively high humidity. The dominant species are the common reed (Phragmytes australis) and bulrush (Typha latifolia), alongside the yellow iris (Iris pseudacorus), sedges (Carex sp.), marsh-marigold (Caltha laeta), and others. 8. Ruderal vegetation, Ocna Mureş – located near the country roads gives a proper habitat for ruderal species that succeed to endure the harsh conditions (high degree of xerophytism, soil very poor in minerals). Fig. 1. Distribution of sampling stations: 1. mixed coniferous and deciduous forest (Banţa Hill – Ocna Mureş), 2. forest gap (Ocna Mureş), 3. willow riverine forest (Ocna Mureş), 4. Banţa Hill pasture (Ocna Mureş), 5. pasture (Uioara de Sus), 6. pasture (Uioara de Jos) 7. wet meadow (Ocna Mureş), 8. ruderal vegetation (Ocna Mureş). 73 Results and disscutions A number of 563 individuals, which belong to 80 species from 51 genera, 10 subfamilies and 4 families of Curculionoidea (tab. 1, fig. 2, 3) have been collected. From the total of 80 identified species, 79 are at their first report in the investigated area and the rare species Ceutorhynchus turbatus Schltz. has been reported again in Ocna Mureş. According to the number of species, the most represented subfamilies were Entiminae (26 species), Apioninae (21 species), Curculioninae (13 species), while the least represented ones were the subfamilies Baridinae, Hyperinae, Nanophyinae şi Rhynchitinae (fig. 2). In the investigated zone, the Curculionoidea species have been differently assigned to the families, ascertaining that the Curculionidae family have the most representants regarding the number of species (72%). The next family is Apionidae (26% species), followed by the Nanophyidae and Rhynchitidae families, each with 1% (fig. 3). Table 1 The snout-beetles identified in Ocna Mureş area during 2004-2006, faunistical, ecological and zoogeografical data Abreviations: n= number of individuals/sampling station, rs = rare species, St = sampling stations 1-8 (see matherial and methods). Ecological indices: A%= relative abundance, D%= dominance. Distribution in Romania: Bn=Banat, Cr=Crişana, Db=Dobrogea, M=Moldavia, Mm=Maramureş, Mt=Muntenia, Ot=Oltenia, Tr=Transylvania (bibliographical data prezented in: Vlad-Antonie & Teodor 2000, Teodor & Vlad-Antonie 2007). General distribution: c-euro = central European species; c, e, euro = central and eastern European species; euro = European species; euras = Eurasian species; eurosib = Eurosiberian species; euro-w-c-as = European, western and central Asian species; hol = Holarctic spread species; n-med = northern Mediterranean species; pal = Palearctic spread species; Ro = Romanian endemic subpecies; s-e c-euro = south-eastern and central European species; w-pal = western Palearctic spread species s-pal = southern Palearctic spread species (for general distribution of species we used different bibliographical data: Endrödi 1963, Dieckmann 1980, 1983, 1986, 1988, Freude, Harde & Lohse 1981, 1983, Colonnelli 1994, Behne 1994, 1998, Knutelski 2005). 