WWW.IRCF.ORG/REPTILESANDAMPHIBIANSJOURNALTABLE OF CONTENTS IRCF REPTILES & AMPHIBIANSIRCF REPTILES • VOL15, N&O AMPHIBIANS4 • DEC 2008 189 • 20(2):44–52 • JUN 2013
IRCF REPTILES & AMPHIBIANS CONSERVATION AND NATURAL HISTORY
TABLE OF CONTENTS
FEATURE ARTICLES The Lesser. Chasing Bullsnakes (AntilleanPituophis catenifer sayi) in Wisconsin: Iguana on St. Eustatius: On the Road to Understanding the Ecology and Conservation of the Midwest’s Giant Serpent ...... Joshua M. Kapfer 190 . The Shared History of Treeboas (Corallus grenadensis) and Humans on Grenada: AA Hypothetical2012 Excursion ...... Population Status UpdateRobert W. Henderson 198 RESEARCH ARTICLESand Causes for Concern . The Texas Horned Lizard in Central and Western Texas ...... Emily Henry, Jason Brewer, Krista Mougey, and Gad Perry 204 . The Knight Anole (Anolis equestris) in Florida 1 2 3 ...... AdolpheBrian O. J. Debrot Camposano,, KennethErik B.L. Krysko, Boman Kevin ,M. and Enge, Hannah Ellen M. Donlan, Madden and Michael Granatosky 212 1Institute for Marine Research and Ecosystem Studies (IMARES), Wageningen UR, P.O. Box 57, 1780AB, Den Helder, The Netherlands ([email protected]) CONSERVATION ALERT 2Agriculture Department of St. Eustatius, Oranjestad, St. Eustatius ([email protected]) . World’s3St. Eustatius Mammals Nationalin Crisis ...... Parks Foundation, Gallows Bay, St. Eustatius ([email protected]) 220 . More Than Mammals ...... 223 . The “Dow Jones Index” of Biodiversity ...... 225
HUSBANDRY . Captive Care of the Central Netted Dragon ...... Shannon Plummer 226 Abstract.—To assess the status and current population densities of the endangered Lesser Antillean Iguana (Iguana delicatissima) onPROFILE the island of St. Eustatius, we spent more than 80 h searching for iguanas and covered more than . Kraig Adler: A Lifetime Promoting Herpetology ...... Michael L. Treglia 234 63 km of trails and tracks — but found only 22 iguanas, for an overall average of 3.7 h per iguana. Overall popula- tion density wasCOMMENTARY 0.35 iguanas per hectare, which represents 0.5–1.0% of densities documented elsewhere in healthy populations. Population. The Turtles densities Have Been Watching have declinedMe ...... across all habitats since the last assessment Eric in Gangloff 2004. 238 The lack of nesting sites and high BOOKiguana REVIEWmortalities due to anthropogenic causes were the two core factors limiting recovery of iguanas on St. Eustatius.. OurThreatened principal Amphibians recommendations of the World edited by S.N. are Stuart, to: M. (a) Hoffmann, Train J.S. and Chanson, equip N.A. border Cox, officials to prevent potential entry of mongooses R.and Berridge, Green P. Ramani, Iguanas and B.E. from Young ...... neighboring islands; (b) implement enforcement Robert Powell and 243 upgrade protective
legislation; (c) developCONSERVATION and maintain RESEARCH new REPORTS: additional Summaries nesting of Published habitat, Conservation a measure Research Reports that is...... both easy and 245 inexpensive; and (d) establish a programNATURAL to HISTORY promote RESEARCH “iguana-friendly” REPORTS: Summaries gardens of Published as the Reports main on Natural means History of ...... reducing cumulative 247 mortality. NEWBRIEFS ...... 248 Finally, we propose EDITORIAL the development INFORMATION of ...... an in situ husbandry and breeding program to help bolster 251 the overall recov- ery program, a moveFOCUS that ON CONSERVATIONalso would benefit: A Project islanders You Can bySupport offering ...... a relaxed setting in which they could 252 better learn to appreciate this emblematic island species.
