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The following new species are described from the Maghreb: Tapinocyba algirica n. sp. and Walckenaeria heimbergi n. sp. The unknown male of Minicia elegans and the unknown females of Alioranus pauper, Cherserigone graciipes and Entelecara truncatifrons are described. Tmeticus hipponense is transfered to the genus Gongylidiellum and HybocoptliS ericicola is removed from synonymy with H. corrugis and revalidated. The Maghrebian species of the genera Alioranus, Brachycerasphora, Cherserigone, Didectoprocnemis, Entelecara, Eperigone, Erigone, Gnathonarium, Gonatium, Gongylidiellum, Hybocoptus, Lessertia, Maso, Mierargus, Microetenonyx, Minicia, Monocephalus, Nematogmus, Ostearius, Prinerigone, Styloetetor, Tapinocyba, Triehoncoides and Trichoncus are all revised. As a final paper in a series on the Linyphiidae of the Maghreb, all the remaining genera are reviewed. A total of 169 species of Linyphiidae has currently been recorded in the Maghreb.
The former and current distribution of the quokka, Setortix brachyurus, was mapped from published and all available unpublished records. At the time of European settlement the quokka was widespread and abundant and its distribution encompassed an area of approximatelyThe former and current distribution of the quokka, Setortix brachyurus, was mapped from published and all available unpublished records. At the time of European settlement the quokka was widespread and abundant and its distribution encompassed an area of approximately 41 200 km2 of south-west Western Australia inclusive of two offshore islands, Bald Island and Rottnest Island. Historical reports indicated an extensive population decline occurred in the 1930s. The decline continued, with a previously undocumented decline apparent in the period from 1980 to 1992. However, this decline may be an artefact of the time scales used for mapping and may well equate with a previously reported decline lor a suite of south -west mammals in the 1970s. By 1992 the quokka´s distribution had been reduced to an area of approximately 17800 km2. An increased awareness of the presence of the quokka on the mainland has resulted in numerous reportings of quokka presence since 1992, has confimled the existence of several populations at the northern extent of the quokka´´s known geographic range and indicated the cmrent, 2005, distribution to be similar to that in 1992. However, survey and population estimates at six of these mainland locations from the northem jarrah forest indicated low abundance. There have been no population estimates elsewhere on the mainland. Two populations have been reported tiom the Swan Coastal Plain, but neither has been confirmed extant. Predation by the introduced fox, Vulpes vulpes, is implicated as a major cause of the quokka´s initial decline, while ongoing predation, habitat destruction and modification through altered tire regimes have contributed to the continued decline. Specific conservation management actions are recommended, namely: (i) Implementing an active adaptive management program in the northern jarrah forest to determine quokka population response to habitat manipulation through the use of fIre, fox baiting and pig control; (ii) Surveying the Stirling fumge and Green Range populations with emphasis placed on determining population size and population genetic structure; (iii) Surveying the reported occurrences from the Swan Coastal Plain, with emphasis on unambiguously determining presence. If confirmed, priority should he directed to assessing population size and determining the management requirements to ensure persistence of the population; (iv) Surveying southem forest and south coast populations to assess quokka population size, the extent of movement between sllbpopulations and assessment of the range of habitat types used by quokkas. The latter should be combined with spatial analyses of known extant populations and suitable and potentially suitable habitat; (v) Determining the role of tire in establishing and maintaining preferred habitat of southern forest and south coast populations; and (vi) Establishing a program to assess the potential effects from management operations.
Techniques for collecting, handling, preparing, storing and examining small molluscan specimens
(2007)
Micromolluscs are small-sized molluscs (< 5 mm), and include the great majority of undescribed molluscan taxa. Such species require special collecting, sorting and handling techniques and different storage requirements to those routinely used for larger specimens. Similarly, the preparation of shells, opercula, radulae and animals poses some challenges for scanning electron microscopy (SEM). An overview of experiences with various techniques is presented, both positive and negative. Issues discussed include those relating to storage of dry specimens and interaction of specimens with glass, gelatine and paper products, handling techniques and storage in various fluids. Techniques for cleaning shells for SEM are described and compared, as well as those for radular extraction. The interactions of chemicals used for the dissolution of tissue with calcareous micromolluscs are described. Methods for handling and mounting small radulae for SEM are detailed and brief guides to SEM and light photography are given. An appendix listing details of frequently-used chemicals is provided.