74 75 1 1 1 1 2 1 1 1 16.V.2004 18.VIII.2004 19.IX.2006 18.VIII.2004 19.VII.2004 Ceratapion (Acanephodus) onopordi (Kirby, 1808) Ceratapion (Echinostroma) scalptum Mulsant & 6.VIII.2004 Rey, 1859 20.V.2006 13.VIII.2004 Aspidapion (s. str.) validum (Germar, 1817) Omphalapion hookeri (Kirby, 1808) Ceratapiini 1 1 2 n 23.IV.2005 15.VIII.2005 18.VIII.2004 Date Aspidapion (s. str.) radiolus (Marsham, 1802) Aspidapiini Perapion (s. str.) violaceum (Kirby, 1808) Aplemonini Apion frumentarium (Linnaeus, 1758) Curculionoidea Apionidae Apioninae Apionini Taxa 4 7 1 2 5 2 2 6 6 3 2 St 2.857 2.439 3.333 1.234 4.081 0.413 2.469 0.413 6.25 2.469 A% 0.355 0.177 0.532 0.532 0.177 0.177 0.355 D% Tr, Mm, Bn, M, Mt Tr, Bn Tr, Bn, M, Mt, Db Tr, Bn, Mt, Db Tr, Bn, Mm, M, Mt, Db pal euro-w-c-as euro-w-c-as euro-w-c-as pal pal pal Tr, Mm, M, Mt, Db, Bn Tr, Bn, Ot, Mt, M, Db General distribution Distribution in Romania 76 2 1 2 7 4 6.VIII.2004 15.VIII.2005 19.VII.2004 13.VIII.2004 19.VII.2005 Catapion seniculus (Kirby, 1808) 1 1 3 1 1 6 19.VII.2004 20.V.2006 Hemitrichapion (Dimesomyops) pavidum (Germar, 19.VII.2004 1817) 22.IV.2006 13.VIII.2004 19.VII.2005 Eutrichapion (s. str.) viciae (Paykul, 1800) Oxystomatina Oxystomatini Catapiina Catapion jaffense (Desbrochers des Loges, 1896) 18 12 1 2 5 4 n 6.VIII.2004 18.VIII.2004 15.VIII.2005 20.V.2006 23.IV.2005 22.IV.2006 Date Taeniapion urticarium (Herbst, 1784) Exapiini Taxa 4 5 6 7 8 5 3 5 7 8 1 1 2 3 4 6 6 St 2.857 6.122 0.413 2.439 8.695 2.040 6.25 4.081 17.07 5.797 6.666 3.718 60 14.81 6.25 5.714 A% Tr, Ot, Mt, M, Db Tr, Bn, Mm, M, Mt 2.131 Tr, Bn, Mm, M, Mt, Db Tr Tr, Bn, M, Mt, Db Distribution in Romania 0.177 2.486 0.355 7.460 D% pal pal pal n-med euro-w-c-as General distribution 77 1 2 2 3 1 6 20.V.2006 18.VIII.2004 20.V.2006 22.IV.2006 19.IX.2006 19.VII.2005 Protapion filirostre ( Kirby, 1808) Protapion fulvipes (Fourcroy, 1785) 2 2 3 2 1 10 6.VIII.2004 18.VIII.2004 20.V.2006 19.VII.2004 13.VIII.2004 19.VII.2005 Protapion apricans (Herbst, 1797) Piezotrachelini 19.VII.2004 Stenopterapion tenue (Kirby, 1808) 1 1 22.IV.2006 Ischnopterapion (s. str.) loti (Kirby, 1808) 1 n 1 19.VII.2004 Date Ischnopterapion (s. str.) aeneomicans (Wencker, 15.VIII.2005 1864) Synapiina Holotrichapion (s. str.) ononis (Kirby, 1808) Taxa 2 4 6 6 8 4 1 2 4 5 7 8 5 6 3 5 St 8.695 1.652 2.469 5.714 2.857 6.666 2.469 8.571 4.081 2.439 14.49 2.040 0.413 6.25 2.040 A% 2.486 0.177 3.552 0.177 0.177 0.177 0.177 D% pal eurosib Tr, Bn, M, Mt, Db Tr, Mm, M, , Bn, Ot, Mt Db pal pal pal w-pal pal General distribution Tr, Mm, M, Bn, Ot, Mt, Db Tr, Bn, Ot, Db Tr, Bn, M, Mt, Db Tr, Bn, M, Mt Tr, Bn, Mm, M, Mt, Db Distribution in Romania 78 1 22.IV.2006 20.V.2006 20.V.2006 20.V.2006 Ceutorhynchus floralis (Paykull, 1792) Ceutorhynchus turbatus Schultze, 1903 rs Coeliastes lamii (Fabricius, 1792) 2 1 2 1 20.V.2006 Ceutorhynchus erysimi (Fabricius, 1787) Ceutorhynchinae Ceutorhynchini Baris artemisie (Herbst, 1795) 3 1 4 1 1 1 2 18.VIII.2004 15.VIII.2005 20.V.2006 19.VII.2005 20.V.2006 n Date 16.V.2004 16.IV.2004 Curculionidae Baridinae Baridini Baridina Pseudoprotapion elegantulum (Germar, 1818) Protapion trifolii (Linnaeus, 1768) Taxa 4 4 1 6 4 2 7 4 2 3 4 8 St 5.714 2.857 6.666 0.413 2.857 3.703 2.439 11.42 1.234 6.25 2.857 2.898 A% 0.355 0.177 0.355 0.355 0.710 0.710 0.888 D% euro-w-c-as w-pal Tr, Bn, M, Mt pal hol Tr, M, Mt Tr, Mm, Cr, Bn, Ot, Mt, M, Db Tr, Bn, Cr, M, Mt, Db eurosib pal Tr, Bn, M, Mt, Db Tr, Bn, Cr, M, Mt, Db pal General distribution Tr, Bn, Mm, M, Mt, Db Distribution in