Primates in Peril
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Ambatotsirongorongo Mounta<strong>in</strong>s and the forestless<br />
pla<strong>in</strong>. Most of this forest has disappeared and only small<br />
fragments rema<strong>in</strong> on the southern flanks of the three<br />
ma<strong>in</strong> summits. Their floristic composition has been<br />
characterized as a predom<strong>in</strong>antly humid, transitional<br />
mixture (Andrianarimisa et al. 2009; Ramanamanjato<br />
et al. 2002).<br />
Until recently, three of these forest fragments were the<br />
only known habitat of Cheirogaleus lavasoensis (Thiele<br />
et al. 2013). The three forest fragments had sizes of 50 ha,<br />
30 ha, and 25 ha <strong>in</strong> 2009 (Andrianarimisa et al. 2009).<br />
Extensive fieldwork <strong>in</strong> nearby transitional, humid, and<br />
littoral forest yielded no evidence for the occurrence<br />
of the species (Hapke et al. 2005; Hapke, Gligor, and<br />
Andrianjaka pers. obs). Lei et al. (2014) reported the<br />
occurrence of Cheirogaleus lavasoensis at Kalambatritra,<br />
170 km north of the Lavasoa-Ambatotsirongorongo<br />
Mounta<strong>in</strong>s at an altitude of approximately 1200 m.<br />
The Kalambatritra forest is Madagascar’s westernmost<br />
ra<strong>in</strong>forest and situated on the islands west-eastern<br />
dra<strong>in</strong>age divide <strong>in</strong> an elevation range of 1200-1680 m<br />
(Irw<strong>in</strong> et al. 2001). It is separated from the eastern humid<br />
forest by 16 km of open grassland and extends over an<br />
area with a north-southern diameter of approximately<br />
60 km.<br />
Thiele et al. (2013) reported data from 17 <strong>in</strong>dividuals<br />
of Cheirogaleus lavasoensis that had been captured<br />
and released between 2001 and 2006. The habitat of<br />
the species <strong>in</strong> the Lavasoa-Ambatotsirongorongo<br />
Mounta<strong>in</strong>s is biogeographically isolated, small,<br />
and fragmented. A survey <strong>in</strong> 2015 confirmed the<br />
persistence of Cheirogaleus lavasoensis <strong>in</strong> this area but<br />
also a further decl<strong>in</strong>e of forest cover (Andrianjaka and<br />
Hapke unpublished). The forest of Kalambatritra could<br />
potentially harbor a considerably greater population of<br />
Cheirogaleus lavasoensis. At present, it is not possible<br />
to estimate its size because Lei et al. (2014) report<br />
data from a s<strong>in</strong>gle <strong>in</strong>dividual that they could assign to<br />
the species. With respect to the differences <strong>in</strong> latitude<br />
and elevation, it is probable that there are strong<br />
ecological differences between Kalambatritra and the<br />
Lavasoa-Ambatotsirongorongo Mounta<strong>in</strong>s. Further<br />
research is necessary to gather <strong>in</strong>formation about the<br />
population size at Kalambatritra and about possible<br />
local adaptations of Cheirogaleus lavasoensis <strong>in</strong> the<br />
two areas. The population at Ambatotsirongorongo<br />
thus deserves high conservation priority, at least until<br />
more data become available about the population at<br />
Kalambatritra.<br />
The entire rema<strong>in</strong><strong>in</strong>g forest <strong>in</strong> the Lavasoa-<br />
Ambatotsirongorongo Mounta<strong>in</strong>s is situated with<strong>in</strong><br />
the Nouvelle Aire Protégée Ambatotsirongorongo.<br />
The greatest threats for the survival of Cheirogaleus<br />
lavasoensis <strong>in</strong> this area are further habitat loss and<br />
degradation. The ma<strong>in</strong> pressures are wood extraction,<br />
slash and burn cultivation, and accidental fires, which<br />
are frequent due to the practice of regular grassland<br />
burn<strong>in</strong>g. The forest fragments <strong>in</strong>habited by Cheirogaleus<br />
lavasoensis are apparently remnants of the most humid<br />
patches with<strong>in</strong> a formerly larger, cont<strong>in</strong>uous forest.<br />
Until recently, the local population relied on dryer<br />
forest remnants as ma<strong>in</strong> sources of construction timber<br />
and firewood. These fragments have now mostly<br />
disappeared, which generates the risk of <strong>in</strong>creas<strong>in</strong>g<br />
pressure onto the rema<strong>in</strong><strong>in</strong>g habitat of Cheirogaleus<br />
lavasoensis. At least two forest fragments <strong>in</strong>habited by<br />
Cheirogaleus lavasoensis harbor sources that are used by<br />
the local population for paddy irrigation and dr<strong>in</strong>k<strong>in</strong>g<br />
water supply. A successful conservation program<br />
should thus <strong>in</strong>tegrate water management, reforestation<br />
and habitat restoration.<br />
References<br />
Andrianarimisa, A., V. Andrianjakarivelo, Z.<br />
Rakotomalala, Z. and M. Anjer<strong>in</strong>ia<strong>in</strong>a 2009. Vertébrés<br />
terrestres des fragments forestiers de la Montagne<br />
d’Ambatotsirongorongo, site dans le Système des Aires<br />
Protégées de Madagascar de la Région Anosy, Tolagnaro.<br />
Malagasy Nature 2: 30-51.<br />
Foiben-Taosar<strong>in</strong>tan<strong>in</strong>’i Madagasikara. 1979. Ranopiso,<br />
Feuille M-62, Carte Topographique au 100000. Institut<br />
National de Géodésie et Cartographie, Antananarivo,<br />
Madagascar.<br />
Groeneveld, L.F., D. W. Weisrock, R. M. Rasoloarison, A.<br />
D. Yoder and P.M. Kappeler. 2009. Species delimitations<br />
<strong>in</strong> lemurs: multiple genetic loci reveal low levels of<br />
species diversity <strong>in</strong> the genus Cheirogaleus. BMC<br />
Evolutionary Biology 9: 30.<br />
Groeneveld, L.F., M. B. Blanco, J. L. Raharison, V.<br />
Rahal<strong>in</strong>arivo, R. M. Rasoloarison, P. M. Kappeler,<br />
P.M., L. R. Godfrey and M.T. Irw<strong>in</strong>. 2010. MtDNA and<br />
nDNA corroborate existence of sympatric dwarf lemur<br />
species at Ts<strong>in</strong>joarivo, eastern Madagascar. Molecular<br />
Phylogenetics and Evolution 55: 833-845.<br />
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