The taxonomy, diversity, and distribution of the aquatic insect order Trichoptera, caddisflies, are reviewed. The order is among the most important and diverse of all aquatic taxa. Larvae are vital participants in aquatic food webs and their presence and relative abundance are used in the biological assessment and monitoring of water quality. The species described by Linnaeus are listed. The morphology of all life history stages (adults, larvae, and pupae) is diagnosed and major features of the anatomy are illustrated. Major components of life history and biology are summarized. A discussion of phylogenetic studies within the order is presented, including higher classification of the suborders and superfamilies, based on recent literature. Synopses of each of 45 families are presented, including the taxonomic history of the family, a list of all known genera in each family, their general distribution and relative species diversity, and a short overview of family-level biological features. The order contains 600 genera, and approximately 13,000 species.
Presented herein is the first morphological analysis of turtle relationships to examine the monophyly of many turtle groups by using only single species as terminals and by integrating a large number of primitive fossil taxa. The data matrix consists of 136 osteological parsimony informative characters with 169 derived character states for 45 fossil and 22 living species of the clade TESTUDINATA. The results corroborate the monophyly of a large number of previously hypothesized clades, but refute the accepted hypothesis regarding the basal split of living turtles. In particular, the primitive turdes Proterochersis robusta, Kayentachelys aprix, Mongolochelys efremovi, Meiolania platyceps, and Kallokibotion bajazidi are removed from their current position as crown turtles and placed along the phylogenetic stem of this clade. The age of the turtle crown is thereby adjusted from the Late Triassic to the Late Jurassic, which is relevant to testing molecular clock hypotheses. This revised topology has important implications for the evolution of several character complexes, because it implies that the common ancestor of all living turtles must have had a partially braced brain case and a primitive trochlear mechanism. Other noteworthy conclusions include the tentative exclusion of protostegids from CHELONIOIDEA, the placement of Platysternon megacephalum outside of CHELYDRIDAE, and the tentative interpretation of Sandownia harrisi as a basal eucryptodire.
Schlüssel zur Bestiminung europäischer Boletales mit Röhren werden vorgestellt. Der Artenschlüssel ist großteils nir Bestimmung von Frischmaterial angelegt. Die Schlüssel zu den Familien und Gattungen sowie die Gattungsdiagnosen sind auf Europa bezogen und müßten in weltweiter Sicht noch erweitert werden. Im Schlüssel wurden einige in den letzten Jahren vorgcnoinmenen Neukombinationen und Synonymisierungen nicht übernommen. Für die nunmehr in Xerocomus integrierte Gattung Phylloporus wird die Schaffung einer Untergattung vorgeschlagen. Auch eine neue Sektion, eine neue Art und einige neue Kombinationen werden vorgeschlagen.
Lepidoptera phylogeny and systematics : the state of inventorying moth and butterfly diversity
(2007)
The currently recognized robust support for the monophyly of the Lepidoptera (and the superorder Amphiesmenoptera comprising Lepidoptera + Trichoptera) is outlined, and the phylogeny of the principal lineages within the order is reviewed succinctly. The state of the taxonomic inventory of Lepidoptera is discussed separately for ‘micro-moths’, ‘macro-moths’ and butterflies, three assemblages on which work has followed historically somewhat different paths. While currently there are about 160,000 described species of Lepidoptera, the total number of extant species is estimated to be around half a million. On average, just over one thousand new species of Lepidoptera have been described annually in recent years. Allowing for the new synonyms simultaneously established, the net increase in species numbers still exceeds 800/year. Most of the additions are foreseeable in the micro-moth grade, but even for butterflies ca 100 species are added annually. Examples of particularly interesting new high-rank taxa that have been described (or whose significance has become realized) since the middle of the 20th century include the non-glossatan lineages represented by Agathiphaga and Heterobathmia and the heteroneuran families Andesianidae, Palaephatidae, Hedylidae and Micronoctuidae. Some thoughts on how present and future systematic lepidopterology might be prioritised are presented.
