760 research outputs found

    Bats as bushmeat in Madagascar

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    Bats are eaten by people throughout Madagascar and although the larger species like Pteropus rufus, Eidolon dupreanum, Rousettus madagascariensis and Hipposideros commersoni are preferred, small insectivorous bats are also eaten. The national hunting season for bats is widely ignored and both unsuitable hunting practices and high offtake represent a serious threat to bat populations in some areas. Bat bushmeat may be an important source of protein for Malagasy people during periods of food shortage but in general there are few data on the socioeconomic and cultural importance of bats. Fruit bats produce a single offspring per year and are therefore susceptible to over-hunting. Nevertheless, large roosts offer the possibility of community managed harvests to secure the colony and provide a source of meat but further research is needed before this can be considered. Roost sites also present the best focus for conservation and greater effort is needed to control hunting using existing legislation and flexible community-based solutions that are sensitive to the local context. The threat of pathogen transfer from bats to people is of growing concern as more bat species are identified as vectors of emergent viral diseases.RÉSUMÉLes gens consomment des chauves-souris partout Ă  Madagascar et s’ils prĂ©fĂšrent les plus grandes espĂšces comme Pteropus rufus, Eidolon dupreanum, Rousettus madagascariensis et Hipposideros commersoni, les petites chauves-souris insectivores sont Ă©galement consommĂ©es. La pĂ©riode d’ouverture nationale de la chasse n’est gĂ©nĂ©ralement pas respectĂ©e et l’on assiste aussi bien Ă  de mauvaises pratiques cynĂ©gĂ©tiques qu’à des prĂ©lĂšvements importants qui reprĂ©sentent une menace sĂ©rieuse pour les populations de chauves-souris dans certaines rĂ©gions. Les chauves-souris peuvent constituer une source de protĂ©ines importante pour les populations villageoises pendant les pĂ©riodes de soudure alimentaire mais en rĂšgle gĂ©nĂ©rale, il existe peu de donnĂ©es sur les valeurs socio-Ă©conomiques ou culturelles des chauves - souris. Les chauves-souris frugivores ne produisent qu’un seul jeune par an, de sorte qu’elles sont sensibles Ă  la pression de chasse bien que les grands dortoirs pourraient offrir l’occasion d’une exploitation gĂ©rĂ©e par la communautĂ© pour assurer la sĂ©curitĂ© des colonies et fournir une source de protĂ©ines mais de plus amples recherches sont nĂ©cessaires avant que cette alternative ne puisse ĂȘtre retenue. Les dortoirs constituent Ă©galement les meilleures cibles des actions de protection de la nature et des efforts plus importants sont nĂ©cessaires pour contrĂŽler la chasse en s’appuyant sur la lĂ©gislation nationale ainsi que sur des solutions locales plus souples et adaptĂ©es, basĂ©es sur la communautĂ©. Les chauves-souris peuvent aussi transmettre des agents pathogĂšnes et cette menace est une source d’inquiĂ©tude grandissante car de plus en plus d’espĂšces de chauves-souris ont Ă©tĂ© identifiĂ©es en tant que vecteurs de maladies virales Ă©mergentes.

    Les baobabs de Madagascar : quel cadre réglementaire pour leur conservation ?