Romania 79 23.IV.2005 20.V.2006 Anthonomus (Furcipus) rectirostris (Linnaeus, 1758) 31.VIII.2005 Anthonomus (s. str.) rubi (Herbst, 1795) Curculioninae Anthonomini Pelenomus comari (Herbst, 1795) Phytobiini 19.VII.2005 Trichosirocalus troglodytes (Fabricius, 1787) 1 1 1 2 1 4 8 10 5 4 101 88 6 20 6 6.VIII.2004 16.V.2004 18.VIII.2004 15.VIII.2005 20.V.2006 23.IV.2005 22.IV.2006 19.VII.2005 23.IV.2005 22.IV.2006 16.IV.2004 n Date Thamiocolus viduatus (Gyllenhal, 1837) Parethelcus pollinarius (Forster, 1771) Nedyus quadrimaculatus (Linnaeus, 1758) Taxa 4 6 5 8 7 1 2 2 3 4 6 6 8 6 6 St 2.857 0.413 2.040 2.898 2.439 2.898 10.74 78.09 31.25 11.42 22.316 13.33 A% 0.177 0.177 0.177 0.355 0.177 4.61 40.14 D% Tr, Mm, Cr, Bn, Ot, Mt, M Tr, M, Mt, Cr, Bn eurosib pal euras pal Tr, Bn, Mm, M, Mt Tr, M, Ot, Mt euro w-pal eurosib General distribution Tr, M, BN Tr, M, Cr, Bn Tr, Bn, Cr, Mm, M, Mt, Db Distribution in Romania 80 1 1 20.V.2006 13.VIII.2004 19.VII.2004 Tychius picirostris (Fabricius, 1787) Tychius quinquepunctatus (Linnaeus, 1758) 1 1 19.VII.2005 Tychius aureolus Kiesenwetter, 1851 1 1 19.VII.2005 20.V.2006 1 1 1 n Sibinia viscariae (Linnaeus, 1761) Tychiini Tychiina Smycronyx (s. str.) jungermanniae (Reich, 1797) Smicronychini Isochnus populicola (Silfverberg, 1977) 16.V.2004 13.VIII.2004 Rhinusa tetra (Fabricius, 1792) Rhamphini Rhamphina 20.V.2006 Date Gymnetron labile (Herbst, 1795) Mecinini Taxa 5 4 7 8 8 4 2 7 4 St 2.040 2.857 2.439 1.449 1.449 2.857 1.234 2.439 2.857 A% 0.177 0.355 0.177 0.177 0.177 0.177 0.177 0.177 D% Tr, Bn, Mm, M, Db Tr, Bn, Cr, M, Db Tr, Bn, Mm, M, Mt, Db Tr, Bn, Cr, M, Mt, Db, Tr, Mm, Bn, Ot, Mt, M, Db euras hol euro-w-c-as eurosib pal eurosib eurosib Tr, M, Mt, Ot, Db, Cr, Bn, Mm Tr, Bn, Cr, Mm, M, Mt euro General distribution Tr, Bn, Cr, M Distribution in Romania 81 Phyllobius (Metaphyllobius) pomaceus (Gyllenhal, 1834) 16.V.2004 20.V.2006 Dodecastichus geniculatus (Germar, 1817) Phyllobiini 16.IV.2004 7-11.IV. 2004 Otiorhynchini Otiorhynchus (Cryphiphorus) ligustici (Linnaeus, 1758) Otiorhynchus (Paracryphiphorus) orbicularis (Herbst, 1795) 16.V.2004 Graptus triguttatus (Fabricius, 1775) Entiminae Alophini 12 1 1 2 2 1 6 13.VIII.2004 19.VII.2005 Tychius stephensi Schönherr, 1836 1 Tychius medicaginis Ch. Brisout de Barneville, 1862 19.VII.2005 n 1 Date 19.VII.2005 Tychius junceus (Reich, 1797) Taxa 2 4 7 2 2 7 8 8 8 St 14.81 2.857 2.439 2.469 2.469 2.439 2.898 1.449 1.449 A% 2.131 0.177 0.177 0.355 0.355 1.243 0.177 0.177 D% n-med s-e, c-euro Tr, Bn, Cr, Mm, M, Mt Tr, Cr, Bn, Ot, M c-euro hol euro Tr, Bn, Mt Tr, Cr, Bn, Ot Tr, Bn, Mm, M, Mt, Db hol euro-w-c-as Tr, M, Mt, Db, Cr Tr, Bn, Mm, M, Mt, Db w-pal General distribution Tr, Cr, M, Mt, Db Distribution in Romania 82 16.V.2004 Phyllobius (s. str.) vespertinus (Fabricius, 1792) Foucartia liturata (Stierlin, 1884) Eusomus ovulum (Germar, 1824) 1 1 1 2 16.V.2004 20.V.2006 19.VII.2005 13.VIII.2004 4 1 1 16.V.2004 16.IV.2004 Liophloeus (s. str.) tessulatus (O.F.Muller, 1776) Liophloeus (Liophloeodes) liptoviensis (J. Weise, 1894) Sciaphilini 16.V.2004 Polydrusus (Eustolus) pterygomalis (Boheman, 1840) Polydrusini 6 1 5 3 16.IV.2005 23.IV.2005 22.IV.2006 16.IV.2004 Phyllobius (s. str.) pyri (Linnaeus, 1758) 1 1 20.V.2006 Phyllobius (s. str.) betulinus (Bechstein & Scharfenberg, 1805) n Date Taxa 7 2 4 8 2 7 2 2 2 6 6 7 4 St 2.439 1.234 2.857 2.898 4.938 2.439 1.234 1.234 7.31 2.479 7.407 2.857 A% 0.177 0.710 0.710 0.177 0.177 0.177 2.664 0.177 D% Tr, Mm, M Tr, M, Mt, Ot, Db, Bn, Mm Tr, M, Bn Tr, Bn, M Tr, Bn, Mm, M, Db Tr, M, Mm Tr, M, Ot, Mt, Cr, Bn Tr, M, Ot, Cr, Bn Distribution in Romania c, e, euro e-sib c-euro c-euro euro euro eurosib n-med General distribution 83 19.VII.2004 Sciaphobus (s. str.) caesius (Hampe, 1870) 1 2 1 5 15.VIII.2005 20.V.2006 31.VIII.2005 19.VII.2005 19.VII.2004 Sitona (s. str.) lineatus (Linnaeus,1758) Sitona (s.str. ) ononidis Sharp, 1860 3 1 19.VII.2005 Sitona (s. str.) lepidus Gyllenhal, 1834 Sitona (s. str.) humeralis Stephens, 1831 Sitona (s. str.) hispidulus (Fabricius, 1776) Sitona (s. str.) cylindricollis (Fabraeus, 1840) 1 2 1 1 3 1 1 1 1 1 2 1 n 18.VIII.2004 15.VIII.2005 20.V.2006 31.VIII.2005 31.VIII.2005 22.IV.2006 15.VIII.2005 22.IV.2006 19.VII.2005 19.VII.2004 Sitonini 13.VIII.2004 Date Paophilus afflatus (Boheman, 1883) Taxa 5 3 4 5 8 8 2 3 4 5 5 6 3 6 8 5 5 7 St 6.122 6.25 5.714 2.040 7.246 1.449 1.234 12.5 2.857 2.040 6.122 0.413 6.25 0.413 1.449 2.040 4.081 2.439 A% 0.532 1.598 0.355 0.532 0.710 0.888 0.355 0.177 D% Tr, Mm, Cr, Bn, Ot, Mt, M, Db Tr, Bn, Cr, Mm, M, Mt, Db Tr, Mm, Bn, Ot, Mt, M, Db pal hol hol pal pal Tr, Mm, Bn, Ot, Mt, M Tr, Bn, Cr, Mm, M, Mt hol se, c-euro s-e, c-euro General distribution Tr, Cr, Mm, M, Mt, Db Tr, Bn, M, Mt Tr, M, Mt, Bn Distribution in Romania 84 3 2 5 1 2 1 1 19.VII.2005 15.VIII.2005 16.V.2004 18.VIII.2004 16.IV.2004 13.VIII.2004 13.VIII.2004 19.VII.2005 Trachyphloeini Trachyphloeina Trachyphloeus alternans Gyllenhall, 1834 Hyperinae Hyperini Hypera(s. str.) ononidis (Chevrolat, 1863) Tanymecus palliatus (Fabricius, 1787) Sitona (s. str.) sulcifrons (Thunnberg, 1789) Tanymecini Tanymecina Chlorophanus viridis viridis (Linnaeus, 1758) 1 1 2 10 10 2 6.VIII.2004 19.VII.2004 13.VIII.2004 19.VII.2005 31.VIII.2005 Sitona (s. str.) puncticollis Stephens, 1831 n Date Taxa 8 7 2 2 7 7 3 8 1 5 7 8 5 St 1.449 2.439 7.31 7.406 12.5 4.347 3.333 4.081 24.39 14.49 4.081 A% 0.177 0.177 1.598 0.355 0.888 4.085 D% Tr, M, Db Tr, M, Mt, Db, Cr, Bn c-euro euro eurosib euro Tr, Bn, Mm, M, Mt Tr, Mm, Cr, Bn, Ot, Mt, M, Db pal pal Tr,M, Ot, Cr, Bn, Mt, Db, Mm Tr, Bn, Cr, Mm, M, Mt, Db General distribution Distribution in Romania 85 Molytinae Plinthina Plinthus squalidus elekesi (Ormay, 1888) rs Hylobiini Hylobiina Lepyrus capucinus (Schaller, 1783) 1 1 18.VIII.2004 1 16.IV.2004 16.IV.2004 Cleonis pigra (Scopoli, 1763) 2 1 16.IV.2004 16.IV.2004 17 2 n 19.VII.2004 19.VII.2004 Date Bothynoderes affinis (Schrank, 1781) = Chromoderus fasciatus (Muller, 1776) Larinus (Larinomesius) obtusus Gyllenhal, 1836 Cleonini Adosomus roridus (Pallas, 1781) Larinus (Phyllonomeus) turbinatus Gyllenhal, 1836 Lixinae Lixini Taxa 2 7 7 7 7 5 5 St 1.234 2.439 2.439 4.87 2.439 34.69 4.081 A% 0.177 0.177 0.177 0.355 0.177 3.019 0.355 D% Romania euro Tr, Cr, Bn, Ot, Mt, M pal pal e-sib euro-w-c-as s-pal General distribution Tr, Bn Tr, M, Ot, Mt, Db, Bn Tr, Bn, Ot, Mt. M, Db Tr, M Tr, Mm, Bn, Ot, Mt, M, Db Tr, Bn, Mm, M, Mt, Db Distribution in Romania 86 Rhynchitidae Rhynchitinae Deporaini Deporaina Deporaus (s. str.) betulae (Linnaeus, 