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Raptors in the East African Tropics and Western Indian Ocean Islands: State of Ecological Knowledge and Conservation Status
j. RaptorRes. 32(1):28-39 ¸ 1998 The Raptor ResearchFoundation, Inc. RAPTORS IN THE EAST AFRICAN TROPICS AND WESTERN INDIAN OCEAN ISLANDS: STATE OF ECOLOGICAL KNOWLEDGE AND CONSERVATION STATUS MUNIR VIRANI 1 AND RICHARD T. WATSON ThePeregrine Fund, Inc., 566 WestFlying Hawk Lane, Boise,1D 83709 U.S.A. ABSTRACT.--Fromour reviewof articlespublished on diurnal and nocturnal birds of prey occurringin Africa and the western Indian Ocean islands,we found most of the information on their breeding biology comesfrom subtropicalsouthern Africa. The number of published papers from the eastAfrican tropics declined after 1980 while those from subtropicalsouthern Africa increased.Based on our KnoM- edge Rating Scale (KRS), only 6.3% of breeding raptorsin the eastAfrican tropicsand 13.6% of the raptorsof the Indian Ocean islandscan be consideredWell Known,while the majority,60.8% in main- land east Africa and 72.7% in the Indian Ocean islands, are rated Unknown. Human-caused habitat alteration resultingfrom overgrazingby livestockand impactsof cultivationare the main threatsfacing raptors in the east African tropics, while clearing of foreststhrough slash-and-burnmethods is most important in the Indian Ocean islands.We describeconservation recommendations, list priorityspecies for study,and list areasof ecologicalunderstanding that need to be improved. I•y WORDS: Conservation;east Africa; ecology; western Indian Ocean;islands; priorities; raptors; research. Aves rapacesen los tropicos del este de Africa yen islasal oeste del Oc•ano Indico: estado del cono- cimiento eco16gicoy de su conservacitn RESUMEN.--Denuestra recopilacitn de articulospublicados sobre aves rapaces diurnas y nocturnasque se encuentran en Africa yen las islasal oeste del Octano Indico, encontramosque la mayoriade la informaci6n sobre aves rapacesresidentes se origina en la regi6n subtropical del sur de Africa. -
Annex a Species Are the Most Endangered, and Most Protected Species and Trade Is Very Strictly Controlled
Raptor Rescue Rehabilitation Handbook APPENDIX B What do the various CITES Annex listings mean? The annex is the critical listing which defines what you can or cannot do with a specimen. Annex A species are the most endangered, and most protected species and trade is very strictly controlled. Unless the specimen is covered by a certificate from the UK CITES Management Authority you cannot legally use it for any commercial purpose, whether or not direct payment is involved. This includes offer to buy, buy, keep for sale, offer for sale, transport for sale, sell, advertise for sale, exchange for anything else, or display to paying customers. To import or (re)export such a specimen into or out of the EU requires both an import permit and an (re)export permit. You will therefore need to contact the management authorities in the countries of export and import, prior to such a move. Annex B species can be traded within the EU providing you can prove “legal acquisition” i.e. the specimen has not been taken from the wild illegally or smuggled into the EU. Annex B specimens which are imported into or (re)exported from the EU require the same documentation as for Annex A specimens (see above) Annex C and D species require an ‘Import Notification’ form to be completed at the time you make your import. To obtain a copy of the form ring 0117 372 8774 The following species are listed on Annex A. Falconiformes Andean Condor Vultur gryphus California Condor Gymnogyps califorianus Osprey Pandion haliaetus Cinereous Vulture Aegypius monachus Egyptian Vulture -
Ultimate Seychelles Bird List February 2020 | Compiled by Pepper Trail