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    With lemurs, baobabs are the most emblematic species of Madagascar internationally. Seven species of the nine existing in the world are Madagascan endemic. This fact testifies the high rate of the biodiversity of the island. Having signed a number of international conventions, Madagascar intends to underline its commitment to the management and conservation of its natural resources. The international system of conservation framing is used for the implementation of national strategy. Thus, in addition to the international system of conservation systems such as the CBD, IUCN or CITES, baobabs of Madagascar are considered as non - timber forest products according to Decree N. 2915/87 of 7 September 1987 related to products accessories forest even if no term is clearly stipulated in this text. Moreover, there is no regulatory framework or specific text about conservation or exploitation of baobabs in Madagascar. Protected areas are then the only protection structures for baobabs. All species of Malagasy baobabs are represented in protected areas but their representation differs depending on the distribution of each species. Except for two protected areas, the baobab is not yet among the specific targets of conservation of protected areas in Madagascar. Adansonia grandidieri is an exception. It benefits indeed from two regional frameworks that specify measures to protect the species and priority activities to be undertaken for the species with the Dinan'ny Menabe and the regional conservation strategy for the species validated in 2013. At the local level, tools and instruments governing the management transfer could constitute framing elements for the management of baobabs. Some species have in fact non-negligible economic values without forgetting the cultural and religious values of some baobab trees. The implementation of the strategy for the conservation of each species is necessary at all levels especially in protected areas as three species are classified as ‘Endangered’ by IUCN. The conservation is necessary to ensure both sustainability of the species and integrity of all uses of baobabs.   RĂ©sumĂ© Avec les lĂ©muriens, les baobabs sont certainement reconnus dans le monde comme l’un des groupes les plus emblĂ©matiques de Madagascar. La Grande Île abrite six espĂšces endĂ©miques dont trois ‘En Danger’ sur la liste rouge de l’UICN et trois ‘Quasi - menacĂ©es’. Cet article se propose de passer en revue les dispositions mises en place ainsi que les opportunitĂ©s et limites de la conservation et de la gestion durable des baobabs endĂ©miques de Madagascar. En ratifiant les conventions internationales sur la diversitĂ© biologique (CDB) et sur le commerce international des espĂšces menacĂ©es (CITES), Madagascar s’est engagĂ© Ă  assurer la conservation et la gestion durable des baobabs, plus particuliĂšrement celles des espĂšces menacĂ©es. Cependant, selon l’ArrĂȘtĂ© n° 2915/87 du 7 septembre 1987 sur les produits accessoires des forĂȘts, les baobabs de Madagascar sont considĂ©rĂ©s comme des produits forestiers non ligneux pouvant ĂȘtre exploitĂ©s et aucune disposition n’a Ă©tĂ© prise pour gĂ©rer durablement leur exploitation. La prĂ©sence des baobabs est confirmĂ©e dans 35 zones protĂ©gĂ©es mais, Ă  l’exception de l’AllĂ©e des Baobabs et de la Montagne des Français, les baobabs ne sont pas considĂ©rĂ©s comme des cibles de conservation mais davantage comme des Ă©lĂ©ments profitant d’une protection intrinsĂšque en faisant partie intĂ©grante d’habitats ciblĂ©s pour la conservation. Seule Adansonia grandidieri bĂ©nĂ©ficie de mesures de conservation rĂ©gionales par la mise en place du Dinan’ny Menabe et de la stratĂ©gie de conservation de l’espĂšce dans la RĂ©gion du Menabe. Or les pressions observĂ©es actuellement et les prospectives portant sur l’aire de distribution des deux autres espĂšces classĂ©es ‘En Danger’ que sont A. perrieri et A. suarezensis justifient la mise en place de stratĂ©gies de conservation.

    Bats roosting in public buildings: A preliminary assessment from Moramanga, eastern Madagascar