Glyptostrobus Endlicher is well represented in early Early Cretaceous to Pleistocene deposits in the middle to high latitudes of North America and Eurasia. Although the taxonomy and nomenclature of the genus is complicated, the fossil record indicates Glyptostrobus was represented by a small number of species. The genus first appears in Aptian age deposits from western Canada and Greenland, and achieved a wide distribution early in its evolutionary history. Exchange of Glyptostrobus between Asia and North America occurred across the Spitsbergen and Beringian corridors, which were functional about 110 and 100 million years ago, respectively The Late Cretaceous fossil record of Glyptostrobus shows that the genus had spread into Russia, China and the shores of the Turgai Strait. By the early Tertiary, Glyptostrobus was a prominent constituent of the polar broad-leaved deciduous forests. Paleocene age deposits across western Canada and the United States indicate the genus was present in great abundance in the lowland warm temperate and subtropical forests east of the Rocky Mountains. The broad distribution in North America and Russia during the Paleocene and Eocene indicates that Glyptostrobus grew and reproduced under a diverse range of climatic and environmental conditions, including the cold and unique lighting conditions of the polar latitudes. The presence of Glyptostrobus in Europe indicates the North Atlantic land bridges that extended between North America and Eurasia (Fennoscandia) and Europe during the early Tertiary were used. In Europe, extensive Glyptostrobus dominated swan1ps occupied the Central European Depression during the late Tertiary. Increasing global aridity and cooling, as well as landscape stabilization together with increasing competition for resources and habitat by representatives of the Pinaceae, seem to have forced the genus out of North America, Europe and most of Asia during the Miocene and Pliocene. In Japan, Glyptostrobus persisted until the early Pleistocene. After the early Pleistocene extinction in Japan, Glyptostrobus reappeared in southeastern China. Details of the taxonomic and biogeographic history of Glyptostrobus are examined.
High-performance liquid chromatography (HPLC) has proved extremely versatile over the past 25 yr for the isolation and punfication of peptides varying widely in their sources, quantity and complexity. This article covers the major modes of HPLC utilized for peptides (size-exclusion, ion-exchange, and reversed-phase), as well as demonstrating the potential of a novel mixed-mode hydrophilic interaction/cation-exchange approach developed in this laboratory. In addition to the value of these HPLC modes for peptide separations, the value of various HPLC techniques for structural characterization of peptides and proteins will be addressed, e.g., assessment of oligomerization state of peptideslproteins by sizeexclusion chromatography and monitoring the hydrophilicitykydrophobicity of amphipathic cr-helical peptides, a vital precursor Tor the development of novel antimicrobial peptides. The value of capillary electrophoresis for peptide separations is also demonstrated. Preparative reversed-phase chromatography purification protocols for sample loads of up to 200 mg on analytical columns and instrumentation are introduced for both peptides and recombinant proteins. Key Words: Peptides; proteins; size-exclusion chromatography (SEC); anion-exchange chromatography (AEX); cation-exchange chromatography (CEX); mixed-mode hydrophilic interaction chromatography (HIL1C)/cation-exchange chromatography (CEX); reversed-phase high-performance liquid chromatography (RP-HPLC); preparative RP-HPLC of peptides and proteins; amino acid side-chain hydrophilicitylhydrophobicity coefficients; amino acid U-helical propensity values; amino acid side-chain stability coefficients
A systematic revision of the genus Dichaeu (Orchidaceae) in Costa Rica is presented. The taxonomic history of the genus and its phylogenetic position are discussed, with emphasis on infragenenc grouping. Characters of vegetative and floral morphology are treated, and their taxonoiilic significance is discussed. Twenty-nine Dichnea taxa are recognized for the flora of Costa Rica, and a key to species is provided. Each taxon is described on the basis of Costa Rican material, illustrated in a composite plate, and its distribution in the country is assessed. Distribution maps for all the taxa are given. Overall distribution, derivation of name, notes on species ecology, and diagnostic features are presented for each taxon. Lectotypes are selectcd for D. acostae Schltr., D. acroblephara Schltr., D. amparoana Schltr., D. costaricensis Schltr., D. dammeriana Kraenzl., D. lycopodioides Rchb. f. ex Kraenzl., D. poicillantha Schltr., D. selaginella Schltr., D. tuercklheimii Schltr., Epidendrum echinocarpon Sw., and E. trichocarpon Sw. A new species, D. gomez-lauritoi, is described and illustrated from the wet Caribbean plains of central Costa Rica.