1758) Nanophyes marmoratus (Goeze, 1777) Nanophyidae Nanophyinae Nanophyini Taxa 1 1 19.VII.2004 20.V.2006 1 n 20.V.2006 Date 4 5 4 St 2.857 2.040 2.857 A% 0.177 0.355 D% Tr, Mm, M, Mt, Db Tr,Bn, Cr, Mm, M, Ot, Mt, Db Distribution in Romania eurosib eurosib General distribution Fig. 2. Percentage of Curculionoidea subfamilies according to the number of species, in Ocna Mureş area. Mureş Species with faunistical importance Ceutorhynchus turbatus Schultze, 1903 - rare species - Collected matherial: 1 ♂, 20.V. 2006 –Banţa forest (station 1) – Ocna - General distribution: Europe, West and Central Asia - Other reports from Romania: Transylvania: Ocna Mureş (Petri 1925/26), Arvăţeni (Kocs & Podlussány 1997), Hăşmaş (Teodor, Beldean & Crişan 1998); Moldavia: Cucuteni and Ruginoasa (Marcu 1947); Muntenia (Greater Wallachia): Comana (Montandon 1908). - Biology and ecology: monovoltin and monophagous species. It can be found on Lepidium draba (= Cardaria draba) and Lepidium campestre, with its larvae living inside fruits, and the pupa in the soil. The adults of the new generation emerge in September. They diapause in the adult state and become active in May and June next year (Scherf 1964, Freude, Harde & Lohse 1983, Mazur 2002, Knutelski 2005). pecies 7) rare. Plinthus squalidus elekesi (Ormay, 1888) - Romanian endemic sub- Collected matherial: 1 ♂, 16.IV. 2004 – Uioara de Sus pasture (station - Distribution: elekesi (Ormay) ssp. is present only in Romania and is 87 Fig. 3. Percentage of Curculionoidea families according to the number of species in Ocna Mureş area. - Other reports in Romania: Transylvania: Râmetea, Gherla, Sighişoara, Braşov (Petri 1912), Detunata, Sacarâmb (Endrödi 1961), Turda Gorges (Teodor 1993); Banat: Reşiţa and Băile Herculane (Endrödi 1961). - Biology and ecology: there is no data record regarding the biology and ecology of this subspecies until present (Schäfer 1964; Freude, Harde & Lohse 1983). Generally Plinthus squalidus Gyllenhal, 1834 has Pinus sylvestris like host plant (Mazur 2002). Zoogeographic analysis From a zoogeographical point of view, the Curculionoidea fauna from Ocna Mureş has a relative diversity (fig. 4, tab. 1). The predominance of Palearctic spread species (31%) can be observed, followed by the Eurosiberian species (19%) and by the European-western-central Asian species and European species (both with 10 %). The smallest percentage is represented by the species with a central-eastern European distribution, southern-Palearctic distribution and the endemic ones from Romania (all with 1%). 88 Fig. 4. Zoogeographical spectrum of Curculionoidea species from Ocna Mureş area Abbreviations: c-euro = central European species; c, e, euro = central and eastern European species; euro = European species; euras = Eurasian species; eurosib = Eurosiberian species; euro-w-c-as = European, western and central Asian species; hol = Holarctic spread species; n-med = northern Mediterranean species; pal = Palearctic spread species; Ro = Romanian endemic subpecies; s-e c-euro = south-eastern and central European species; w-pal = western Palearctic spread species s-pal = southern Palearctic spread species. Most of the species have a wider distribution on the territory of Romania (tab. 1), only a few have a