Keywords: Lesser Antillean Iguana, Iguana delicatissima, St. Eustatius, conservation, status Front Cover. Shannon Plummer. Back Cover. Michael Kern Totat et velleseque audant mo Totat et velleseque audant mo he Lesser Antillean Iguana, Iguanaestibus delicatissima inveliquo velique (Laurenti rerchil estibus inveliquo velique rerchil erspienimus, quos accullabo. Ilibus erspienimus, quos accullabo. Ilibus T1768)(Fig. 1), has a very limitedaut dolor distribution apicto invere pe dolum in the aut dolor apicto invere pe dolum Lesser Antilles and is gradually beingfugiatis extirpated maionsequat throughouteumque fugiatis maionsequat eumque moditia erere nonsedis ma sectiatur moditia erere nonsedis ma sectia- its range due to three principal causes:ma derrovitae Invasive voluptam, predators, as quos tur ma derrovitae voluptam, as habitat loss, and hybridization withaccullabo. invasive Green Iguanas (I. iguana). Of the six islands of the Dutch Caribbean, the species is today found only on St. Eustatius, where it is the largest native terrestrial animal and a prime emblem of the island’s biodiversity. Populations have been extirpated on Antigua, Barbuda, St. Kitts and Nevis, Les Îles des Saintes, Marie Galante, as well as on St. Martin as recently as 1996 (Breuil 2002). Of the 13 remaining island populations, only two (Dominica and Guadeloupe) exceed the long-term mini- mum viable population (MVP) size of 5,000 individuals, and Fig. 1. The Lesser Antillean Iguana (Iguana delicatissima) is gradually being six are critically endangered. While the species’ precarious sta- extirpated throughout its range. Of the six islands of the Dutch Caribbean, tus would appear to emphasize the need for scientific study, the species is today found only on St. Eustatius, where it is the largest life history information on I. delicatissima remains very lim- native terrestrial animal. Photograph © John S. Parmerlee, Jr. ited (Pasachnik et al. 2006, Knapp 2007).
Copyright © 2013. Adolphe O. Debrot. All rights reserved. 44 DEBROT ETAL. IRCF REPTILES & AMPHIBIANS • 20(2):44–52 • JUN 2013
Fig. 2. Map of St. Eustatius showing 91 locations at which one or more iguanas were documented in 2012 during dedicated transect surveys (◊) (N = 14), during opportunistic sightings (∆) (N = 47), from interviews (+) (N = 24) and as recent nest digging locations (°) (N = 6). Map © E. Dijkman.
Past population size estimates for St. Eustatius were about Kitts (about 15 km away) and Saba (about 25 km away). It 300 animals in 1992, less than 300 animals in 2000, and lies in the northeastern trade winds and experiences hurri- about 425 (275–650) animals in 2004 (Fogarty et al. 2004). cane conditions once every 4–5 years. Air temperatures on The species is listed by the IUCN as “endangered” (Breuil et St. Eustatius average 26.9 °C, with the hottest temperatures al. 2010). In light of the growing list of declines and threats (28.0 °C) occurring in July, August, and September. The throughout its range, Powell and Henderson (2005) argued annual average rainfall is about 990 mm/yr. The island con- that, if not for scattered surviving populations on multiple sists of three main geomorphological zones: The northwestern islands, the status listing of “critically endangered” would hills, the central plains, and the Quill, a dormant volcano in necessarily apply. The objective of this study was to provide a the southeastern section of the island. The flora comprises new population assessment for this endangered species on St. about 505 species of plants, for which Freitas et al. (2013) Eustatius and provide conservation recommendations. recently described 13 (semi)natural vegetation types that are St. Eustatius forms part of the inner volcanic arc of the distributed in four main and 16 sub-landscape types. All areas Lesser Antilles and has a surface area of about 21 km2. The continue to be heavily impacted by feral livestock. The island capital and only town is Oranjestad with about 4,000 inhab- has three large terrestrial protected areas. Two of these are itants. The island is situated roughly on a line between St. in the northwestern hills (Boven: 3.30 km2 and Signal Hill: 45 DEBROT ETAL. IRCF REPTILES & AMPHIBIANS • 20(2):44–52 • JUN 2013
Fig. 3. A female Iguana delicatissima adapted to the suburban life of St. Eustatius. Photograph © Hannah Madden.