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    Madagascar has many synanthropic bat species but relatively little is known about how people interact with them. A preliminary assessment on the presence of bats in buildings and their interactions with people was conducted in the eastern town of Moramanga. Fifty of the 156 buildings were reported to contain active bat colonies and 46 of these were in schools. The bats, two species of Molossidae, roosted principally in the roof spaces of buildings that were more than ten years old. Users of the buildings were relatively tolerant of the bats, although 41% reported negative attitudes because of the odor of roosting colonies and some concerns over the possibility of contracting respiratory ailments from bat faeces. Guano accumulated in classrooms and was observed on floors and desks. Basic renovations could improve the learning environment for children and could be conducted in a bat-friendly way. More research is needed to assess the health risks to people from interacting with bats in Madagascar, and this includes people who study, eat, and handle bats or work and live in buildings or caves where bats roost. RÉSUMÉCertaines espĂšces de chauves-souris ont su s’adapter Ă  l’environnement humain et ont ainsi colonisĂ© certaines parties des constructions humaines. Pourtant, de nombreuses espĂšces de chauves-souris sont associĂ©es Ă  certaines maladies Ă©mergeantes. Madagascar possĂšde plusieurs espĂšces synanthropiques de chauves-souris dont quelques unes associĂ©es Ă  des virus alors que l’interaction de ces animaux avec les gens est trĂšs peu connue. Pour mieux comprendre ce phĂ©nomĂšne, nous avons menĂ© une Ă©tude prĂ©liminaire sur la prĂ©sence de chauves-souris et de leurs interactions avec les gens dans des constructions urbaines, plus particuliĂšrement dans des bĂątiments publics (ceux de l’éducation ou de la santĂ©) Ă  Moramanga, une ville situĂ©e dans la partie orientale de l’üle. Des enquĂȘtes informelles ont Ă©tĂ© rĂ©alisĂ©es auprĂšs des usagers de ces enceintes et des comptages nocturnes de chauves - souris ont Ă©tĂ© effectuĂ©s pour certains de ces bĂątiments au moment oĂč ces animaux quittaient leur dortoir. Les chauves-souris ont Ă©tĂ© identifiĂ©es grĂące Ă  des photos ainsi qu’à partir de mesures et caractĂ©ristiques morphomĂ©triques des individus capturĂ©s Ă  l’aide de filets fauchoirs. Nous avons Ă©talĂ© des films en plastique pour rĂ©colter les fĂšces de chauves-souris dans les combles ou dans des salles de classes, et nous avons Ă©galement recueilli les guanos amassĂ©s aprĂšs le nettoyage des salles de classe. Les fĂšces ont Ă©tĂ© pesĂ©es avec des Pesola. Sur les 156 constructions rĂ©pertoriĂ©es, une cinquantaine Ă©tait habitĂ©e par des chauves-souris. La prĂ©sence de ces animaux a Ă©tĂ© confirmĂ©e dans la plupart des Ă©coles visitĂ©es (46 sur 65) mais pas dans les bĂątiments hospitaliers et les centres mĂ©dicaux. Les chauves-souris reprĂ©sentĂ©es par deux espĂšces de Molossidae, vivaient dans des combles de bĂątiments publics construits depuis plus de dix ans. Les personnes utilisant ces bĂątiments Ă©taient relativement tolĂ©rantes sur la prĂ©sence des chauves - souris bien que 41% relevait des attitudes nĂ©gatives portant soit sur l’odeur dĂ©gagĂ©e par les colonies, soit sur des affections respiratoires attribuĂ©es aux fĂšces de ces chauves-souris, de sorte que certains occupants de ces bĂątiments publics ont essayĂ©, mais en vain, de se dĂ©barrasser de ces animaux. Les matiĂšres fĂ©cales s’accumulaient dans les salles de classe et ont Ă©tĂ© observĂ©es sur le sol et les bureaux. Des rĂ©parations Ă©lĂ©mentaires pourraient amĂ©liorer l’environnement Ă©ducatif pour les enfants et pourraient ĂȘtre conduites de maniĂšre Ă  ne pas menacer les chauves-souris. Des recherches supplĂ©mentaires sont nĂ©cessaires pour Ă©valuer les risques sanitaires des interactions avec les chauves-souris Ă  Madagascar, et plus particuliĂšrement pour les gens qui Ă©tudient, consomment ou touchent les chauves-souris, et mĂȘme ceux qui travaillent ou vivent dans des immeubles ou des grottes oĂč les chauves-souris gĂźtent

    Lois et rĂšglements sur la faune sauvage Ă  Madagascar : ProgrĂšs accomplis et besoins du futur