limited distribution. Thus, Catapion jaffense (Desbr.) is found only in Transylvania, Plinthus squalidus elekesi (Ormay) only in localities from Transylvania and Banat, being a Romanian endemic subspecies, Ceratapion (Echinostroma) scalptum Muls. & Rey is found only in Transylvania and Banat and Adosomus roridus (Pall.) can be found in Transylvania and Moldavia (tab. 1). Data about the ecology of the studied species Species with the highest abundance (tab. 1) in the investigated stations were: 1. In mixed coniferous and deciduous forest (Banţa Hill – Ocna Mureş): Taeniapion urticarium (Hbst.) (60%), Nedyus quadrimaculatus (L.) (13.33%). 89 2. In forest gap (Ocna Mureş): Taeniapion urticarium (Hbst.) (14.81%), Phyllobius (Metaphyllobius) pomaceus (Gyll.) (14.81%), Nedyus quadrimaculatus (L.) (22.312%). 3. In willow riverine forest (Ocna Mureş), Nedyus quadrimaculatus (L.) (31.25%), Sitona (s. str.) cylindricollis (Fabr.) (12.5%), Tanymecus palliatus (Fabr.) (12.5%). 4. In Banţa Hill pasture (Ocna Mureş), Nedyus quadrimaculatus (L.) (11.42%), Pseudoprotapion elegantulum (Germ.) (11.42%), Protapion apricans (Hbst.) (8.57%). 5. In pasture (Uioara de Sus), Larinus (Larinomesius) obtusus Gyll. (34.69%), Hemitrichapion (Dimesomyops) pavidum (Germ.) (6.12%), Sitona (s. str.) hispidulus (Fabr.) (6.12%), Sitona (s. str.) ononidis Sharp (6.12%). 6. In pasture (Uioara de Jos), Nedyus quadrimaculatus (L.) (78%), Parethelcus pollinarius (Forst.) (10.74%). 7. In wet meadow (Ocna Mureş), Sitona (s. str.) puncticollis Steph. (24.39%), Catapion seniculus (Kirby) (17.07%). 8. In ruderal vegetation (Ocna Mureş) Protapion apricans (Hbst.) (14.49%), Sitona (s. str.) puncticollis Steph. (14.49%). Dominant species in the area was Nedyus quadrimaculatus (L.) (40.14%), and codominant species were Taeniapion urticarium (Hbst.) (7.46%) and Parethelcus pollinarius (Forst.) (4.61%). Our reported species have been distributed differently in the research stations (fig. 5), the highest number of species being present in the forest gap (24 species), followed by Banţa Hill pasture (23 species) and wet meadow (22 species), due to the high floristic diversity of these ecosystems. The smallest number of species can be found in mixed coniferous and deciduous forest (6 species). The low number of species from this forest is influenced by the high soil acidity determined by the dominance of the planted scots pine in the place of the native deciduous species. According to Shannon – Wiener ecological diversity index, the greatest biodiversity has been observed in the Banţa Hill pasture (0.671), followed by the willow riverine forest from Ocna Mureş (0.666). The station with the lowest value of biodiversity index was the Uioara de Jos pasture (0.251) (tab. 2, fig. 6 ). There are great differences between the pastures of Ocna Mureş and Uioara de Sus, where the biodiversity of the snout-beetles is higher and the pasture from Uioara de Jos where the biodiversity of the snout-beetles is very low due to intense grazzing. The evenness is also very low in this pasture (0.363). All the other studied ecosystems have the biodiversity and evenness indices high or very high (tab. 2), which proves that the Curculionoidea populations from here are very stable. 