0.44 km2) and one circles the 600-m Quill, down to altitudes Preliminary analyses indicated very low sighting frequencies, of about 250 m ASL for a total surface area of approximately such that meaningful density estimates and statistical analy- 2.14 km2. These protected park areas are all managed by sis were not possible using the small (50-m) transect method the St. Eustatius National Parks Foundation (STENAPA) chosen. We therefore estimated density and calculated density (MacRae and Esteban 2009), which was a key supporter of indices by including the distances linking the (short) tran- our iguana work. sects (i.e., all distance and time spent searching in the field). Densities were expressed both in terms of iguanas per unit Methods time spent searching, following Fogarty et al. (2004) and Dedicated iguana surveys.—Iguana surveying methods remain Reichling (2000), and in terms of iguanas per hectare. problematic even in high density populations, leading to only rough estimates of population size and density (e.g., Lorvelec Questionnaire and opportunistic sightings.—Aside from et al. 2007). We chose to apply a line transect method. The directed iguana surveys, opportunistic sightings were solic- island was divided into “habitat” sectors following Fogarty et ited from inhabitants of the island, using a simple protocol al. (2004). Iguana surveys were conducted between March to structure information collection. All such sightings, as and November 2012 at 1000–1400 h to coincide with peak well as sightings we made outside field sampling sessions, daily activity (Pasachnik et al. 2002). We felt that in most were mapped to provide additional indications of the distri- habitats we could reliably find iguanas to 5 m on each side of bution and abundance of iguanas on the island. the transect. In this, counts were conducted using 10-m wide transects of 50-m lengths. Replicate transects were separated Results and Discussion by a minimum of 50 m. All positions were marked by GPS Documented distribution.—Figure 2 shows the locations of beginning and endpoints. iguanas sighted during dedicated searches as well as all oppor- Field data were collected during a total of 39 excursions tunistic sightings recorded. Our field surveys were conducted during which two to more than 10 transects were surveyed. during 39 different survey sessions, during which a total
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Table 1. Iguana sampling effort in the different areas of the island and the number of iguanas detected, expressed as iguanas per hour searched and search time per iguana detected. Results by Fogarty et al. (2004) are included for comparison.
Sector Number Time Distance Area Iguanas Iguanas Iguanas h/ 2004 of Visits (h:min) (m) (m2) Seen /ha /h iguana h/iguana
Quill crater 2 3:15 1,400 14,000 0 0.00 0 indef. — Quill out. slopes 5 17:38 11,700 117,000 1 0.09 0.06 17.63 8.30 Quill foothills 6 9:03 5,250 52,500 1 0.19 0.11 9.05 — Island estates 2 4:10 3,600 36,000 6 1.67 1.44 0.69 0.20 Central plains 4 3:35 6,500 65,000 0 0.00 0.00 indef. — Northern Hills 10 28:07 27,222 272,220 2 0.07 0.07 14.06 1.80 Border N. H. 6 9:49 6,500 65,000 9 1.38 0.92 1.09 — Oranje Bay 4 4:40 1,500 15,000 3 2.00 0.64 1.56 0.40
Total 39 80:21 63,672 636,720 22 0.35 0.27 3.70
63,672 m of trails and transects were walked and 80 h and 21 or (c) the central plains (Cultuurvlakte). We did conduct min were spent searching for iguanas in the field. Based on directed sampling in all three of these habitat zones. We fur- locations from which iguanas could be documented (either ther sampled the escarpments of Lower Town (Oranje Bay) from transect counts, opportunistic sightings, from inter- as a distinct habitat, whereas Fogarty et al. (2004) labeled this views, or as evidenced from recent nest digging activity), the area as part of the “central plains.” species can be seen to be relatively widely distributed on the Iguanas were not detected in the Quill crater or on the cen- island (Fig. 2). Iguanas certainly are not relegated to faraway tral plains, and these results correspond closely to the findings/ places; if essential conditions are met, they could thrive in the observations of Fogarty et al. (2004). The Quill crater ridge central inhabited part of the island (Fig. 3). lies at a minimum altitude of 378 m, whereas the crater floor lies at about 278 m above sea level. These areas often are cov- Dedicated iguana sightings and relative density.