SPOTTERS GUIDE Boulders (8 - 20 Meters) Aquarium

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SPOTTERS GUIDE Boulders (8 - 20 meters) Aquarium Spa Gym House Reef SPA HILL TRAIL (7 - 16 meters) Pool Piazza Bar & Lounge Granite Outcrop Guest Relations 100 Library Spa Hill Boutique Activity & Dive Centre Environment Centre PETITE ANSE BEACH Kids Playground 1 2 3 4 EAST BEACH5 6 Marsh 7 8 10 9 Villas 1 -10 Open Grassland Villa North Island Native Palm Forest North East Point (7 - 16 meters) Main Marsh BERNICA TRAIL Grand Paloss 180 110 Wooded Forest Bernica Wooded Forest GRAND PALOSS TRAIL Villas View Points Trails HONEYMOON Roads HONEYMOON TRAIL SUNSET BAR BEACH DECK Helipad Dive Spots THE SPOT Snorkel Spots HONEYMOON BEACH Picnic Spots Buggy Park SUNSET BEACH Open Grassland Coral Gardens Sprat City (8 - 20 meters) (6 - 22 meters) AFRICAN GRASS BLUE BUTTERFLY ALDABRA GIANT TORTOISE BLACK MUD TURTLE (TERRAPIN) SEYCHELLES SKINK LIZARD PHELSUMA GECKO AFRICAN LAND SNAIL HERMIT CRAB GHOST CRAB KEY TO BIRD, FAUNA AND FLORA ALIEN INVADER ENDEMIC TO THE SEYCHELLES INDIGENOUS TO THE SEYCHELLES REINTRODUCED ENDEMIC MIGRANT SPECIES SALLY LIGHTFOOT CRAB SEYCHELLES FRUIT BAT FAUNA OF NORTH ISLAND SEYCHELLES WHITE EYE SEYCHELLES BLUE PIGEON MADAGASCAR FODY BARRED GROUND DOVE COMMON WHIMBREL COMMON MYNA COMMON MOORHEN MADAGASCAR TUTRLE DOVE GREEN-BACKED HERON WHITE TAILED TROPIC BIRD BRIDLED TERN RUDDY TURNSTONE CRAB PLOVER SEYCHELLES KESTREL SEYCHELLES SUNBIRD BIRDS OF NORTH ISLAND COCONUT PALM THIEF PALM SEYCHELLES STILT PALM MILLIONAIRE’S SALAD HORNE’S PANDANUS COCO-DE-MER PALM TAKAMAKA TREE FISH POISON TREE BEACH GARDENIA TREE BEACH MORNING GLORY SEA LETTUCE INDIAN MULBERRY SURINAM/BRAZILIAN CHERRY LOOKING GLASS TREE INDIAN ALMOND TREE CASUARINA TREE WILD HIBISCUS TREE CASHEW NUT TREE BILIMBI TREE BREADFRUIT TREE FLORA OF NORTH ISLAND SOLID TABLE CORAL LETTUCE CORAL SQUAMOSE GIANT CLAM PORCELAIN CRAB TWOBAR ANEMONEFISH EMPEROR ANGELFISH COACHMAN BLOTCHEYE SOLDIERS BLUEBANDED SNAPPERS ORBICULAR BATFISH BLUEFIN KINGFISH DEVIL FIREFISH ROUND RIBBONTAIL RAY SPOTTED EAGLE RAY GREEN TURTLE HAWKSBILL TURTLE GIANT MORAY EEL WHITETIP REEF SHARK BOTTLENOSE DOLPHINS WHALE SHARK UNDER THE OCEAN VISIT NORTH-ISLAND.COM.

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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.
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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
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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
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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˙ ńska 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-Zyczyńska,Z.; Sielicki, S.; and observed heterozygosity were different in different breeding groups.
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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.
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American Kestrel
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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;
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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).
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Download and View Environment
NORTH ISLAND SUSTAINABILITY WHAT IS THE NOAH’S ARK PROJECT? NORTH North Island was purchased with the goal of restoring the unique biodiversity of the Seychelles to the island, by reintroducing endemic species that had become ISLAND locally extinct or brought to the verge of extinction previously, due (directly or indirectly) to human impact. Recognising the opportunity to contribute and to marry ECOLOGY & sustainability and ecotourism, North Island immediately embraced a comprehensive ENVIRONMENT rehabilitation and conservation plan that was soon dubbed “the Noah’s Ark project.” From the onset, there was, however, no doubt as to the high costs this would involve. The vehicle to generate the required funds was an ecotourism venture to be constructed on the island in an environmentally responsible way. WHY WAS THE ISLAND IN NEED OF RESTORATION? It is a well-known fact that the fragile ecology and the unique endemism of so many islands have been substantively and often irreversibly damaged by humans. Many islands of the Seychelles, unfortunately, are no exception. Even before colonialists settled permanently on the inner granitic islands in 1756, visiting ships of early traders had already harvested local animals and plants and brought in, some purposely and others accidentally, alien species. Some of these flourished and became pests, surviving to the detriment of the endemic fauna and flora. North Island’s original fauna and flora, for instance, suffered tremendously after the European black rat, an arboreal rodent, came to the island with visiting boats. In 1826, Madame Beaufond turned the island into a thriving coconut plantation and a fruit, vegetable and spices farm, bringing in several alien plants and domestic animals.
