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AN INITIAL BIODIVERSITY ASSESSMENT OF KABAENA ISLAND
INTRODUCTION
Kabaeana Island lies 56km to the west of Buton Island in SE Sulawesi. The island is more mountainous than Buton and has the 1500m Gunung Sambopolulu as the centre-piece of the island. It also boasts a large limestone crag, Batusangia, 1000m, which adds to the impressive vista, and the island is home to many cave systems. The geology is different to that of Buton with large areas of ultra basic rock.
Most importantly from the biological perspective, there have been virtually no surveys of the wildlife of this substantial island. In 1999 an Operation Wallacea bird survey team visited the island for 2 weeks. This initial survey revealed the presence of a species of ground thrush (Zoothera sp.) that appeared markedly different from previously described species. In 2002 an Operation Wallacea bird survey team returned to Kabaena to mist net the ground thrush and make detailed drawings, take photographs and make recordings of the calls for comparison with the ground thrush species on Buton and the mainland of Sulawesi. This work appeared to confirm that the Zoothera species on Kabaena may be new to science.
Birds are the best studied taxonomic group worldwide and if a species new to science could be found on Kabaena Island, then the possibility for the discovery of new species in other groups was very high indeed. Moreover, the earlier visits by the Operation Wallacea survey teams had shown that much of the island was already de-forested and the remaining areas appeared to be under threat. There are no protected forest areas on Kabaena island, yet if the early indications from the bird work proved to be correct, then the island may contain a number of unique species.
The objectives of the 2001 survey therefore were to undertake rapid assessments on a range of other taxonomic groups in addition to birds and to identify the best remaiining areas of forest on the island which may contain these unique species.
In September 2001 the following scientists participated in the survey;
Dr Boeadi, Institute of Environmental Sciences (project leader and taxonomy of mammal species)
Dr Graeme Gillespie, Arthur Rylah Institute, Melbourne (herpetofauna surveys)
Dr Tigga Kingston, Boston University (bat surveys)
Dr Dave Kelly, Trinity College Dublin & Julia Robinson-Dean, RSPB (birds)
Dr Dave Bird, University of West of England (fish)
Andy Jennings, Durham University & Nicola Grimwood, Manchester Metropolitan University (small mammal surveys)
Graeme Cooper & Phil Stanier, Operation Wallacea (macaques)
In addition Evette Stevens and Mike Hawkins, University of Birmingham completed final year Honours dissertations on aspects of the macaque survey.
LOGISTICS ARRANGEMENTS
This year’s base camp was in the village of Enano, a very hospitable and culturally active village, with satellite camps in Tangkeno, Pongkalero, Dongkala and Rahadopi and far reaching flying camps in Batusangia, Gunnung Sambopululu, and in the forests downstream from Tangkeno. With up to 60 volunteers and staff present on the island at any one time, in up to four different locations, logistics were complex. Two ports serve the island, Sikeli on the west, and Dongkala on the east with a single road connecting them. Enano is slightly nearer Dongkala than Sikeli, and most movements, people and supplies from Bau Bau used this port, however the local market in Sikeli was more appropriate for local supplies of fresh fish and vegetables. There is also a driveable road from Sikeli to Tangkeno which was used for moving equipment and supplies; people tended to walk the old road, now a wide trail, direct from Enano, 2hrs as opposed to the 2.5hr drive, as it was much more comfortable. Kabaena’s road is more of a dirt track than a road, so two 4x4s with experienced drivers/mechanics were shipped from Bau Bau for the length of the expedition; an additional vehicle was hired when necessary. Accomodation in Enano, and other satellite camps was in local houses, as agreed by the Kepala Desa (head man), and all flying camps were simple hammock and tent arrangements.