—We detected ered in clouds and fog, and according to Veenenbos (1955), only 22 iguanas for an average effort of 3.70 h for each iguana the amount of rainfall on the Quill (above 400 m) averages detected (Table 1). Fogarty et al. (2004) spent no time sam- 1,500–2,000 mm per year. The moisture and lower tempera- pling directly in either (a) the lower Quill foothills, (b) the ture probably makes this habitat less than ideal for iguanas. The border region between the northern hills and the central plain, central plains consist of areas with low shrubs and grassland that provided iguanas with few refugia in the form of either high vegetation or boulder fields with crevices. Although the habitat would otherwise be suitable, iguanas appear not to occur in these areas. The lower foothills of the Quill were not sampled by Fogarty et al. (2004). However, we spent 9 h and 3 min searching in these areas and found only one iguana, leading to the conclusion that iguanas do occur here but at exceedingly low densities (Table 1). As Fogarty et al. (2004) indicated, the northern hills are particularly important iguana habitat; con- sequently, we spent more than 28 h during 10 different excur- sions into the area and included both hills sampled by them (Boven and Gilboa) in addition to Signal Hill and natural habitat within the NUSTAR industrial complex. However, again, we found very few animals. One important natural iguana habitat was the zone with Fig. 4. The favorite natural iguana habitat on St. Eustatius is an ecologi- cal discontinuity where the northern hills abut onto the central plains. vegetated and boulder-strewn slopes where the northern hills Photograph © Adolphe Debrot. abut onto the central plains (Fig. 4). These areas had the 47 DEBROT ETAL. IRCF REPTILES & AMPHIBIANS • 20(2):44–52 • JUN 2013
Fig 5. Hatchling Iguana delicatissima predation by the native Red-bellied Racer (Alsophis rufiventris). St. Eustatius, January 2008. Photograph © Hannah Madden. third-highest estimated iguana densities (1.38 iguana/ha) and Comparison to the 2004 survey.—In 2004, Fogarty et al. saw second-highest encounter rates (1.09 h/iguana) of all habitats more iguanas during considerably less time spent in dedi- studied. These areas essentially constitute a band not much cated surveys. Across the board, our indices of density were more than 100 m wide running along the base of the hills much lower than those of Fogarty et al. (2004), suggesting from Signal Hill in the west to Gilboa in the central-eastern lower densities of iguanas across the island (Table 1). Whereas part of the island. Iguanas often exploit and seek out disconti- Fogarty et al. (2004) indicated that their lack of experience nuities in habitats, and this area apparently offered the iguana in spotting iguanas possibly meant that their relative density the best of both the plains (sun and potential nesting sites) estimates might have been on the low side, in our case, both and the hills (escarpments and crevices for escape and shelter). researchers are good iguana-spotters, the lead author having These areas also had plenty of Acacia Trees (Vachellia), which more than 40 years of iguana-spotting experience. While pos- iguanas cherish as food (particularly the flowers), as well as sible that we actually missed animals (particularly juveniles) dense Calabash Tree (Crescentia cujete) groves in which they in the narrow transects we surveyed, we tended to sample in like to hide and where they were frequently seen. the best habitats available to iguanas in the chosen areas, and The highest iguana densities and sighting rates were likely included iguanas that fell just outside the 10-m tran- found in the estate subdivisions concentrated along the north- sect width when they were observed. Therefore, we believe western lower flanks of the Quill and along the escarpment that our density estimates are most likely to err on the high and cliffs between the Oranjestad harbor and the town located side and feel confident in concluding that iguana numbers above the cliffs. In the latter area, the relatively high density on Statia have taken a turn for the worse since the survey by (2.00 iguanas/ha) and sighting frequency (1.56 iguana/h) was Fogarty et al. (2004). largely due to a small concentration (possibly up to seven dif- The Smoke Alley population described by Fogarty et ferent iguanas) living between the STENAPA office in the al. (2004) as flourishing, and then numbering between 10 harbor and the Roman Catholic church directly above on the and 50 animals is no longer present. This population used cliff. In the rest of the area, iguanas were virtually absent. to be situated around the Kings Well Hotel, which started a
