• Ganzhorna's mouse lemur (Microcebus ganzhorni). The IUCN Red List of Threatened Species 2020

      Ganzhorn, J.; Donati, G; Eppley, Timothy M.; Hyde Roberts, S; Poelstra, J.W; Rakotondranary, S.J.; Ramanamanjato, J.-B.; Randriantafika, F.M.; Refaly, E.; Tsagnangara, C.; et al. (2020)
      Up to 2016, the south-eastern subpopulation of Grey Mouse Lemurs has been considered to represent a disjunct population of Microcebus murinus (Mittermeier et al. 2010). Based on samples from the littoral forest of Mandena a new form has been separated from M. murinus and been named as M. ganzhorni based on genetic grounds (Hotaling et al. 2016). Morphologically M. ganzhorni is indistinguishable from M. murinus and difficult to distinguish from M. griseorufus (M. griseorufus has a white belly with white underfur while M. murinus and M. ganzhorni have greyish underfur) and thus, taxonomic assignments in the field remain uncertain without genetic analyses. Given these uncertainty, the Extent of Occurrence was unclear at the time the species was described. New genetic analyses showed that M. ganzhorni does not occur in Andohahela National Park (Tiley, Poelstra, Yoder et al., unpubl. data) and does not move up the coastal mountains as this is the range of M. tanosi and M. manitatra (Rasoloarison et al. 2013, Donati et al. 2019). M. ganzhorni thus seems to be restricted to littoral forests east and possibly west of Fort Dauphin. In any case, the area of occupancy (AOO) is estimated to be above 10 km� but below 500 km�. These forests are severely fragmented with the largest fragments measuring less than 2 km�. The size of most forest fragments is declining and forests are being degraded. The species tolerates forest degradation and occurs in a wide range of different habitats, including gardens....
    • Thomas' dwarf lemur (Cheirogaleus thomasi). The IUCN Red List of Threatened Species 2020

      Ganzhorn, J.; Donati, G; Eppley, Timothy M.; Lahann, P; Rakotondranary, S.J.; Ramanamanjato, J.-B.; Randriantafika, F.M. (2020)
      This species has been assessed as Endangered as the area of occupancy (AOO) is estimated to be between 12 and 260 km2, and the extent of occurrence is estimated to be 458 km2. The forests are severely fragmented with the largest fragments measuring less than 4 km2. The size of most forest fragments is declining and forests are being degraded. The species does not seem to tolerate forest degradation and thus does not occupy all forest fragments of the region (Ganzhorn et al. 2007). Given the impact of habitat loss, the species is thought to be in decline.