We were there in late August, September, Kabaena’s dry season with an average daily temperature of 35 degrees in the shade, so most work survey work was done in early morning and late afternoon, though general trekking, caving and waterfall/river activities took place throughout the day. Due to our experience of the local porter availability during the recce in 2000, we brought some key local staff from Buton who not only had experience of working with the scientists, but had logistical awareness of what was required in expedition circumstances. Local porters were hired in addition when necessary, and the balance created by this was a good one; but for future reference, local "guides" often know less about the lay of the land than a well armed volunteer with a compass, map and GPS!
Medical facilities on the island are concentrated in Teomokole, near Sikeli, where there is a good clinic and supportive staff, and in Dongkala with a smaller clinic. Any expedition that comes here in the future should come medically prepared, with at least two medics on site at all times.
Radio communications with Bau Bau were conducted on SSB radios, and all satellite and flying camps were linked to Enano by VHF, the exception being Pongkalero where it was necessary to set up an additional SSB due to the distance between Pongkalero and Enano (20km). A radio operator is essential, as this is a remote island with no pre existing systems.
GEOLOGY
Kabaena is, geologically speaking, one of the least well known of the medium-sized Indonesian islands. No detailed geological map has been published, although the island appears on the 1:1,000,000 Ujung Pandang sheet (Sukamto et al.), which shows it to consist of two belts of ophiolitic rocks, in the north and south, separated by an east-west trending belt of metamorphic rocks exposed in an irregular strip of lower ground that cuts across the island from Sikeli to Tolitoli. Work during the 2001 visit was confined to the ‘lateral valley’ and the adjacent higher ground, utilising Enano as the base of operations. The outcrop pattern shown on the published map was confirmed and explained. It seems that the ophiolite rests on a sub-horizontal thrust sheet which is generally a few tens to a few hundreds of metres above sea level. Outcrops in the lower ground, and hence below this thrust, are of metamorphic rocks which become more deformed as the thrust plane is approached. Outcrops at higher levels, in the cental mountain range, are of ophiolitic rocks. It is assumed that the same is true of the northern hills, although these were not visited. In the vicinity of Enano, the ophiolitic rocks are dominantly gabbros.
The lateral valley was evidently below sea level in the not too distant past, since coral reef knolls west of Enano now rise to heights of over 100 m above the plain. These are assumed to be Quaternary, although no dates have been reported. Near Sikeli, on the west coast, there is an area of low rounded hills which support only a poor grassland vegetation. These are formed of probably fluviatile coarse sands and gravels, which may be contemporaneous with the reef knolls.
As outlined here, the geology of Kabaena appears very simple. Almost certainly, this is due to the fact that work on the island was limited to a period of only five days. Even within that time, two anomalies were apparent. The river immediately east of Enano, despite being remote from any significant areas of high ground and close to roadside exposures of metamorphic rocks, is full of ophiolitic float and there is a possible outcrop of basic rock in the river bed just to the north of the grid. Also, the spectacular crest of Batusangia, at a height of well over 1000m, appears (from a distance, at least), to be formed of a coral reef knoll similar to those seen at much lower level in the median valley. One possible explanation for both these observations is that there has been strongly differential uplift of individual blocks now forming Kabaena.
Geologically, Kabaena seems very similar to much of eastern Sulawesi, especially those parts north of the Lawanopo Fault, where ultramafic rocks are most plentiful. Despite recent publications (e.g. Maury et al.), many problems remain in East Sulawesi geology. It is not clear whether the ophiolites all have the same provenance or are members of two or more ophiolitic suites. Opinions differ as to whether they formed in a back-arc basin or a supra-subduction zone (forearc) environment. The history of metamorphism is also unclear, and there is little or no geobarometric control. Although blueschists have been reported from the nearby Rumia Mountains of the Sulawesi mainland, the majority of the metamorphic rocks of Sulawesi have been described as greenschists, indicating relatively normal pressure-temperature relationships. Further work on Kabaena should be directed towards shedding further light on the evolution of the East Sulawesi block. A certain amount of straightforward mapping work is required, but the most important results will come from the laboratory.