48 DEBROT ETAL. IRCF REPTILES & AMPHIBIANS • 20(2):44–52 • JUN 2013 breeding population that was subsequently released around 2000. While at least one animal is present at the Old Gin House and was observed opportunistically during this study, and about seven individuals still inhabit the cliffs behind the STENAPA headquarters, this once promising population has all but disappeared. The habitat quality of this erosion-prone escarpment area has all but been destroyed by extensive mats of the invasive Mexican Creeper vine (Antigonon leptopus), locally known as “Corallita.” These areas, formerly without Corallita, would have been among the best nesting habitat available to iguanas in the central section of the island. The available habitat also is very narrow, pinned in between the busy harbor road along the waterfront and the town directly above and along the cliff edge. The area is prime waterfront and in the long-term will be used for waterfront real estate Fig. 6. The most common form of fencing used on St. Eustatius and quite dangerous to adult gravid female iguanas, whereas less expensive wide- development. Its long-term prospects as iguana habitat are meshed “goat wire” would be equally suitable Photograph © Adolphe limited. Debrot. In contrast, the estates development area of the island continues to harbor substantial numbers of iguana. This area current population size certainly lies on the low side of this showed the overall highest encounter rate (0.69 h/iguana) range. It is in any case far below the required minimum viable and second-highest density estimate (1.67 iguana/ha). It is population size (MVP) of 5,000 animals and means that the characterized by spacious villas situated on large lots. Many iguana is critically endangered on St. Eustatius. Nevertheless, vacant lots remain undeveloped and have high semi-natural islanders still report seeing iguanas relatively regularly. Of the dry-evergreen vegetation. At least 50% of the villas are not 53 islanders interviewed, 30 persons (56%) reported seeing permanently occupied, inhabited only 3–6 months of the year iguanas at or near their residence within the last three months by foreign owners. Iguanas appear largely absent from lots and 14 (26%) within the last week. This could be based on a with dogs, and about 50% of estate owners (10 of 19) kept small number of mobile animals seen by many people, result- dogs. At least one lot was observed to have iguanas despite ing in a false sense of abundance — and could undermine any a dog being present; iguanas stayed near the fence-line and local sense of the real urgency required for effective conserva- could escape from the dog by climbing up or going through tion and recovery of this species. the fence. The importance of the estates area as a refuge for iguanas is hence dependent largely on the happy circumstance Conclusions and Recommendations of undeveloped lots, which serve as the main habitat refuge, The numbers of iguanas on St. Eustatius remain disappoint- and a number of villa owners who do not keep dogs and/or ingly low. After an apparent upturn between 1999 and 2004 are iguana-aware. Suitable nesting habitat was very scarce in (Fogarty et al. 2004), the status of the species has quite con- the estates area. vincingly taken a turn for the worse. While natural mortality certainly includes predation by native predators such as Red- Population densities and size.—Under favorable circumstances, tailed Hawks (Buteo jamaicensis), American Kestrels (Falco iguana populations can attain densities in excess of 30/ha sparverius), or Red-bellied Racers (Alsophis rufiventris; Fig. (Breuil 2002, Knapp and Perez-Hydrich 2012). Our density 5), the principal problems faced by iguanas on St. Eustatius estimates for St. Eustatius varied between zero and a maxi- appear to be high levels of human-induced mortality, nota- mum of 2.00 for an overall average of 0.35 iguanas/ha. These bly dogs, entanglement in fencing (Fig. 6), abandoned cis- densities are clearly very low (0.5–1.0%) compared to poten- terns, and traffic (Debrot and Boman 2013b), as well as low tial densities under ideal circumstances. Iguanas generally are availability of nesting habitat (Debrot et al. 2013). However, gregarious animals, and probably thrive best under higher several measures were identified that, if implemented, could densities than observed in St. Eustatius. Aside from being a certainly help safeguard or even improve the situation of the major threat to the species, these low densities, make den- species. sity estimates and analyses problematic (too many zeros), and Two massive threats to iguanas elsewhere, and the constitute a major impediment for studies of critical aspects most important causes for the species’ extirpation on islands of the biology and ecology of the species. Our results show throughout its current and former range, are predation by that compared to 2004, when the population was estimated invasive Small Indian Mongooses (Herpestes javanicus), and to number 425 (275–650) animals (Fogarty et al. 2004), hybridization with Green Iguanas (Iguana iguana). Green
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Fig. 7. The Pandanus, a hardy garden ornamental with sharply serrated leaves, is cherished by iguanas as a shelter site. Photograph © Adolphe Debrot; insert © Robert Powell.