Ultimate Seychelles Bird List February 2020 | Compiled by Pepper Trail 17 18 19 20 21 22 23 24 25 26 27 27 28 At Sea Assumption Aldabra Aldabra Cosmoledo Astove At Sea Alphonse Poivre Desroches Praslin La Digue Mahe Galliforms Gray Francolin Pigeons and Doves Rock Pigeon X European Turtle-Dove X Madagascar Turtle-Dove x X X X X X Zebra Dove X X X X X Comoro Blue-Pigeon x X X Seychelles Blue-Pigeon x X X X Cuckoos Madagascar Coucal x X Nightjars Madagascar Nightjar Swifts Seychelles Swiftlet x X Rails, Gallinules & Allies White-throated Rail x X ? Eurasian Moorhen Plovers Black-bellied Plover x X X X X Pacific Golden-Plover Ultimate Seychelles Bird List February 2020 | Compiled by Pepper Trail 17 18 19 20 21 22 23 24 25 26 27 27 28 At Sea Assumption Aldabra Aldabra Cosmoledo Astove At Sea Alphonse Poivre Desroches Praslin La Digue Mahe Lesser Sand-Plover x X Greater Sand-Plover x X X Common Ringed Plover Sandpipers Whimbrel x X X X X X X Eurasian Curlew Bar-tailed Godwit Ruddy Turnstone x X X X X X Curlew Sandpiper x X X Sanderling x X X Little Stint Terek Sandpiper Common Sandpiper x X Common Greenshank x X X X Wood Sandpiper Crab-Plover x X X X X X Gulls and Terns Brown Noddy x X X X X X X X X Lesser Noddy x X White Tern x X X X X X X X X Sooty Tern Bridled Tern x X X X Saunders’s Tern White-winged Tern Roseate Tern Ultimate Seychelles Bird List February 2020 | Compiled by Pepper Trail 17 18 19 20 21 22 23 24 25 26 27 27 28 At Sea Assumption Aldabra Aldabra Cosmoledo Astove At Sea Alphonse Poivre Desroches Praslin La Digue Mahe Black-naped -
Assessment of the Genetic Potential of the Peregrine Falcon (Falco Peregrinus Peregrinus) Population Used in the Reintroduction Program in Poland
G C A T T A C G G C A T genes Article Assessment of the Genetic Potential of the Peregrine Falcon (Falco peregrinus peregrinus) Population Used in the Reintroduction Program in Poland Karol O. Puchała 1,* , Zuzanna Nowak-Zyczy˙ ´nska 1, Sławomir Sielicki 2 and Wanda Olech 1 1 Department of Animal Genetics and Conservation, Warsaw University of Life Sciences, 02-787 Warszawa, Poland; [email protected] (Z.N.-Z.);˙ [email protected] (W.O.) 2 Society for Wild Animals “Falcon”, 87-800 Włocławek, Poland; [email protected] * Correspondence: [email protected] Abstract: Microsatellite DNA analysis is a powerful tool for assessing population genetics. The main aim of this study was to assess the genetic potential of the peregrine falcon population covered by the restitution program. We characterized individuals from breeders that set their birds for release into the wild and birds that have been reintroduced in previous years. This was done using a well-known microsatellite panel designed for the peregrine falcon containing 10 markers. We calculated the genetic distance between individuals and populations using the UPGMA (unweighted pair group method with arithmetic mean) method and then performed a Principal Coordinates Analysis (PCoA) and constructed phylogenetic trees, to visualize the results. In addition, we used the Bayesian clustering method, assuming 1–15 hypothetical populations, to find the model that best fit the data. Citation: Puchała, K.O.; Units were segregated into groups regardless of the country of origin, and the number of alleles ˙ Nowak-Zyczy´nska,Z.; Sielicki, S.; and observed heterozygosity were different in different breeding groups. -
Phelsuma 19.Indd
Development on Silhouette Harbour construction Since the 19th century access to most of Silhouette was via the narrow pass through the reef at La Passe and the settlement’s jetty (Fig. 16a). In 2000 the pass was widened and deepened, and a harbour excavated (Fig. 16b). The impacts on the natural environment were considerable in the short term, resulting in the death of thousands of reef-flat animals (most obviously molluscs, brittle stars and sea cucumbers – Fig. 17). In 2005 the channel was cleared from coral regrowth by blasting, this caused some fish mortality at the time (Fig. 17). Fig. 16 La Passe sea access. a) La Passe in 1960 b) in 2006 c) view of harbour in 2006 96 The harbour improved access to the island, enabling larger vessels to reach the shore. This also increased vulnerability of the island to new human impacts. In September 2005 an oil spill occurred in the harbour when a boat carrying waste oil from North Island to Mahé developed a leak and made an emergency stop in the Silhouette harbour (Gerlach 2005). The vessel was beached on Silhouette on 7th September and patched. It was refloated on 10th September but the repairs were not successful. It sank in the harbour in the night of 11th September. Oil was observed leaking from the wreck (Fig. 18), although this was reported to IDC and the vessel’s owners no action was taken. The Ministry of Environment sent a clean-up team but this did not arrive until after the floating oil had been flushed out of the harbour by a falling tide. -