90 Fig. 5. Numeric distribution of snout-beatle species by sampling stations: 1-8 (see matherial and methods). Table 2 Shannon-Wiener (H’) ecological diversity index and evenness index (e) Sampling stations: 1. mixed coniferous and deciduous forest, 2. forest gap, 3. willow riverine forest, 4. Banţa Hill pasture (Ocna Mureş), 5. pasture (Uioara de Sus), 6. pasture (Uioara de Jos) 7. wet meadow, 8. ruderal vegetation H’ e 1 0.450 0.65 2 0.537 0.775 3 0.666 0.961 4 0.671 0.968 5 0.602 0.868 6 0.251 0.363 7 0.647 0.933 8 0.521 0.752 The biodiversity and evenness of the mixed coniferous and deciduous forest it is high when compared to the pasture of Uioara de Jos, but it is very low when compared to the other studied ecosystems. Because of the planting of scots pine instead of native trees that have been cut down, the floristical biodiversity of the forest has been depleting, thus leading to a decrease in the biodiversity of the snout-beetles. In the forest gap where no scots pine have been planted, the curculionidae biodiversity and evenness are higher. The gaps resulted from deforestation should be populated with the native wood species. In this way, the forest ecosystems would be restored and in consequence, its specific biodiversity. 91 Fig. 6. Representation of Shannon-Wienner and evenness indices (for sampling stations 1-8 see tab. 2). Conclusions A number of 80 species belonging to 51 genera, 10 subfamilies and 4 families of Curculionoidea have been identified. Out of the total 80 species identified, 79 are at their first report in the investigated area. We have reported the rare species Ceutorhynchus turbatus Schltz. again in the area and also reported the presence of the endemic and rare subspecies Plinthus squalidus elekesi (Ormay). Ecoprotective measures are necessary in the areas where the first and second species have been reported (Banţa Hill– Ocna Mureş, respectively Uioara de Sus pasture). The Palearctic species were predominant, followed by the Eurosiberian, European- western and central Asian, and European ones. The dominant species was Nedyus quadrimaculatus (L.), which also had the greatest abundance in pastures and in willow riverine forests. The species Taeniapion urticarium (Hbst.) and Parethelcus pollinarius (Forst.) were codominant. The highest number of species was present in the forest gap (24 species), followed by the Banţa Hill pasture (23 species) and wet meadow (22 species), and the lowest number of species was found in mixed coniferous and deciduous forest (6 species). The highest curculionidae biodiversity was reported in the Banţa Hill pasture (0.671), followed by Ocna Mureş willow riverine forest (0.666). Uioara de Jos pasture has the lowest biodiversity index value (0.251). The mixed coniferous and deciduous forest has a small number of species (6 species) and its biodiversity index (0.450) and evenness (0.65) quite 92 low due to the presence of scots pine that has been planted here. 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Lucian Alexandru Teodor, Dragomir Cosmin David “Babeş-Bolyai” University, Faculty of Biology and Geology, Department of Taxonomy and Ecology, Str. Clinicilor 5-7, RO-400006, Cluj-Napoca [email protected] [email protected] received: 28.11.2010 accepted: 2.12.2010 printed: 18.12.2010 94