FRESHWATER AND ESTUARINE FISH
The freshwater fish of Kabaena have never been described. This report describes the results of a survey of freshwater species carried out in September 2001. A field guide to the fishes of Western Indonesia and Sulawesi (Kottelat et al., 1993) contains keys and descriptions of more than 1000 species, but specific information about Kabaena is not included. The only other published work contains a preliminary checklist of 102 species of fish from Sulawesi that includes 13 new species and 6 species endemic to the region (Tjakrawidjaja & Hadiaty, 1996).
The objectives were to:
Fish samples were collected using electrofishing and beach seining. The position of each site was recorded using GPS. Current velocity, temperature, pH and water conductivity was measured using portable meters. The substrate was characterised using the Wentworth Classification of substrate particle substratum size.
Fish were anaesthetised in benzocaine and representative individuals photographed alive. Fish were identified to species where possible (Kottelat et al., 1993) and up to 6 individuals of each species were prepared as museum specimens as previously described in the report for Buton.
When compared with Buton, the rivers on Kabaena tended to be more alkaline (up to pH 8.2) and less conductive. These differences are presumably due to the widespread occurrence of ultrabasic rocks on Kabaena in contrast to the predominantly calcareous deposits on Buton. A total of 11 sites were sampled over a 2-week period. The sites were selected to cover the widest possible range of freshwater and estuarine habitats. These ranged from hillstreams approximately 500m above sea level to estuarine river mouths. Many of the common species collected on Buton were also seen in collections on Kabaena, but there were some interesting differences between the two islands.
On Buton, a species of ‘halfbeak’ was collected (Nomorhamphus sp.) that could not be identified and may be a new species. One of the distinguishing characteristics of this fish was the red coloration of the fins that also extended over the body in mature males. On Kabaena, a very similar species was collected, but unlike the form on Buton, had a distinctive sulphurous yellow ventral surface and no red fins. Whether the Kabaena form is a different species or just a morphological variation will need to be confirmed.
Collections from a fast flowing upland river, approximately 500 m above sea level, contained two species of gobies that had not been encountered in the survey on Buton. One was an extremely flattened species of Sicyopterus that could not be identified to species. The other goby had a distinctive red caudal region but could not be identified beyond the Family level. Both these gobies may be adapted to live in the fast flowing upland streams that are a feature of Kabaena, but further taxonomic work will be necessary to establish the identity of these fish.
HERPETOFAUNA
Kabaena is characterised by a mountainous terrain, dominated by ultrabasic marine sediments, whereas Buton is dominated by more recent limestone deposits. Although the annual rainfall of Kabaena is similar to that of Buton, the wet and dry seasons are more pronounced on Kabaena. Collectively these factors have produced markedly different forest types and habitats on these islands. These differences, combined with the relative isolation of the two islands may have resulted in the development of markedly different faunal assemblages. This may be most strongly reflected in the herpetofaunal assemblage, which is potentially most sensitive to local altitudinal, climatic and forest structural differences, and least able to disperse across sea barriers. Knowledge of the herpetofauna of Kabaena Island is therefore an important component of characterising the herpetofaunal component of the biodiversity of this region of Sulawesi.
The survey was based in the vicinity of Enano in central Kabaena Island. Sampling was conducted between late August and late September 2001. A variety of methods were employed to sample the herpetofauna.
Pitfall traps were established at 8 sites in a variety of habitats. Each trap comprised five 60 L buckets embedded in the ground, spaced 5 m apart, with a 1 mm gauge wire mesh drift fence 30 cm high and 20 m long, passing over the centre of each bucket. Pitfall trap sites were chosen to sample the range of broadly-distinct habitat types within the Enano region. These included terraces and mid-slopes in dry rainforest with varying levels of man-made disturbance from selective logging and slash & burn agriculture, and several sites in highly disturbed habitats, such as regenerating cleared forest and plantations. Pitfall traps were checked every morning and operated for two to four weeks.