American Kestrel
Department of Planning and Natural Resources Division of Fish and Wildlife U.S.V.I. Animal Fact Sheet #05 American Kestrel Falco sparverius Taxonomy Kingdom - - - - - Animalia Phylum - - - Chordata Subphylum - - - Vertebrata Class - - - - Aves Subclass - - - Neornithes Order - - - Falconiformes Family - - Falconidae Genus - - Falco Species - sparverius Subspecies (Caribbean) - caribbaearum Identification Characteristics ♦ Length - 19 to 21 cm ♦ Wingspan - 50 to 60 cm ♦ Weight (males) - 102 to 120 gm ♦ Weight (females) - 126 to 166 gm ♦ Facial bars - two ♦ Color of tail & back - rusty reddish ♦ Tail pattern - black band at tip Description wings are rusty brown like their back and their tail The American kestrel, Falco sparverius, is a is rusty reddish with a black band at the end. common falcon in the Virgin Islands. Although frequently called a "sparrow” hawk - in reference Distribution & Habitat to its small size - these kestrels eat more than The American Kestrel permanently inhabits sparrows. Locally, the American Kestrel is also (without seasonal migration) North and South known as the killy-killy, probably because of the America from near the tree line in Alaska and shrieking sounds they make. Canada, south to Tierra del Fuego. The bird can The American Kestrel is the smallest raptor in also be found in the West Indies, the Juan our area. Worldwide, the only smaller species in Fernandez Islands and Chile. It is largely absent the genus Falco is the Seychelles kestrel. from heavily forested areas, including Amazonia. Generally, the American Kestrel is about 20 cm The American Kestrel nests in tree cavities, long, with a wingspan of 50 to 60 cm. Males woodpecker holes, crevices of buildings, holes in weigh from 103 to 120 g and females between 126 banks, nest boxes or, rarely, old nests of other and 166 g. -
Supplementary Table 1. List of Demonstrated Beneficiaries
Supplementary Table 1. List of demonstrated beneficiaries. IUCN Red List Island Country Common Scientific Animal status Event Citation Petroica New australis Adele Zealand South Island robin australis Landbird LC reintroduction (1) Branta United Aleutian cackling hutchinsii Agattu States goose leucopareia Landbird LC reintroduction (2) United Evermann's rock Lagopus muta Agattu States ptarmigan evermanni Landbird LC reintroduction (2) United unassisted Ailsa Craig Kingdom Black guillemot Cepphus grylle Seabird LC colonization (3) United Fratercula unassisted Ailsa Craig Kingdom Atlantic puffin arctica Seabird LC recolonization (4) United Oenanthe unassisted Ailsa Craig Kingdom Northern wheatear oenanthe Landbird LC colonization (4) United Tadorna unassisted Ailsa Craig Kingdom Common shelduck tadorna Landbird LC colonization (3) Philesturnus New South Island carunculatus Allports Zealand saddleback carunculatus Landbird NT reintroduction (2) Bettongia Alpha Australia Burrowing bettong lesueur Mammal NT introduction (5) Branta (6; Steve Amchitka United Aleutian cackling hutchinsii unassisted Ebbert, pers. Island States goose leucopareia Landbird LC recolonization comm.) Amukta United Aleutian cackling Branta Landbird LC unassisted (7) IUCN Red List Island Country Common Scientific Animal status Event Citation States goose hutchinsii recolonization leucopareia Sally Amy Poncet, Island/Outer United Cinclodes unassisted unpublished Knob Kingdom Tussacbird antarcticus Landbird LC recolonization data Sally Amy Poncet, Island/Outer United unpublished -
Breeding Biology and Food Habits of the Madagascar Kestrel (Falco Newtoni) in Northeastern Madagascar
j. RaptorRes. 39(2):149-155 ¸ 2005 The Raptor ResearchFoundation, Inc. BREEDING BIOLOGY AND FOOD HABITS OF THE MADAGASCAR KESTREL (FALCO NEWTONI) IN NORTHEASTERN MADAGASCAR LILY-ARISONRENE DE ROLAND,JEANNENEY RABEARIVONY, HARILALAINAROBENARIMANGASON, AND GILBERTRAZAFIMANJATO ThePeregrine Fund's Project in Madagascar,B.P 4113, Antananarivo(101), Madagascar RUSSELL THORSTROM 1 ThePeregrine Fund, 5668 WestFlying Hawk Lane, Boise,ID 83709 U.S.A. ABSTRACT.