Iguanas are present and abundant on Saba (which supports problem (Debrot and Boman 2013), the number of animals an endemic population of that species) and St. Maarten on the island is so small that no hunting can be warranted. (where the niche formerly occupied by native Lesser Antillean With compliance already high (hunting is very limited and Iguanas has been occupied by introduced Green Iguanas), hardly profitable), renewed enforcement of the legislation whereas mongooses are abundant on both St. Kitts and St. should be preceded by an information campaign to give due Maarten. St. Eustatius has regular inter-island traffic with all warning. three of these islands, and the risk of accidental introductions Debrot et al. (2013) confirmed a virtual lack of suitable of either of these two scourges is high. Keeping them out of nesting sites in most areas of the island. Those sites that are St. Eustatius in the long-term can only be achieved with better present are additionally vulnerable to large numbers of tram- legislation, awareness, and training of and control by border pling livestock or potential nest predators. Good nesting sites and customs personnel. Currently, no legislation prevents the are relatively easy to establish, maintain, and protect. They importation of Green Iguanas or mongooses. Therefore, legis- also can form pivotal sites for research and serve as a source of lating the prohibition of importing either species is critical. young animals for headstarting, breeding, and other studies. The Lesser Antillean Iguana has been listed as a protected STENAPA currently is using the recommendations of this species in the “Statia Flora and Fauna Ordinance” of 1997 study to advise estate developers on the need to provide safe (MacRae and Esteban 2009), which stipulates maximum nesting sites for iguanas. penalties of up to 1 month of incarceration and fines up to Knapp and Perez-Heydrich (2012) noted that, if fac- 5,000 guilders per infraction. While hunting is only a small tors such as degraded nest sites and killing by non-native
50 DEBROT ETAL. IRCF REPTILES & AMPHIBIANS • 20(2):44–52 • JUN 2013 mammalian predators are mitigated, moderately disturbed, “kinds” of iguanas occurred on the island. This overall lack human-occupied areas can be managed as corridors or buf- of understanding detracts from the resident public’s sense of fer zones for I. delicatissima in increasingly fragmented land- urgency for protection. People experience iguanas as being scapes. Along those lines, one of the important habitat areas relatively “abundant” (also elsewhere) and conservation con- for the iguana at present is the estates development area of the cerns are believed to have been exaggerated by “over-zealous” island. The owners of these estates are largely retirees, many of environmentalists. whom, with the right information, might be willing to devote A second aspect of awareness is that in general, iguanas a little attention to the critical matter of survival of the larg- evoke fear and disgust in many local inhabitants. Very few est and most spectacular native terrestrial vertebrate of Statia. have experienced iguanas as gentle and beautiful animals One measure might be to phase out the use of harmonica- that deserve a safe spot in every yard. Awareness can best be wire (chain-link) fencing, which is dangerous to iguanas due stimulated by taking tame pet iguanas to schools for chil- to the threat of entrapment (Debrot and Boman 2013b). dren to experience first-hand. Therefore, current educational In response to our findings, the Department of Agriculture efforts by STENAPA include the species, and these should be Animal Husbandry and Fisheries (LVV) of St. Eustatius has funded and preferably formalized as part of the educational already started to phase out its use of this type of wire fencing curriculum. (Director R. Hensen, pers. comm.). We hope that private cit- Finally, establishing a small local husbandry project could izens will follow suit. The habitat value of the estates area can play a decisive role in supporting an iguana action plan (Fig. also