Opportunistic searches were conducted for reptiles over a wider area. These searches generally comprised walking slowly through various habitats, such as forests, along streams, agricultural areas or swamps, looking for active reptiles and investigating under logs, rocks or other ground debris for sheltering animals.
Nocturnal searches were conducted for frogs and reptiles. These searches were mostly targeted at, or near, aquatic environments, such as streams, but nocturnal searches were also conducted in other forest habitats and caves, specifically targeting geckos and snakes.
Voucher specimens were collected of most taxa detected to confirm field identification, to aid identification of unknown species or suspected new species, and to collect material for taxonomic groups requiring further systematic resolution. These specimens will be lodged with the National Museum in Bogor.
Nomenclature follows that used by Iskandar and Nio (1996) and Manthey and Grossman (1997).
A total of 36 species were detected during the survey (Table 1 in the Appendix). This comprised eight species of frog (Ranidae, Bufonidae, & Rhacophoridae), 13 species of snake (Colubridae, Pythonidae, Typhlopidae), and 15 lizard species (Agamidae, Gekkonidae, Scincidae, Varanidae). A number of taxa could not be confidently identified in the field, due to the limited information available on species descriptions for the region. The identity of three lizard and one snake taxa are yet to be determined by examination of existing museum specimens.
Most of the species located have also been found on Buton Island. Several species were located that have not been recorded on Buton (Table 1). In most cases these species are widespread in Sulawesi. One species of gecko (Gehyra sp.) could not be identified.
The fewer number of species detected on Kabaena compared with Buton is most likely due to lower survey effort (ie. 1 month compared with 5 months) and seasonal effects. The survey was conducted during the middle of the dry season. During this time, reptile and frog activity levels are reduced due to limited access to moisture and extreme temperature conditions. Most of the species located are relatively common and widespread species. In addition, access to more remote undisturbed habitats was difficult and these were not sampled effectively during the survey. More survey effort during seasons more appropriate for herpetofauna are likely to increase this species list significantly
In summary, this preliminary survey has not detected any major differences in the herpetofaunal assemblage of Kabaena compared with Buton. However, the survey was probably biassed to more widespread and cosmopolitan species. Further survey effort is required to consolidate knowledge of the herpetofauna of Kabaena Island.
BIRDS
Four weeks was spent assessing the bird fauna of the forests and farmland areas of Kabaena Island. Mist netting was performed at Tangkeno and Enano to supplement the observations. The avifauna of coastal areas was excluded from this intial survey. Table 1 in the Appendix lists the species identified from the 2001 survey.
The most important species identified to date on Kabaena is the ‘Red-backed’ Thrush (Zoothera sp.). Observations from 1999 and 2000 have shown the birds on Kabaena to be significantly darker than their mainland and Buton counterparts. This year’s project aimed to trap a number of individuals and take some as museum specimens. Using these animals and data from other populations (including DNA samples) it is hoped that it will be possible to resolve the taxonomic status of these birds. From the information collected and analysed to date it appears more likely that the bird will be described as a new subspecies, rather than a full species.
The taxonomic status of this bird may contribute to conservation efforts on Kabaena. This year’s studies focussed on an area of relatively undisturbed forest near to Tangkeno. The population density of the thrush appeared relatively high here. We succeeded in trapping six individuals, and took two of these (one male, one female) as museum specimens. During the 1999 season a number of birds were observed in more disturbed habitats. Indeed, the first individual to be trapped was caught on the edge of a football pitch. This year, only one individual was observed outside of the Tangkeno forest area. This bird was seen in highly disturbed forest beside a river just south of Enano. It appears that the bird has a preference for less disturbed habitat, but can survive without it. Recent observations from Buton support this idea.