--Westudied MadagascarKestrels (Falconewtoni) on Masoala Peninsula, northeastern Mada- gascarduring the 1997 and 1998breeding seasons. We locatedfive nestsites and observedeight nesting attemptsduring the two breeding seasons.All nestswere in tree cavitiesand averaged13.8 + 2.0 m (SE) above the ground in trees averaging22.8 +- 0.8 m (SE) in height (N = 5 nests). Egg laying took place from mid-Septemberto the first week of October.The modal clutch sizewas 4 + 0.9 (N = 6 nests, range 3-5 eggs).The incubationperiod averaged28 d, varying from 27-29 d (N = 5 nests).Hatching occurred from the middle of October to the first week of November with young fledging in late No- vember.Of 24 eggslaid in six nests,13 (54%) hatched,and seven(54%) of thosehatchlings fledged; thus, a total of 1.2 young fledged per breeding attempt were produced and overall nest successwas 50%. The MadagascarKestrel diet of 338 identifiedprey wascomposed of 93.8% lizards(N = 317), 2.6% insects(N = 9), 2.4% amphibians(N = 8), and 1.2% birds (N = 4). KEYWORDS: MadagascarKestrel; Falco newtoni; nestingbiology; food habits;nests; -
Assessing Conservation Value of Islands in the Central Seychelles
ASSESSING CONSERVATION VALUE OF ISLANDS IN THE CENTRAL SEYCHELLES ABSTRACT Data gathered in the island assessment process are used to prioritise the islands visited (and, by extrapolation, other islands in the central Seychelles) for conservation value, particularly in regard to conservation of endemic land birds. Several criteria of particular importance for endemic bird conservation are identified, and these could be used in more rapid assessment of other islands in the area for conservation. INTRODUCTION Several authors have attempted to formalise criteria to evaluate land for conservation purposes in order that the most appropriate sites can be selected for protection (see, for example, Smith and Theberge, 1986; Usher, 1986). There is no simple consensus that can be applied in all situations although a number of biological and physical indicators that are commonly cited include the presence of rare species of animals and plants, or rare habitats, diversity (of species or habitats), size, "representativeness" or "naturalness", and the relative fragility of an arez or habitat (Bibby, 1998). In addition, social, cultural and management practicalities need to be considered, especially where an area has multiple use (such as scientific research or recreation in addition to conservation). While many criteria emphasise existing conservation values, the concept of "potential value" (Ratcliffe, 1977) or, in this case, "rehabilitation value", is particularly important for the islands of the granitic Seychelles. The original habitats of all islands have been profoundly altered in the past 200 years. Active human intervention is likely to be necessary to realise the conservation value of any of the small or medium-sized islands. -
Management of Raptors 935
40_Raptorsnew.qxd 8/24/2005 12:04 PM Page 935 Chapter 40 | MANAGEMENT OF RAPTORS 935 frequently reported conditions. For a comprehensive review of bacterial diseases in raptors, the reader is referred to a recent publication on this subject.9 Tuberculosis is a bacterial disease produced by Myco- bacterium avium avium. This condition is considered rare in North American raptors65 but is frequently found in the United Kingdom and continental Europe.9,29 The disease is characterized by the presence of tubercles pri- marily in the liver, spleen, gastrointestinal tract and bones. Subcutaneous tubercles also have been described in raptors.9,29 Diagnosis with the tuberculin test is unre- warding.29 The use of radiology in bone-related infec- tions has proved useful.65 For a more accurate diagnosis, Fig 40.53 | Pseudomonas aeruginosa stomatitis as a sequel to a recent trichomoniasis infection. Note the characteristic multi- suspected birds should be subjected to endoscopic ple caseous masses present in the caudal and lateral aspects of examination and subsequent liver biopsy and histo- the oropharynx and on the tongue. In most cases, the tongue is pathology analysis. Treatment of tuberculosis is not rec- grossly enlarged, preventing birds from eating normally. ommended in raptors, particularly when the birds are in close contact with humans; but if treatment is deemed general depression. In acute cases, clinical signs include appropriate, a number of therapeutic agents have been general depression, reduced appetite, regurgitation, soft proposed.7 The treatment protocol should run parallel brown feces progressing rapidly to reddish and hemor- to an adequate biosecurity program targeted at contain- rhagic, pastel green-colored urates and recumbency.29 ing the disease (see Chapter 28, Implications of Suggested treatments for the acute form include the use Mycobacteria in Clinical Disorders). -
