Taxonomy

endemique
protegee
UICN

Common name :

Le Gecko Géant de Sarasin Sarasins’ Giant Gecko

Red List Status -

Vulnerable (VU) , assessed in 11/12/2017

Protected species -

in Southern Province , in Northern Province

Description

 

Description:

A large species of gecko growing to a body length of 135mm and with a tail approximately the length of the body; moderately broad toes; and a colour pattern of pale to dark brown above, variably with obscure to bold, pale, V-shaped nape neck markings and scattered pale spots or blotches either side of the middle of the back.

 

Natural distribution:

Southern New Caledonia.

Distribution within Province Sud: Recorded from eight locations in the very far south of the island, ranging from Baie du Prony in the south, to Mt Koghis in the north.

 

 

Habitat:

Humid forest.

 

Threats

  • high but localised level of threat to low elevation humid forest on the southeast coast through loss, modification and fragmentation of coastal forest habitat.

  • high level of threat to humid forest habitat on ultramafic soils through repeated firing of adjacent maquis habitat, leading to loss and degradation of the forest edge.

  • moderate to high but localised level of threat to isolated humid forest and gully forests on southern ultramafics through loss or degradation of habitat from activities associated with mining.

  • potentially high level of threat to populations in humid forest with high infestation levels of the introduced Little Red Fire Ant (Wasmannia auropunctata), resulting in a significant decline in abundance.

  • potentially high level of threat from exotic pests such as rats and cats (predation of adults, young & eggs) in heavily affected forest patches.

  • localised but potentially intensive decline resulting from collection for illegal trade at readily accessible sites.

 

Conservation Status: Vulnerable

 

Rhacodactylus sarasinorum is a large gecko with a very restricted distribution, it is known from only seven locations in the south of the island, each representing an isolated sub-population - it is likely to occur in other closed forest patches in gullies of the Plaine des Lacs region. However, these forest patches are usually small isolates with little connectivity between them and although the number of sub-populations is likely to increase the overall real area of occupancy will remain low, and individual sub-populations will be at an increased level of risk by virtue of their very small size.

 

A large part of the species distribution lies within an area which is undergoing extensive change due to mining activities. Humid forest in this region has suffered and is still experiencing a decline in area of occupancy and/or quality. This in combination with the range of existing and potentially high level threats identified above and the specialised biology of the giant geckos in the genus Rhacodactylus, indicate Rhacodactylus sarasinorum satisfies the criteria to be categorised as Vulnerable, and could be moved to a higher level of conservation concern if those threats intensify.

 

 Department of Herpetology, Australian Museum, 6 College Street, Sydney 2000, New South Wales, Australia

 


Although Correlophus sarasinorum occurs in several protected areas, its overall distribution is restricted and fragmented, and there is continuing decline in the extent and quality of its habitat, mainly from wildfires, mining activities and introduced ungulates. Hence it is listed as Vulnerable.

Geographical area


This species is endemic to Province Sud, New Caledonia. It is known only from a number of isolated populations across the far south of Grande Terre (south of Mt Koghis). Known populations are widely scattered and often in small, isolated closed forest remnants. It occurs at elevations between 20 m to 600 m. The extent of occurrence is estimated at 708 km2, and the area of occupancy at 56 km2.

Population


This species is presumed to have suffered a substantial reduction in population size and area of occupancy in the past due to the logging and wildfires that have decimated closed forests and left them severely fragmented. Although logging has now stopped, the expanding nickel industry in the south of Grande Terre is resulting in further habitat loss and fragmentation. Correlophus sarasinorum is still relatively common at some locations but there are no quantitative data on population size or trends.

Habitat


This species primarily occurs in closed humid forests but has been documented in adjoining tall maquis shrublands (maquis paraforestier) and coastal forests. It is nocturnal and arboreal. It shelters by day in tree crevices and holes and forages at night on trunks and branches. Found in almost all forest patches with suitably sized trees. Probably highly dependent on hollows in trees.

Threats


The primary threat to this species is the further loss or degradation of habitat, particularly from mining in the southern part of its range, but also including peripheral damage to forest remnants from wildfires in maquis shrublands and damage from introduced ungulates (deer and pigs). Other threats include predation by introduced mammals as rodents (Thibault 2017) and cats (Palmas 2017) and the introduced ant, Wasmannia auropunctata, which is expected to have a detrimental impact (Jourdan et al. 2000, 2001). Correlophus sarasinorum is also vulnerable to illegal collection and trafficking at accessible locations.

Conservation


This species is protected in Province Nord under Code de l'environnement de la Province Nord (Délibération No. 306-2008/APN, 24 October 2008) and in Province Sud under Code de l'environnement de la Province Sud (Délibération No. 25-2009/APS, 20 March 2009). It is present in Parc Provincial de la Rivière Bleue and a number of other reserves in the south including Mt Koghis, Forêt Cachée, Pic du Pin, Pic du Grand Kaori and Forêt Nord. No active conservation management is currently being undertaken for this species.

Bibliography


IUCN 2021. The IUCN Red List of Threatened Species. Version 2021-2.

Bauer, A.M. and Sadlier, R.A. 2000. The Herpetofauna of New Caledonia.

Bauer, A.M., Jackman, T.R., Sadlier, R.A. and Whitaker, A.H. 2012. Revision of the giant geckos of New Caledonia (Reptilia: Diplodactylidae: Rhacodactylus). Zootaxa(3404) , p.1–52.

Uetz, P. (ed.) 2017. The Reptile Database.

Bauer, A.M., Jackman, T.R., Sadlier, R.A. and Whitaker, A.H. 2012. Revision of the giant geckos of New Caledonia (Reptilia: Diplodactylidae: Rhacodactylus). Zootaxa(3404) , p.1–52.

Jourdan, H., Sadlier, R.A. and Bauer, A.M. 2000. Premières observations sur les conséquences de l’invasion de Wasmannia auropunctata 1863 (Roger) sur les prédateurs supérieurs dans les écosystèmes Néo-calédoniens. Actes des collectes insectes sociaux(13) , p.121-126.

Jourdan, H., Sadlier, R.A. and Bauer, A.M. 2001. Little Fire Ant Invasion (Wasmannia auropunctata) as a threat to New Caledonian lizards: Evidences from a sclerophyll forest (Hymenoptera: Formicidae). Sociobiology(38) , p.283-301.

Thibault, M., Brescia, F., Vidal, E. and Jourdan, H. 2017. Invasive rodents, an overlooked threat for skinks in a tropical island hotspot of biodiversity. New Zealand Ecological Society(41) , p.74-83.

Palmas, P., Jourdan, H., Rigault, F., Debar, L., De Meringo, H., Bourguet, E., Mathivet, M., Lee, M., Adjouhgniope, R., Papillon, Y. and Bonnaud, E. 2017. Feral cats threaten the outstanding endemic fauna of the New Caledonia biodiversity hotspot. Biological Conservation(214) , p.250-259.

Experts


Assessor(s): Sadlier, R., Bauer, A., Jourdan, H., Astrongatt, S., Deuss, M., Duval, T., Bourguet, E., McCoy, S., Bouteiller, A., Lagrange, A.

Reviewer(s): Cox, N.

Contributor(s): Whitaker, A.

Facilitator(s): Tanguy, V., Lietar, J., Warimavute, G.


Geographical distribution