be improved simply and inexpensively by creating suit- 8). Captive husbandry and/or breeding and the facilities able nesting habitat for resident iguanas (fenced-off to keep entailed could provide not only a venue for critical scientific dogs out) and by encouraging owners to plant suitable bushes studies but also function as an ideal setting from which to near fence lines (so iguanas can more easily escape predators). promote awareness of school children and the general pub- Suitable plants would include dense, thorny ornamental lic via direct contact with tame animals. So, local husbandry Pandanus (Fig. 7), which in several gardens was documented could not only provide a means of propagating animals and as night-time iguana shelter sites. An “iguana-friendly yard” increasing population size but also could promote the devel- program with annual awards for the best new yards, iguana opment of vital knowledge about the species, especially con- numbers, or proof of nesting could stimulate and encourage sidering the low number and low population density of wild estate owners to adopt practices favoring better iguana stew- and/or semi-wild iguanas on Statia. Such facilities also could ardship. be used to house animals in need of rehabilitation due to inju- In casual conversations with many native Statians, little ries or acute situations arising after certain types of hurricane real appreciation for the uniqueness of Statian iguanas was scenarios. For optimum results, on-island efforts could also evident. Most inhabitants are not even aware that Green be coupled with an ex-situ zoo-breeding program. Finally, Iguanas, so common elsewhere, are a separate species that is by making tame animals available for interactions with the not threatened, and several individuals believed that different public in a relaxed setting, captive breeding should allow the public to develop a new appreciation for the species. An on- island husbandry program could probably be established at relatively low cost and managed by expanding existing efforts by STENAPA. A small-scale program existed previously but was never formally documented or professionally managed.
Acknowledgments This research was a joint project between STENAPA (St. Eustatius National Parks Foundation), the St. Eustatius Agriculture Service and IMARES. IMARES’s contribution was made possible as part of the Wageningen University BO research program (BO-11-011.05-004) and was financed by the Ministry of Economic Affairs, Agriculture, and Innovation (EL&I) under project number 4308701004. STENAPA’s involvement was made possible thanks to struc- tural financial support by the island government. We thank Mike McDonald, director of the Statia NuStar terminal, for Fig. 8. Local captive husbandry, with breeding as the ultimate goal, could provide pivotal support toward core I. delicatissima conservation objectives. arranging access to company grounds. Elze Dijkman plotted Figure © Adolphe Debrot. our map. Drs. Charles Knapp and Robert Powell provided
51 DEBROT ETAL. IRCF REPTILES & AMPHIBIANS • 20(2):44–52 • JUN 2013 access to key literature and valuable comments on earlier ver- Knapp, C.R. 2007. Ecology and conservation of the Lesser Antillean Iguana (Iguana sions of this work. delicatissima). Iguana 14:223–225. Knapp, C.R. and C. Perez-Heydrich. 2012. Using non-conspicuous metrics to examine selected impacts of disturbance on a long-lived reptile. Endangered Literature Cited Species Research 17:193–200. Breuil, M. 2002. Histoire naturelle des amphibiens et reptiles terrestres de l’Archipel Lorvelec, O., M. Pascal, C. Pavis, and P. Feldmann. 2007. Amphibians and rep- Guadeloupéen. Guadaloupe, Saint-Martin, Saint-Barthélemy. Patrimoines tiles of the French West Indies: Inventory, threats and conservation. Applied Naturels 54:1–339. Herpetology 4:131–161. Breuil, M., M. Day, and C. Knapp. 2010. Iguana delicatissima. In: IUCN 2012. MacRae, D.R. and N. Esteban. 2009. The Quill/Boven National Park and Botanical IUCN Red List of Threatened Species. Version 2012.2.
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