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    In many countries wildlife species are threatened by hunting for meat or collection for the pet trade. Wildlife laws which control where these activities can occur, limit the timing of exploitation, or provide strict protection for some species are therefore an important component of the conservation strategy. However it is important that these wildlife laws reflect the ecology and threat status of the species concerned, and that they are aligned with any relevant international conventions. In this article we discuss the legal framework for exploiting and protecting tetrapod species in Madagascar. We review the 2006 update to wildlife legislation with respect to international treaties, other national legislation and the IUCN Red List of Threatened Species. We also present a summary of the different categories of hunting (sport, commercial, scientific, and subsistence) and the control of hunting in protected areas. Madagascar has a sound legal framework for the use and protection of wildlife and the classification of species into protected, pest and legally hunted is clear and mostly fits well with the species’ classification according to the IUCN Red List and CITES. A revision of the protected species list managed is needed however to (i) include marine mammals that are protected by fisheries law and the Convention on Migratory Species and to (ii) better reflect the rights of people whose livelihoods rely heavily on the income or protein derived from hunting animals. Renewed effort to communicate and enforce wildlife legislation is needed, especially regarding the illegal hunting and export of protected species. This would also support the ongoing initiative to expand the protected area system and could be integrated into a revised National Biodiversity Strategy and Action Plan that Madagascar should produce for 2011-2020 as part of its commitment to implementing the Convention on Biological Diversity. RÉSUMÉLes lois et rĂšglements dĂ©terminant les niveaux de protection des espĂšces de la faune et de la flore sauvages sont des indicateurs importants de l’importance qu’accorde un pays Ă  la conservation de sa biodiversitĂ©. Dans cette revue, nous Ă©valuons la cohĂ©rence entre les lois et rĂšglements portant sur la gestion de la faune sauvage Ă  Madagascar, en considĂ©rant la lĂ©gislation nationale, les conventions internationales ratifiĂ©es et la Liste Rouge de l’UICN pour les confronter aux rĂ©alitĂ©s locales. Suite Ă  nos analyses, nous pouvons conclure que Madagascar dispose d’un cadre juridique adĂ©quat pour rĂ©glementer la protection et l’exploitation des animaux sauvages. Cependant, des rĂ©visions et mises Ă  jour sont nĂ©cessaires, particuliĂšrement en ce qui concerne la liste des espĂšces dans les diffĂ©rentes catĂ©gories et la facilitation de la mise en application de la loi

    Case Study: Producer concerns and perceptions regarding the effect of methane on cattle production and the environment: A survey of Nebraska producers

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    Enteric methane production from cattle and its effect on climate change has been a topic of debate. Multiple studies have explored methods to reduce cattle enteric methane production while simultaneously improving performance. However, most strategies developed have not been widely implemented by cattle producers. Knowledge of producer concerns and perceptions on methane production from cattle and its effect on the environment may be limited. Therefore, the objectives of this survey were to determine what Nebraska producers know about methane production by cattle and how it affects performance and to determine whether different age groups, regions of Nebraska, and production size and type affects producer opinions on enteric methane production and climate change. The survey had a response rate of 22%. Regarding climate change, approximately 39% of producers disagreed, 33% were neutral, and 28% agreed they were concerned. However, producers in central and eastern Nebraska were closer to neutral than producers in western Nebraska (P \u3c 0.05). Younger producers perceived cattle to have a more positive effect on the environment and reported that they were more likely to adopt new management techniques that have been shown to improve animal performance than older producers (P \u3c 0.05). Most producers reported receiving production-related information from veterinarians (47.6%), followed by the “other” category (34.9%), the University of Nebraska (15.6%), and state and federal governments, which were the lowest (1.4 and 0.6%, respectively). In the last 3 yr, approximately 57% of producers attended one or fewer extension meetings, but 37% had not attended any extension meetings

    Case Study: Producer concerns and perceptions regarding the effect of methane on cattle production and the environment: A survey of Nebraska producers

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    Enteric methane production from cattle and its effect on climate change has been a topic of debate. Multiple studies have explored methods to reduce cattle enteric methane production while simultaneously improving performance. However, most strategies developed have not been widely implemented by cattle producers. Knowledge of producer concerns and perceptions on methane production from cattle and its effect on the environment may be limited. Therefore, the objectives of this survey were to determine what Nebraska producers know about methane production by cattle and how it affects performance and to determine whether different age groups, regions of Nebraska, and production size and type affects producer opinions on enteric methane production and climate change. The survey had a response rate of 22%. Regarding climate change, approximately 39% of producers disagreed, 33% were neutral, and 28% agreed they were concerned. However, producers in central and eastern Nebraska were closer to neutral than producers in western Nebraska (P \u3c 0.05). Younger producers perceived cattle to have a more positive effect on the environment and reported that they were more likely to adopt new management techniques that have been shown to improve animal performance than older producers (P \u3c 0.05). Most producers reported receiving production-related information from veterinarians (47.6%), followed by the “other” category (34.9%), the University of Nebraska (15.6%), and state and federal governments, which were the lowest (1.4 and 0.6%, respectively). In the last 3 yr, approximately 57% of producers attended one or fewer extension meetings, but 37% had not attended any extension meetings

    A conservation assessment of Rousettus madagascariensis (Grandidier, 1929, Pteropodidae) roosts in eastern Madagascar

