|Scientific Name:||Boophis septentrionalis Glaw & Vences, 1994|
Boophis luteus ssp. septentrionalis Glaw & Vences, 1994
|Taxonomic Source(s):||Frost, D.R. 2015. Amphibian Species of the World: an Online Reference. Version 6.0. New York, USA. Available at: http://research.amnh.org/herpetology/amphibia/index.html.|
|Taxonomic Notes:||This species was removed from the synonymy of Boophis luteus by Andreone and Randriamahazo (1997).|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||IUCN SSC Amphibian Specialist Group|
|Contributor(s):||Glaw, F., Scherz, D. & Vences, M.|
|Facilitator/Compiler(s):||Luedtke, J., Hobin, L. & Coals, L.|
Listed as Least Concern in view of its wide distribution across the forests of northern Madagascar and presumed large population.
|Previously published Red List assessments:|
|Range Description:||This species is known from Fôret d’Ambre Special Reserve and Montagne d'Ambre National Park (D'Cruze et al. 2008), forest fragments in the Tsarakibany area (Durkin et al. 2011), from Tsaratanana Strict Nature Reserve, Manongarivo (Andreone et al. 2008), from the Andapa region - including Ambolokopatrika - and the Masoala peninsula (Glaw et al. 2010). Its altitudinal range is between 379-1,150 m asl. It might prove to be more widespread, but as currently mapped its extent of occurrence (EOO) is 40,147 km2.|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||It is a locally common species. However due to ongoing declines in the extent and quality of habitat, the population is suspected to be decreasing.|
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||It inhabits both pristine and degraded rainforest, as well as secondary vegetation where trees survive. It probably cannot survive complete opening up of the habitat and is always found along streams, in which it breeds.|
|Continuing decline in area, extent and/or quality of habitat:||Yes|
|Movement patterns:||Not a Migrant|
|Use and Trade:||There are no records of this species being utilized.|
Its forest habitat is receding due to subsistence agriculture, timber extraction, charcoal manufacture, invasive spread of eucalyptus, livestock grazing, fire and expanding human settlements. It is probably also impacted by pollution of streams.
Intensive illegal wood extraction of rosewood species within Marojejy National Park that followed the 2009 political crisis of Madagascar caused concerns for the survival of rainforest–restricted species, such as this one. However, while illegal rosewood logging has probably ceased, wood extraction currently taking place in the Park seems to occur at lower elevations and is not thought to have reached elevations where this species has been recorded; along the boundaries of Marojejy deforestation is taking place to clear land for agriculture (F. Glaw pers. comm. November 2015).
Species in this genus have tested positive for Batrachochytrium dendrobatidis (Bd), however currently there have been no negative effects observed within amphibian populations in Madagascar suggesting the Bd strain has a low virulence level (Bletz et al. 2015).
It occurs in Fôret d’Ambre Special Reserve, Montagne d'Ambre National Park, Manongarivo Special Reserve, Tsaratanana Strict Nature Reserve, Marojejy National Park, and may possibly occur in Anjanaharibe-Sud Special Reserve.
Further protection of forest habitats in the region is required.
Further research is required to clarify the species' distribution, population size and trends, and is essential to fully understand the distribution, origin, type and virulence of Bd lineages found in Madagascar (Bletz et al. 2015).
|Citation:||IUCN SSC Amphibian Specialist Group. 2016. Boophis septentrionalis. The IUCN Red List of Threatened Species 2016: e.T57428A67205090.Downloaded on 21 June 2018.|
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