Taxonomy

endemique
protegee
UICN

Common name :

le Gécko Géant crêté

Red List Status -

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

Protected species -

in Southern Province , in Northern Province

Description

 

Description:

A moderately large species of gecko growing to a body length of 130 and with a tail approximately the length of the body; moderately broad toes with basal webbing; a row of elongate soft spiny scales either side of the head and neck from the behind the eye to just above the shoulder forming a raised crest; and a colour pattern that is highly variable, ranging from uniformly light to dark brown, or with broad pale vertebral stripe consisting of a series of large, broken blotches.

 

Natural distribution:

Known from a few scattered locations in the central and southern regions of the main island, Ile des Pins, and Belep Islands.

Distribution within Province Sud: On the main island recorded from Riviére Bleue and the adjacent Pourina river valley, Mt Koghis, Mt Ouin, and the Isle des Pines (but not its offshore islands).

 

Distribution within Province Nord: Known from the Belep Islands off the northern tip of the main island, and possibly the east coast based on historical records in the late 1800’s from ‘Kanala’.

 

Habitat:

Humid forest.

 

Threats:

  • high level of threat to all low-mid elevation 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 to closed forest on coastal lowlands of the Ile des Pins through loss, modification and fragmentation of forest habitat to local agriculture.

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

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

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

 

Conservation Status: Vulnerable

 

Rhacodactylus ciliatus is recorded from closed forest habitat or adjacent edge vegetation at four locations in the south of the Grand Terre. Those at Mt Koghis clearly represent an isolated sub-population and research in progress shows significant genetic sub-structuring between individuals from Mt Ouin and Riviére Bleue, indicating the possibility of further discrete sub-populations in this region, as do those from the Isle of Pins and Belep Island.

 

The species distribution is small with a total area of occupancy of <500km2, and its overall range and area occupancy is considered unlikely to change significantly. These factors in combination with the range of potentially high level threats identified above and the specialised biology of the giant geckos in the genus Rhacodactylus, indicate Rhacodactylus ciliatus conservatively satisfies the criteria for the species to be categorised as Vulnerable, but could be moved to a higher level of conservation concern given the number and intensity of those threats. The sub-populations on the Belep Islands and on the Ile des Pins are particularly at risk given their small range and the increased impact of threats on insular sub-populations.

 

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


Correlophus ciliatus is listed as Vulnerable because it has a restricted distribution and there is continuing decline in the extent and quality of its habitat and number of mature individuals.

Geographical area


This species is endemic to New Caledonia. It occurs in Grande Terre and Ile des Pins. On Grande Terre, it was known from localities widely scattered across the southern half of the island (Canala to Rivière Bleue) and it has been found recently in the northern part (Néhoué). It is possible that this species occurs in intervening forested areas. It occurs at elevations between 150 and 1,000 m. The extent of occurrence is estimated to be 5,861 km2 and the area of occupancy is estimated to be 44 km2.

Population


There are no quantitative data on population size or trends. It is presumed to have suffered a substantial reduction in population size and extent in the past through habitat loss associated with logging, wildfires and the clearance of low and mid-elevation forests for agriculture.

Habitat


This species inhabits coastal forests, closed humid forests and montane forests. It is nocturnal and arboreal. It shelters by day in tree crevices and holes or amongst dense foliage, and forages at night in the canopy.

Threats


The main threats to this species are predation by rodents (Thibault 2017) and the illegal collection and trafficking at accessible location. Other threats are the loss or degradation of habitat from wildfires, the impact of the introduced ant, Wasmannia auropunctata (Jourdan et al. 2000, 2001) and the predation by feral cats (Palmas 2017).

Conservation


Protected in Province Sud under Code de l'environnement de la Province Sud (Délibération No. 25-2009/APS, 20 March 2009) and in Province Nord under Code de l'environnement de la Province Nord (Délibération No. 306-2008/APN, 24 October 2008). This species is present in Parc Provincial de la Rivière Bleue and in Pic du Grand Kaori reserve but it is not known to occur in other protected areas. No active conservation management is currently being undertaken for this species.

Bibliography


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.

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.

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

Seipp, R., and Henkel, F.W. 2000. Rhacodactylus: biology, natural history and husbandry.

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.

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.

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.

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.

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): Lietar, J., Warimavute, G., Tanguy, V.


Geographical distribution