Range Contractions in the Critically Endangered Seychelles Terrapins [Pelusios Spp.)
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Oryx Vol 35 No 4 October 2001 Range contractions in the Critically Endangered Seychelles terrapins [Pelusios spp.) J. Gerlach and L. Canning Abstract The status of the Seychelles endemic terra- and 6.02 ha for P. castanoides and P. subniger, respect- pins is reviewed based on field-surveys. Pelusios ively) that have decreased by over 50 per cent in recent castanoides intergularis and P. subniger parietalis are years. Conservation of these species requires both the confined to a small number of marshes and rivers. All protection of wetland habitats and the establishment of the sites occupied are limited in area (<4.5 ha) and new populations in protected areas. A captive breeding under threat from drainage, predation and invasion by programme has been established with the aim of alien water plants. The smallest populations are unlikely reintroducing juveniles into secure reserves. The to be viable in the long-term. Both species can be endemic species P. seychellensis may be extinct. categorized as Critically Endangered using the IUCN Red List categories, with highly restricted ranges (2.89 Keywords Marsh, Pelusios, river, Seychelles, terrapin. tions in several lowland rivers and marshes (Bour, Introduction 1983). There are also isolated reports from mid-altitude Three endemic terrapin taxa have been recorded from suburban areas (Le Niol and La Misere; Gerlach & Seychelles. Two of these, Pelusios subniger parietalis and Canning, 1996). Pelusios castanoides has been recorded P. castanoides intergularis, are subspecies of African from the islands of Mahe, Cerf, Praslin and La Digue, species, whereas the third is an endemic species, P. subniger from Mahe, Cerf, Praslin, La Digue and P. seychellensis, closely related to P. castanoides. Both Fregate, and unspecified taxa on St Anne, Silhouette, P. subniger and P. castanoides have been introduced to Cousin, Aride and Curieuse (Bour, 1983; Gerlach, other island groups (Bour, 1983,1984) but appear to be a 1997a). There are no published records from the other natural component of the Seychelles fauna. Their pres- islands that have, or had, marshy areas (North, Cousine ence in the islands is probably a result of colonization and Grande Soeur). during the Wisconsin glacial period (15,000 years ago) The aim of this paper is to review the status of when sea levels were some 120 m lower than at present Seychelles terrapins based on studies that we carried out (Taylor et ah, 1979) and the submarine banks of the in 1996-1999, and to highlight conservation measures Seychelles plateau and Amirante banks would have required for their survival. provided a land chain from Africa and Madagascar. No other terrapin genera are native to the islands. Methods There is little information available on the distribu- tion, population size or biology of terrapins in Sey- The largest areas of marsh habitat, which were expected chelles. Pelusios seychellensis is known only from three to support the most important terrapin populations, specimens collected from an unknown locality in 1895 occurred on the larger islands of Mahe, Silhouette, (Siebenrock, 1906; Bour, 1983, 1984) and one record Praslin and La Digue. We therefore concentrated our attributed to this species in 1994 (Gerlach and Canning, work on these islands, but we also collected historical 1996). Research into the status of P. seychellensis was and recent records from smaller islands. From 1 : 10,000 recommended as a high priority in the 1989 Tortoise and survey maps we identified 59 marsh sites and estimated Freshwater Turtle Action Plan (Swingland & Klemens, their areas (Table 1). Trapping studies were carried out 1989). No further specimens have been located and its at 10 sites on Mahe, Praslin and La Digue (Table 2), taxonomic status is unclear. selected for accessibility, specific habitat features or Both P. subniger and P. castanoides appear to be because the presence of terrapins had been reported. An widely distributed in Seychelles (Fig. 1), with popula- additional 18 sites were examined but trapping was not carried out, because either there were no suitable trap sites or problems with access would have prevented J. Gerlach (Corresponding author) and L. Canning 133 Cherry Hinton the repeat visits required for trapping. The remaining Road, Cambridge CB1 7BX, UK. E-mail: [email protected] 31 small marshes were not investigated and terrapin Revised manuscript accepted for publication 11 July 2001 313 © 2001 FFI, Oryx, 35(4), 313-321 Downloaded from https://www.cambridge.org/core. IP address: 170.106.33.14, on 28 Sep 2021 at 22:30:25, subject to the Cambridge Core terms of use, available at https://www.cambridge.org/core/terms. https://doi.org/10.1046/j.1365-3008.2001.00203.x 314 J. Gerlach and L. Canning 1 55"3 y Aride—«• Curieuse Grande Soeur Anse Kerlan ^^ ^L^ MareSoupape ™ Cousin—• North Cousine ^~-La Digue T >id Anse Silhouette Praslin »>» 0$B$fcr—La Passe Grande Barbe 4"30— North-east