A comparison of the avifaunas of Kabaena and Buton is underway. To date, a number of species have been identified as absent from the depauperate forests of Kabaena. These include Knobbed Hornbill, Sulawesi Hornbill, Bay Coucal, Pied Cuckoo Shrike, Sulawesi Hawk Cuckoo, Ochre-bellied Hawk Owl and Sulawesi Nightjar. Perhaps the more interesting absentees are the Coucal and Cuckoo Shrike, as these species do not appear to be dependent on pristine habitat on Buton. The Pied Cuckoo Shrike has a patchy distribution across its range, and its absence could simply be a result of this. Bay Coucals are secretive birds, and prefer good cover. However, two closely related species, Fiery-billed Malkoha and Black-billed Koel, are present on Kabaena. These two species appear to have similar habitat requirements to the Bay Coucal. Perhaps the Bay Coucal is a more sensitive species, and as such may be a useful indicator of higher quality forests.
A few rarer species have yet to be recorded on Kabaena, these include: Ochre-bellied Hawk Owl, Sulawesi Hawk Cuckoo, Sulawesi Nightjar. These are all forest species, and may simply be absent, but a more complete survey is required to be sure.
A cursory study of the songs and calls of the birds of Kabaena has revealed some subtle differences between Kabaena and Buton birds. Such differences may allow a way of monitoring the divergence of species, and hence the process of speciation. Further studies in this area could prove interesting, and may suggest additional species for taxonomic review.
SMALL MAMMALS
The aim of the Kabaena 2001 small mammal project was to carry out a baseline biodiversity survey of the small mammal fauna. The small mammal fauna of Kabaena has not previously been studied, and it is important to begin to establish the range of species present. A large proportion of Sulawesi small mammals are endemic, and therefore of high conservation value.
The survey took place between the 5th and the 20th September, and was based predominantly in disturbed forest located around the village of Enano in the central region of Kabaena. Some additional trapping was also carried out from the 12th to the 15th September in disturbed forest adjacent to Pongkalaero, a village on the south-west coast of the island. Four sites were selected at Enano; two were located on the south face of a ridge to the north of the village, and two to the south. Of the sites to the south, one was located on a river terrace, and the second on the north face of a ridge. Traps were also set at one site at Pongkalaero, at the base of a ridge approximately one to two kilometres east of the village.
Twenty wire cage Tomahawk traps, and 30 Longworth traps were available for use on Kabaena. The Tomahawks were set to trap the larger rodent species, and the smaller Longworth traps used for the smaller rodents and shrews. All traps were baited with a standard small mammal bait consisting of peanut butter and oats. Each site to be trapped was reconnoitered, and a selection of traps were then set in positions which showed evidence of small mammal use (for example burrows, faeces or feeding remains). If no clear evidence was present, traps were set in locations which provided habitat features which might be used by small mammals (e.g. logs, tree buttresses, rock piles). After an initial trapping period at all sites, trapping effort was concentrated on the two sites south of Enano which were yielding the best range of specimens, including potentially undescribed species.
All traps were checked each morning, and re-baited where necessary. Morphometric data was collected for all captured animals; this included sex, reproductive state weight, length of head and body, hind foot and tail. In addition a brief description of other identifying features was taken down, for example pelage colour and texture. A small DNA sample was taken from the ear of all captured animals. A small number of individuals of each species captured were taken as specimens. Some specimens will be lodged in the collection of the Bogor Museum and the remainder will be sent to Dr. Guy Musser at the American Museum of Natural History in New York for identification.
Over the course of the study 46 individuals of at least ten species of small mammal were captured, consisting of three shrew species, two mouse species and at least five species of rat. A total of 32 specimens were collected.
Of the shrew species, the majority of captures consisted of an undescribed species of Crocidura. The other species trapped were C. elongata and C. levicula.
Only one specimen of each mouse species was trapped; these species have yet to be identified.
Of the rat species trapped, one was readily identified as Paruromys dominator (the Sulawesi giant rat). Two specimens in the genus Bunomys were taken, but these have not yet been identified to species level. Two specimens of a suspected Rattus were also trapped; the species has yet to be determined.