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Conservation Gains and Missed Opportunities 15 Years After Rodent Eradications in the Seychelles
J.E. Millett, W. Accouche, J. van de Crommenacker, M.A.J.A. van Dinther, A. de Groene, C.P. Havemann, T.A. Retief, J. Appoo and R.M. Bristol Millett, J.E.; W. Accouche, J. van de Crommenacker, M.A.J.A. van Dinther, A. de Groene, C.P. Havemann, T.A. Retief, J. Appoo and R.M. Bristol. Conservation gains and missed opportunities 15 years after rodent eradications in the Seychelles Conservation gains and missed opportunities 15 years after rodent eradications in the Seychelles J.E. Millett1, W. Accouche1, J. van de Crommenacker1,2, M.A.J.A. van Dinther2, A. de Groene3, C.P. Havemann4, T.A. Retief4, J. Appoo1 and R.M. Bristol5 1Green Islands Foundation, PO Box 246, Victoria, Mahé, Seychelles. <[email protected]>. 2Frégate Island Private, PO Box 330, Victoria, Mahé, Seychelles. 3WWF-Netherlands, Driebergseweg 10, 3708 JB Zeist, Netherlands. 4North Island, P.O. Box 1176, Victoria, Mahé, Seychelles. 5La Batie, Beau Vallon, Mahé, Seychelles. Abstract The Seychelles was one of the ﬁ rst tropical island nations to implement island restoration resulting in biodiversity gain. In the 2000s a series of rat eradication attempts was undertaken in the inner Seychelles islands which had mixed results. Three private islands with tourist resorts successfully eradicated rats: Frégate (2000), Denis Island (2003) and North Island (2005). Frégate Island was successful with the ﬁ rst eradication attempt whereas North and Denis Islands were initially unsuccessful, and both required second eradication operations. All three islands have developed conservation programmes including biosecurity, habitat rehabilitation, and species reintroductions, and have integrated nature into the tourism experience.
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Associations of Evolutionary & Ecological Distinctiveness Amongst
Chancellor, R. D. & B.-U. Meyburg eds. 2004 Raptors Worldwide WWGBP/MME Associations of evolutionary & ecological distinctiveness amongst Indian Ocean kestrels Jim J. Groombridge, Malcolm A. Nicoli, Carl G. Jones & JeffWatson ABSTRACT The evolutionary relationship between African kestrels, and their radiation across the Indian Ocean islands has attracted much debate from both evolutionary biologists, and conservationists tasked with recovering the endangered island forms. A molecular cytochrome-^ phylogeny of African kestrels has delivered a novel perspective on the distinctiveness of several mainland and endemic island kestrels. The molecular phylogeny supports an Old World origin for typical kestrels, and indicates a recent radiation of kestrels from Madagascar towards Mauritius and the Seychelles. The earlier arrival of kestrels on Mauritius appears consistent with the cessation of major island-forming volcanic activity there, whereas colonisation of the Seychelles appears compatible with the Pleistocene emergence of smaller islands. The different history of island isolation experienced by the Mauritius and Seychelles forms provides an ideal framework in which to compare morphological and ecological change. The molecular phylogeny reveals the Mauritius Kestrel to be the most evolutionarily distinct of the two island forms, whereas wing morphology and prey choice illustrate parallel forest-dwelling adaptations on both islands for ambush-style hunting of endemic Indian Ocean Phelsuma geckos. The molecular study underlines the conservation priority that has ensured the successful recovery of the Mauritius Kestrel, and reveals ecological patterns and processes elsewhere. INTRODUCTION Traditionally, the uniqueness - or biodiversity value - of an endangered species has been based upon a culmination of ecological, morphological, and behavioural comparisons with the remaining species in the genus.
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Forestry Department Food and Agriculture Organization of the United Nations
Forestry Department Food and Agriculture Organization of the United Nations Forest Health & Biosecurity Working Papers Case Studies on the Status of Invasive Woody Plant Species in the Western Indian Ocean 5. Seychelles By C. Kueffer1 and P. Vos2 1. Geobotanical Institute, ETH (Federal Institute of Technology), Zurich, Switzerland 2. Forestry Section, Ministry of Environment & Natural Resources, Seychelles May 2004 Forest Resources Development Service Working Paper FBS/4-5E Forest Resources Division FAO, Rome, Italy Disclaimer The FAO Forestry Department Working Papers report on issues and activities related to the conservation, sustainable use and management of forest resources. The purpose of these papers is to provide early information on on-going activities and programmes, and to stimulate discussion. This paper is one of a series of FAO documents on forestry-related health and biosecurity issues. The study was carried out from November 2002 to May 2003, and was financially supported by a special contribution of the FAO-Netherlands Partnership Programme on Agro-Biodiversity. The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. Quantitative information regarding the status of forest resources has been compiled according to sources, methodologies and protocols identified and selected by the authors, for assessing the diversity and status of forest resources. For standardized methodologies and assessments on forest resources, please refer to FAO, 2003.
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