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In the North Atlantic, the waters surrounding the Cape Verde Islands are a "potential hot spot" for cookiecutter shark Isistius spp. interactions with cetaceans. These occurrences were recently identified by the improved efforts of researchers to document cetacean strandings in the Cape Verde archipelago, as well as by the photo identification efforts of live whales and dolphins. The documentation of individual and mass stranding events confirmed that cookiecutter shark interactions with cetaceans in Cape Verde seas are remarkably common.
For two centuries, the seas of the Cape Verde archipelago were a favorite whaling ground – known as the ‘San Antonio Ground’ among whalers – for an international fleet of whaling ships and especially for the "Yankee whalers" from New England, USA. One of their main targets was the humpback whale Megaptera novaeangliae, of which large numbers were caught (e.g. Clark 1887, Townsend 1935, Reeves et al. 2002, Smith & Reeves 2003, 2010).
The shores of Cape Verde hosts one of the most important nesting populations of the loggerhead turtle Caretta caretta in the world, as well as important feeding grounds for hawksbill Eretmochelys imbricata and green turtles Chelonia mydas. In the past few years, a number of scientific studies have demonstrated the relevance of the waters and beaches of this archipelago for the conservation of these endangered marine megavertebrates. This article aims to bring together the most relevant scientific information published on the subject so far. In addition, we will provide an overview of the current situation of sea turtles in Cape Verde, their conservation status and their importance in an international context.
Arthropoda is the most diverse phylum of the animal kingdom. The majority of bloodsucking arthropods of public health concern are found in two classes, Arachnida and Insecta. Mosquitoes, ticks, cattle flies, horseflies and biting midges are the main hematophagous groups occurring in the Cape Verde Islands and whose role in infectious disease transmission has been established. In this literature review, the main morphological and biological characters and their role in the cycle of disease transmission are summarized.
Loggerhead Caretta caretta is now the only species of marine turtle nesting on the island of Sal, Cape Verde Islands. Since 2008, ADTMA - SOS Tartarugas has patrolled all the southern beaches of the island in order to protect nesting females and to collect nesting data. Although hunting is still a major issue, with 90 turtles killed in 2009, habitat loss and light pollution are becoming an ever more serious threat. Construction sites, hotels, apartment buildings and restaurants close to beaches, bright lights and illegal removal of sand are contributing to a marked decrease in the total number of nesting turtles on some beaches. In 2009, beaches on Sal experienced an average increase in nests of 200%, while the beach most affected by construction (Tortuga Beach) saw a decrease of nests of 7.3% (from 19.1% of total number of nests in 2008 to 11.8% in 2010). This beach also recorded a much lower nest to emergence ratio than normal (17.6% of emergences resulting in nests compared to 29.9% in other areas), indicating reluctance to nest due to light pollution and other disturbances.
Sponges belonging to the genera Amphilectus Vosmaer, Esperiopsis Carter and Ulosa de Laubenfels of the family Esperiopsidae were collected during 1986 and 1988 expeditions of the Netherlands Centre for Biodiversity Naturalis (at that time the National Museum of Natural History at Leiden and the Zoological Museum of Amsterdam) in waters off the coasts of Mauritania and the Cape Verde Islands. Four new species, Amphilectus utriculus sp. nov., Amphilectus strepsichelifer sp. nov., Esperiopsis cimensis sp. nov., Ulosa capblancensis sp. nov., and two already known species, Amphilectus cf. fucorum (Esper) and Ulosa stuposa (Esper) are described and discussed.
Recent data on status and distribution of resident and migrant birds in the Cape Verde Islands are presented, including records of 25 taxa new to the archipelago, viz. Mareca penelope, M. americana, Anas carolinensis, A. clypeata, Pterodroma arminjoniana, Sula dactylatra, Egretta thula, Ardea melanocephala, Hieraaetus pennatus, Porzana porzana, Crecopsis egregia, Porphyrula martinica, Pluvialis apricaria, Calidris fuscicollis, C. bairdii, Gallinago delicata, Larus audouinii, L. atricilla, Streptopelia decaocto, Ceryle rudis, Ptyonoprogne rupestris, Motacilla citreola, Erithacus rubecula, Oenanthe leucopyga and Lanius senator. The current situation of some endemic taxa is discussed, some of which (e.g. Ardea bournei) are critically endangered, while others (e.g. Acrocephalus brevipennis) have been shown to be more widespread than previously known.
Recent data on status and distribution of resident and migrant birds in the Cape Verde Islands are presented, including records of nine taxa new to the archipelago, viz. Ixobrychus sturmii, Botaurus stellaris, Butorides striatus, Circus cyaneus, Porzana pusilla, Fulica atra, Chlidonias niger, Acrocephalus schoenobaenus and Hippolais polyglotta. Also presented are data on a number of breeding taxa, including the first record of the endemic Raso lark Alauda razae outside the islet of Raso. The alarming situation of the magnificent frigatebird Fregata magnificens, of which probably only two individuals remain in Cape Verde, constituting the entire population in the East Atlantic, is highlighted. During the past decade, breeding populations of common moorhen Gallinula chloropus appear to have become well-established on the islands of Santiago and Boavista. Following its expansion through Northwest Africa and the Canary Islands, Eurasian collared dove Streptopelia decaocto has now also colonized the Cape Verde Islands.
Humpback whales Megaptera novaeangliae perform the longest known migrations among mammalian species (Stone et al. 1990, Rasmussen et al. 2007), feeding at high latitudes during the summer and undertaking annual journeys to their wintering breeding grounds in warm and shallow tropical waters (Winn & Reichley 1985, Clapham & Mead 1999). Due to breeding site fidelity and temporal separation at low latitudes, gene flow between Northern and Southern Hemisphere populations appears to be very limited (Rizzo & Schulte 2009). However, inter-oceanic exchange has recently been documented (Pomilla & Rosenbaum 2005, Stevick et al. 2010), demonstrating that philopatry may not be as strong as previously inferred (cf. Baker et al. 1993, 1994, Valsecchi et al. 1997).