The remaining specimens consisted of a number of rats that could not be allocated to any described species. These individuals showed some unusual features which indicate that they may belong to a new species. One group of specimens consisted of medium to large sized rats, with the males displaying a very distinctive large single scent gland located on the ventral centre line. The gland was up to 1cm in width, and ran for several centimetres from the genital area towards the chest. A single individual of an extremely small rat species was also trapped; this also possessed a single ventral scent gland, but in addition had spiny pelage. These features have not been described for any species previously recorded in Sulawesi.
This initial project has produced some very interesting findings, and shows that the small mammal fauna of Kabaena may warrant further study. Little is known about the ecology of the endemic small mammal fauna of Sulawesi, or about the potential impact of human activity resulting in habitat loss or degradation.
MACAQUES
Information on the macaque species of Kabaena Island has previously been very sparse due to very little research having been carried out. Reports of an introduced species of long-tailed macaque (Macaca fasicularis) have indicated that this is the main (if not only) species of macaque currently found in Kabaena, despite not being found in any other part of Sulawesi. An interview survey of locals in different villages was carried out witht he following objectives;
A questionnaire was devised as a basis for a fairly informal interview, covering a variety of areas in an attempt to meet the objectives of the survey. Five villages were selected in different parts of Kabaena: Enano/Lengora, Tangkeno, Dongkala, Pongkalaero and Rahadopi. In each village permission was first gained from the Kapela Desa (or secretary) then interviews were carried out with individuals who have seen macaques. Ideally a stratified random sample would have been taken of the population of each village but realistically this proved far too difficult for the timescale involved. Instead a quota of twenty questionnaires for each village was set, along with attempts to get as wide a cross-section of people as possible. Interviews were conducted, using a translator, in Bahasa Indonesia, and the quota was reached in all areas except Rahadopi, where logistical problems meant only eleven interviews were completed.
Long-tailed Macaques are distributed throughout all the areas studied, though often sparsely, with higher concentrations in the coastal areas around Dongkala and Pongkalaero. Crop raiding is a problem in all areas to a greater of lesser extent, especially on farms situated far from villages and adjacent to the forest. A couple of the interviews with older residents suggested that Pig-tailed Macaques used to exist on Kabaena, but have not be seen for the last 40 - 50 years. There was however no supporting evidence for this assertion and the date when Long-tailed Macaques were introduced to the island and whether or not there was an existing population of Pig-tailed macaques remains unresolved.BATS
Despite its current vicinity to Buton, Kabaena Island is thought to have been associated with the South-east arm of Sulawesi since the Tertiary, contrasting with Buton’s relatively recent arrival from Melanesia in the Late Miocene. The topology and habitat differ dramatically from Buton, and a preliminary survey in 2000 suggest that the extensive karst limeston cave systems of Kabaena support large and diverse populations of both fruit-eating and insectivorous bats. There is considerable evidence that roosts may be limiting for many bat species, and caves maybe pivotal to local survival when alternative roost sites, such as large hollow trees are reduced by forest clearance. Forest loss is a conservation issue on Kabaena, and as a consequence the cave systems may represent a keystone resource for the bat fauna of Kabaena.
Surveying at caves involved a combination of mist netting, harp trapping and the use of hand nets to capture individuals. Acoustic monitoring at emergence from caves was implemented. Mist nets and harp traps were also deployed in the forest remnants and sugar palm areas around Enano village, and nets set over rivers and streams.
16 species were captured in the course of the survey; 12 insectivorous species and 4 fruit bats. All species had been recorded on Buton Island but both Hipposideros cervinus and Rhinolophus sp. were significantly smaller than their Buton counterparts. The caves at Lengora were extensively surveyed and included large colonies of Dobsonia viridis, Miniopterus australis, M. schreibersi, and a Rhinolophus that is currently unidentified but may be R. arcuatus or R. affinis. Smaller colonies of the Sulawesi endemic Hipposideros dinops were found in both the Lengora system and in a cave near Tangkeno. Surveys at small caves around Tangkeno added Rousettus celebensis, Rhinolophus philippinensis and Rhinolophus sp. to the cave-bat list. Cynopterus brachyotis and Macroglossus minimus were commonly captured in mist nets in disturbed areas and forest remants, as was R. arcuatus/affinis. Hipposideros cineraceus, Myotis muricola, Murina florium and Kerivoula hardwickii were all captured by harp traps in disturbed forest and palm-dominated areas around streams. Bat activity was notably concentrated around forest remnant near streams.