Eradication of Invasive Animals and Other Island Restoration Practices in Seychelles: Achievements, Challenges and Scaling up Perspectives
G. Rocamora Rocamora, G. Eradication of invasive animals and other island restoration practices in Seychelles: achievements, challenges and scaling up perspectives Eradication of invasive animals and other island restoration practices in Seychelles: achievements, challenges and scaling up perspectives G. Rocamora Scientifi c Director & Chair, Island Biodiversity & Conservation Centre, University of Seychelles, Anse Royale Campus, Box 1348, Victoria, Seychelles. <[email protected]>. Abstract In recent decades Seychelles has accumulated extensive experience in the management of invasive species and other island restoration practices. Non-government organisations (NGOs), governmental, parastatal and private stakeholders have conducted successful programmes to control and eradicate invasive animals and plants, particularly on small islands of high biodiversity value. Biosecurity protocols have been implemented to prevent (re)infestations. With at least 50 vertebrate populations (33 mammal, 16 bird and one reptile) from 14 diff erent species successfully eradicated, Seychelles is the third country in the world after Australia and the USA for invasive vertebrate eradications from tropical islands, and the seventh when considering all countries. Twenty-four islands have benefi ted from invasive vertebrate eradications and other ecosystem restoration processes to create refuges for native biodiversity. About 470 ha of woodland have been rehabilitated through replanting and recovery of native vegetation, and at least 36 successful island translocations of native birds and reptiles have been conducted. This includes 16 conservation introductions or reintroductions of six endemic land birds (all but one threatened), two of a terrapin species and 18 of Aldabra giant tortoises. Recovery of native species and natural recolonisations have occurred on islands where invasive predators have been removed. -
CEPF Impact Report
CEPF | 2019 IMPACT REPORT 2000 to CEPF empowers nongovernmental organizations, indigenous groups, 30 June 2019 universities and private enterprises to protect the world’s biodiversity hotspots and help communities thrive. We do this through grants for conservation, organizational strengthening and sustainable development. 24 hotspot strategies implemented CEPF’S APPROACH • Donor partnership: CEPF is a joint initiative of l’Agence Française de Dével- oppement, Conservation International, the European Union, the Global 2,408 Environment Facility, the Government of Japan and the World Bank. grantees supported • Focused investment: On the basis of an assessment of opportunities and threats, CEPF donor partners choose which biodiversity hotspots to invest in as funding becomes available. US$242 million in grants • Participatory priority-setting: Grant making is guided by ecosystem committed profiles—analyses of the biodiversity and socio-economic conditions in each hotspot that are produced by, and in consultation with, local stakeholders. The result is a regional conservation strategy tailored to the most urgent needs, using practical solutions. US$376 million leveraged by • Local management: CEPF partners with a regional implementation team in those grants each biodiversity hotspot to help shepherd the investment and build local conservation leadership. • Grants to civil society: Civil society entities—including nongovernmental 98 organizations, communities, indigenous peoples groups, universities and countries and territories benefited small businesses—apply for grants that are awarded on a competitive basis for projects that contribute to CEPF’s conservation strategy. • Enduring conservation: Projects funded by CEPF add up to a portfolio of 15.3 complementary conservation actions addressing critical priorities while million hectares of also building local conservation communities that will continue to lead protected areas created protection of the hotspots after CEPF funding is completed.