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    We visited four cave roosts of the near threatened, and endemic, fruit bat Rousettus madagascariensis over a five year period and found major threats to the bats from hunting and deforestation. The conservation of this species is particularly challenging because it is legally hunted inside its cave roosts. Although provisional protected area status was obtained for two sites with community support, hunting continued. R. madagascariensis roosts were associated with humid forest and the loss of vegetation around caves rendered them unsuitable for the bats at two abandoned sites. A few individual hunters can have a rapid and destructive impact on R. madagascariensis roosts and future initiatives in this area should involve working with hunters to develop realistic solutions to reduce hunting. These efforts need to be supported by habitat protection measures.  RÉSUMÉ L’espĂšce de chauve-souris frugivore Quasi MenacĂ©e Rousettus madagascariensis est endĂ©mique Ă  Madagascar. Nous avons Ă©tudiĂ© quatre gĂźtes dans des grottes oĂč cette espĂšce a Ă©tabli des dortoirs diurnes en procĂ©dant Ă  des visites multiples au cours d’une pĂ©riode de cinq ans et avons trouvĂ© que la chasse et la dĂ©forestation constituaient les principales menaces pesant sur R. madagascariensis. La conservation de cette espĂšce est particuliĂšrement difficile dans la mesure oĂč la chasse dans ses dortoirs ou gĂźtes est permise. Bien que les deux sites abritant l’espĂšce bĂ©nĂ©ficient du statut de Nouvelle Aire ProtĂ©gĂ©e avec le soutien de la communautĂ© locale, la chasse ne cesse de s’intensifier. Les gĂźtes de R. madagascariensis sont associĂ©s Ă  la forĂȘt humide, de sorte que la disparition de la vĂ©gĂ©tation arborĂ©e autour de deux de ces gĂźtes les a rendus impropres Ă  hĂ©berger R. madagascariensis qui a fini par les abandonner. La disparition de la vĂ©gĂ©tation arborĂ©e autour du gĂźte pourrait ĂȘtre Ă  l’origine d’un changement de microclimat Ă  l’intĂ©rieur de la grotte qui constitue le gĂźte diurne. Les activitĂ©s de certains chasseurs peuvent aussi avoir un impact destructif rapide sur les gĂźtes de R. madagascariensis et des initiatives Ă  mener conjointement avec les chasseurs sont nĂ©cessaires pour Ă©laborer des mesures rĂ©alistes afin de rĂ©duire la chasse. De tels efforts doivent ĂȘtre Ă©tendus et appuyĂ©s par des mesures de protection de l'habitat car plusieurs autres gĂźtes pourraient exister dans les forĂȘts du versant est de Madagascar et subir les mĂȘmes pressions anthropiques. Des recherches rĂ©centes ont Ă©galement montrĂ© que l’histoire naturelle de R. madagascariensis est Ă©troitement liĂ©e Ă  la forĂȘt naturelle, de sorte que la perte de la biodiversitĂ© de la forĂȘt naturelle malgache menace les plantes dont se nourrit cette espĂšce ainsi que l’équilibre de l’ensemble de l’écosystĂšme dont elle dĂ©pend.