Die 4. Fassung der Roten Liste der Brutvögel Deutschlands wurde durch das "Nationale Gremium Rote Liste Vögel" erarbeitet, in dem die wissenschaftlichen Institutionen der Ornithologie und Avifaunistik in Deutschland vertreten sind. Die Rote Liste ersetzt die 3. Fassung aus dem Jahr 2002 (BAUER et al. 2002); sie wurde erstmalig nach dem für alle Tier- und Pflanzenartengruppen sowie den Pilzen in Deutschland entwickelten Kriterienschema (5. LUDWIG et al. 2007) erarbeitet. Somit wird ein direkter Vergleich der Gefährdungssituation zwischen diesen Gruppen ermöglicht. Bestandsgröße, kurzfristiger (25 Jahre) und langfristiger (50-150 Jahre) Bestandstrend sind die wichtigsten Parameter zur Gefahrdungseinstufung der einzelnen Arten. Zusätzlich wurde jeweils die Wirksamkeit von Risikofaktoren artspezifisch identifiziert und berücksichtigt. Alle Einstufungen werden transparent vorgenommen und in der Anhangsliste publiziert. Der Dachverband Deutscher Avifaunisten (DDA) hat zur Erstellung der Datengrundlagen mit Stand 2005 für die Gefahrdungseinstufung ein neues Abfrageschema entwickelt, in dem die relevanten Informationen aus den nationalen Vogelmonitoring-Programmen aufgearbeitet und als Hintergrunddaten für die Einschätzungen von Bestandstrend und -größe auf Landesebene bereitgestellt wurden. Dadurch gewinnen die Einstufungen an Verlässlichkeit und Nachvollziehbarkeit. Der langfristige Trend wurde vom "Nationalen Gremium Rote Liste Vogel" ermittelt. Vor der Einstufung der Brutvogelarten wurde je Art eine Statuszuordnung vorgenommen, von denen nur die regelmäßig brütenden einheimischen Arten den weiteren Weg der Rote Liste-Erstellung durchlaufen. In der Roten Liste 2007 werden insgesamt 260 regelmäßige einheimische Brutvogelarten in Deutschland berücksichtigt, 25 weitere Arten brüteten nur unregelmäßig ('vermehrungsgäste': Status II), zudem wurden 29 Neozoen-Arten ermittelt (Status III), von denen 20 regelmäßig brüten. Dies ergibt zusammen 314 Arten, die höchste Zahl an Brutvogelarten, die je für eine Rote Liste zu Grunde gelegt wurde. Insgesamt befinden sich 110 regelmäßige Brutvogelarten in den Kategorien der Roten Liste 2007 (0 = ausgestorben, 1 = vom Aussterben bedroht, 2 :: stark gefährdet, 3 :: gefährdet und R = extrem selten), das entspricht 42,3 % der Arten, was einer minimal geringeren Gefahrdungsquote gegenüber der Vorgängerliste entspricht. Erfreulich ist, dass mit dem Bruchwasserläufer und dem Steinrötel zwei ehemals in Deutschland ausgestorbene Arten zwischen 2000 und 2005 wieder regelmäßig gebrütet haben. Dem entgegen ist mit der Blauracke eine weitere Art ausgestorben. Schwarzstorch, Wanderfalke, Seeadler und Uhu sind hier erstmals seit der ersten deutschen Roten Liste 1971 nicht mehr aufgeführt - ein Erfolg jahrzehntelanger direkter Schutzmaßnahmen der ehrenamtlichen und amtlichen Vogelschützer und gleichzeitig ein Beweis, dass sich Vogelschutz bei stark gefährdeten Arten lohnen kann. Andererseits sind mit Schreiadler, Zwergseeschwalbe oder