Point R. Mare Anglaise tea, Q t. Anne Baau Valloii \ \ ••••jWF> /^ xCerf - ^ Roche Caiman Fregate ^__Anse Royale Anse La Mouche\^BBF Anse aux Poules Bleus—atmBBP —^Anse Forbans i Fig. 1 The islands of Seychelles, with marshes in which terrapius have been 20 km trapped or observed. presence was evaluated from information provided by habitats were further categorized as open (permanent local residents. woodland river or marsh containing Eleocharis or Typha In order to estimate population sizes a mark-recapture reed-beds), seasonal (subject to annual drying out) or trapping system was used with baited funnel traps invaded (covered by water lettuce Pistia stratiotes). Any (Legler, 1960). Tinned tuna in soya oil was used as bait obvious pollution (e.g. rubbish and organic waste) for most of the traps, although a small number were was noted. The numbers of aquatic invertebrates were baited with coconut, snails or chicken entrails to assessed in 31 marshes by counting all taxa in investigate the effects of different baits on trap success. 10 x 1 sq m quadrats. Terrapins were only caught in fish-baited traps and so The study was undertaken during both dry (July- fish was used exclusively after the first week. Ten traps September 1996, July 1997) and wet (January 1997, were widely distributed within each marsh, and were January 1998, January 1999) seasons. Numbers of trap set approximately 5 m apart along river banks or days are given in Table 2. The initial period of margins of pools. The captured terrapins were marked trapping in 1996 was the most intensive; subsequent with individual marginal notches, using a hand-saw, to trapping was carried out opportunistically. These allow identification on subsequent recapture. These subsequent trapping periods concentrated on sites shallow (2 mm) notches have been used for many years where terrapins were recorded in the initial period. in chelonian marking and have no effect on health or Within the Beau Vallon - Riviere Mare Anglaise survival (Cagle, 1939). marsh system on Mahe a number of the initial trap The trapped terrapins were sexed and examined for sites were later found to be inappropriate (e.g. in any obvious signs of damage, and all taxonomically exposed sites, saline or rapidly running water). These useful external characteristics (Bour, 1983) were recor- sites were not used again until January 1999 when all ded to the nearest millimetre. Females have short tails, the trap positions in the marsh system were repeated, reaching forward to the suture between the 11th and 12th confirming the unsuitability of some for catching marginals, and a concave anal notch; whereas males terrapins. Opportunities for trapping at Anse Kerlan have longer tails, reaching to the 10-1 lth marginals, and on Praslin were more limited and trapping effort a straight sided anal notch. Individuals over 10 cm varied but was maintained at a minimum of 80 trap straight carapace length could be sexed in this way, days per trapping period. whereas those below this size could not be sexed with confidence and were categorized as 'juveniles'. In addi- tion, privately kept captive terrapins were examined. Results Study sites were categorized as high altitude marsh We only discovered terrapins in lowland habitats (500 m above sea level), mid-high altitude river (>200 m (Table 1), with P. castanoides in woodland rivers above sea level) or lowland habitat. The lowland and reed-beds and P. subniger in marshes. Relatively © 2001 FFI, Oryx, 35(4), 313-321 Downloaded from https://www.cambridge.org/core. IP address: 170.106.33.14, on 28 Sep 2021 at 22:30:25, subject to the Cambridge Core terms of use, available at https://www.cambridge.org/core/terms. https://doi.org/10.1046/j.1365-3008.2001.00203.x https://doi.org/10.1046/j.1365-3008.2001.00203.x Downloaded from Table 1 Suitable terrapin habitat on the larger Seychelles islands and records of terrapin populations from Honegger (1966), Bour (1984) and the present study. Marshes where we carried out https://www.cambridge.org/core trapping for terrapins are marked with an asterisk, and habitat areas supporting terrapins are in italics. Habitat area (ha) in 1999 Low altitude marsh Present Mid-high High-altitude Pond snails Island Marsh Historical records study Species Open Seasonal Invaded altitude river marsh (per m2) Mahe Beau Vallon* 1962 (Bour, 1984) castanoides 0.11 6.4 Mare Anglaise* 1983 (Bour, 1984) castanoides 0.07 0.05 366.2 . IPaddress: North-East Point 1983 (Bour, 1984) 1.67 0.39 2.10 0 Victoria 0.05 0.1 Roche Caiman O castanoides 0.24 2.66 12.0 Anse Aux Pins 0.01 0.40 170.106.33.14 0 Anse Royale* 1983 (Bour, 1984)- - castanoides 0.06 0.09 0.09 0 1994 (pers. obs.) Anse Forbans* 1983 (Bour, 1984) o subniger 0 4.52 0.02 0 , on Anse Marie Louise* 0.01 0 Police Bay 1964 (Bour, 1984) 0.05 28 Sep2021 at22:30:25 Petite Police 1983 (Bour, 1984) 0.30 Anse Intendance 1983 (Bour, 1984) 0.05 3.6 Anse Takamaka 1983 (Bour, 1984) 0.02 1.78 0 Anse Gaulettes 0 1.50 Val Mer 0 0.09 Anse Gouvernment 1.50 1.3 , subjectto theCambridgeCore termsofuse,available at A.