    Preliminary fish survey of Lac Tseny in northwestern Madagascar

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    We surveyed the fish fauna of Lac Tseny, in the Sofia Region of northwestern Madagascar, during October 2010 by observing commercial catches and targeted netting of areas used by endemic species. We recorded seven native fish species at the lake, including three endemic cichlids, a herring and a catfish. We confirmed the continued survival of the Critically Endangered Paretroplus menarambo, as well as the presence of a Paretroplus taxon that may be new to science. The commercial fishery in the lake is sustained by introduced tilapiines and the native Savagella robusta. The three endemic cichlids (Paretroplus spp.) were not targeted by commercial fishermen, but when caught in small numbers were retained for domestic consumption. Submerged trees in the west of the lake restrict fishing with nets and probably provide important habitat for P. menarambo. Priority next steps at the lake include (i) additional surveys and biological studies of the endemic fish species and the Critically Endangered Madagascar big-headed turtle, Erymnochelys madagascariensis, (ii) clarification of the taxonomic status of Paretroplus cf. kieneri and, should it prove a new taxon, its formal scientific description, and (iii) continued engagement with fishing communities and authorities to promote practices that benefit livelihoods and the survival of threatened fish species.   RÉSUMÉ La composition spĂ©cifique de l'ichtyofaune du lac Tseny, dans l'ouest de Madagascar (rĂ©gion de Sofia) a Ă©tĂ© inventoriĂ©e au cours du mois d’octobre 2010, en observant les prises des pĂȘcheurs et des pĂȘches ciblĂ©es sur les espĂšces endĂ©miques. Sept espĂšces de poissons indigĂšnes ont Ă©tĂ© observĂ©s, dont trois cichlidĂ©s endĂ©miques (Paretroplus menarambo, Paretroplus lamenabe et Paretroplus cf. kieneri), un hareng indigĂšne (Sauvagella robusta) et un poisson-chat (Arius madagascariensis). Deux de ces espĂšces sont classĂ©es comme MenacĂ©es dans la Liste Rouge de l'UICN : P. menarambo est une espĂšce en Danger Critique d’Extinction qui n’est connue que du lac Tseny et A. madagascariensis est une espĂšce en Danger d’Extinction et endĂ©mique de la rĂ©gion de Sofia. Un des poissons que nous avons inventoriĂ© dans le genre Paretroplus semble ĂȘtre une forme non dĂ©crite. Les pĂȘcheurs ont indiquĂ© que P. menarambo est associĂ© Ă  des arbres immergĂ©s le long de la rive occidentale du lac qui offrent un habitat propice Ă  la reproduction et Ă  l'alimentation. Ces arbres immergĂ©s empĂȘchent l'utilisation des filets pour la pĂȘche et limitent ainsi la pression de pĂȘche qui s’exerce sur cette espĂšce. Les trois espĂšces endĂ©miques de Paretroplus sont prisĂ©es par les pĂȘcheurs qui les gardent pour leur consommation personnelle plutĂŽt que de les vendre. La pĂȘche commerciale pratiquĂ©e dans le lac semble pĂ©renne grĂące Ă  la prĂ©sence de tilapias allogĂšnes et du hareng indigĂšne (Sauvagella robusta) qui approvisionnent les marchĂ©s de poisson local (Tsaratanana), rĂ©gionaux (Boriziny et Mandritsara) et national (Antananarivo). Les populations locales ont rapportĂ© que la surpĂȘche, l'immigration, l’utilisation illĂ©gale de filets Ă  petit maillage et le non respect de la saison de fermeture de la pĂȘche Ă©taient les principales menaces pesant sur l’ichtyofaune du lac Tseny. Une baisse de la pĂȘche commerciale pourrait entraĂźner une ruĂ©e vers les espĂšces endĂ©miques et l'ouverture des zones d’arbres immergĂ©s pour la pĂȘche. Le lac Tseny abrite un assemblage unique de poissons qui doivent ĂȘtre protĂ©gĂ©s dans leur habitat qui est essentiel aux cichlidĂ©s endĂ©miques par le maintien d'une pĂȘche commerciale pĂ©renne. Les prochaines Ă©tapes Ă  mener en prioritĂ© pour le lac incluent : (i) des Ă©tudes supplĂ©mentaires sur la biologie des poissons endĂ©miques et de la PodocnĂ©mide de Madagascar (Erymnochelys madagascariensis), une tortue en Danger Critique d’Extinction, (ii) la clarification du statut taxinomique de Paretroplus cf. kieneri qui pourrait ĂȘtre une nouvelle espĂšce et sa description, le cas Ă©chĂ©ant, et (iii) l’engagement continu avec les communautĂ©s de pĂȘcheurs et les autoritĂ©s locales pour promouvoir des pratiques Ă©quitables en faveur des populations riveraines et pour la survie des espĂšces de poissons menacĂ©es

    Baryon Charge Radii and Quadrupole Moments in the 1/N_c Expansion: The 3-Flavor Case

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    We develop a straightforward method to compute charge radii and quadrupole moments for baryons both with and without strangeness, when the number of QCD color charges is N_c. The minimal assumption of the single-photon exchange ansatz implies that only two operators are required to describe these baryon observables. Our results are presented so that SU(3) flavor and isospin symmetry breaking can be introduced according to any desired specification, although we also present results obtained from two patterns suggested by the quark model with gluon exchange interactions. The method also permits to extract a number of model-independent relations; a sample is r^2_Lambda / r_n^2 = 3/(N_c+3), independent of SU(3) symmetry breaking.Comment: 30 pages, no figures, REVTeX
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