Großem Brachvogel Alien in die höchste Gefährdungskategorie eingestuft worden, die zwar auch im Fokus des Vogelschutzes standen und stehen, bei denen aber bislang Maßnahmen nicht ausreichend erfolgreich umgesetzt werden konnten. Gerade die Kategorie "vom Aussterben bedroht" umfasst mit nunmehr 30 Arten den höchsten Wert seit Erscheinen der gesamtdeutschen Roten Liste. Der Analyse der aktuellen deutschen Brutvogelfauna zufolge sind die Boden brütenden Vogelarten, Großinsektenfresser und Langstreckenzieher am stärksten von Gefährdungen betroffen. Vogelgruppen mit einem hohen Anteil gefährdeter Arten sind demzufolge Hühnervögel, Rallen, Limikolen und Würger, während Eulen und Schnäpperverwandte derzeit vergleichsweise wenig gefährdet sind. Zudem erfolgt deutschlandweit ein weiteres Ausdünnen der typischen Vögel in der Normallandschaft, was sich vor allem in den Trendanalysen manifestiert, aber in der Roten Liste noch nicht sehr stark zum Ausdruck kommt. Die Nutzungsintensivierungen von Land- und Forstwirtschaft in jüngster Zeit geben hier großen Anlass zur Sorge in diesen Großlebensräumen. Diese Rote Liste stellt erneut ein kritisches Zeugnis über den Zustand der deutschen Vogelwelt aus. Aufgrund der in jüngster Zeit stark ausgeweiteten Monitoringprogramme wird es in Deutschland zukünftig noch besser möglich sein, die Gefahrdung aufzuzeigen. Um den dauerhaften Rückgang der Vogelbestände zu stoppen oder wenigstens zu verlangsamen, müssen die wirksamen Gefahrdungsfaktoren reduziert und minimiert werden. Dem gezielten Vogelartenschutz stellen sich dabei folgende vordringliche Aufgaben: Erhaltung der offenen Kulturlandschaft, Erhaltung strukturreicher Walder, Erhaltung nährstoffarmer Lebensräume, Sicherung der Schutzgebiete - insbesondere Natura 2000, Stärkung der internationalen Zusammenarbeit im Vogelschutz, Reduktion der Populationsverluste durch Unfälle und menschliche Verfolgung sowie Förderung des vogelkundlichen Nachwuchses.
The impact of naval sonar on beaked whales is of increasing concern. In recent years the presence of gas and fat embolism consistent with decompression sickness (DCS) has been reported through postmortem analyses on beaked whales that stranded in connection with naval sonar exercises. In the present study, we use basic principles of diving physiology to model nitrogen tension and bubble growth in several tissue compartments during normal div ng behavior and for several hypothetical dive profiles to assess the risk of DCS. Assuming that normal diving does not cause nitrogen tensions in excess of those shown to be safe for odontocetes, the modeling indicates that repetitive shallow dives, perhaps as a consequence of an extended avoidance reaction to sonar sound, can indeed pose a risk for DCS and that this risk should increase with the duration of the response. If the model is correct, then limiting the duration of sonar exposure to minimize the duration of any avoidance reaction therefore has the potential to reduce the risk of DCS.