The bat fauna of Kabaena would appear to be a subset of that of Buton Island. The fruit-bat fauna was probably under-sampled by this survey, and Kerivoula papillosa was notably absent from the insectivorous bat community. The omission of the latter may be indicative of this species’ dependence upon intact forest which was not sampled in this survey.
CONCLUSIONS
This initial survey has shown that Kabaena for the most part has a subset of the fauna found on Sulawesi, with some notable omissions. Small islands have been shown to support a smaller assemblage of species than larger islands in the same area and the finding that Kabaena has a subset of the Sulawesi fauna is therefore not surprising.
There were, however, some differences between the fauna of Kabaena and either Buton or mainland Sulawesi with the discovery of 2 small mammals, at least 2 freshwater fish, the ground thrush, three reptiles and one snake all of which may be new to science. It should be noted though that this survey was carried out in the dry season and the frog fauna were therefore difficult to survey. In addition both the freshwater fish and small mammal teams need additional survey time on Kabaena to complete their assessments.
The best remaining forest and the area from which most of the new species were sampled, was a mountain valley near Enano. This valley has pristine forest and appears too inaccessible to have suffered from logging. This was the only forest area on Kabaena that was noted by the survey team as being worthy of protection.
It is therefore proposed that Operation Wallacea requests that the Department of Forestry and Wildlife Conservation give protected forest status to the mountain valley near Enano , to preserve the unique fauna of the island. In addition a follow up survey of the frogs, freshwater fish and small mammals in this mountain valley is scheduled in the Operation Wallacea survey programme for the end of the wet season in 2002 to add more details about these groups in the proposed protected forest area..
APPENDIX
TABLE 1
List of reptiles and frogs detected on Kabaena Island. * - species not recorded on Buton.
Amphibia
Reptilia
Table 2 Bird species recorded from Kabaena Island
|
Species |
Scientific Name |
|
Christmas Island Frigatebird |
Fregata andrewsi |
|
Purple Heron |
Ardea purpurea |
|
Woolly-necked Stork |
Ciconia episcopus |
|
Barred Honey-Buzzard |
Pernis celebensis |
|
Black-shouldered Kite |
Elanus caeruleus |
|
Brahminy Kite |
Haliastur indus |
|
White-bellied Sea-Eagle |
Haliaeetus leucogaster |
|
Sulawesi Serpent-Eagle |
Spilornis rufipectus |
|
Spotted Harrier |
Circus assimilis |
|
Spot-tailed Goshawk |
Accipiter trinotatus |
|
Rufous-bellied Eagle |
Hieraaetus kienerii |
|
Spotted Kestrel |
Falco moluccensis |
|
Sunda Teal |
Anas gibberifrons |
|
Blue-breasted Quail |
Coturnix chinensis |
|
Red Junglefowl |
Gallus gallus |
|
Barred Rail |
Gallirallus torquatus |
|
White-breasted Waterhen |
Amaurornis pheonicurus |
|
Spotted Dove |
Streptopelia chinensis |
|
Slender-billed Cuckoo-Dove |
Macropygia amboinensis |
|
White-faced Cuckoo-Dove |
Turacoena manadensis |
|
Emerald Pigeon |
Chalcophaps indica |
|
Black-naped Fruit-Dove |
Ptilinopus melanospila |
|
Green Imperial Pigeon |
Ducula aenea |
|
Ornate Lorikeet |
Trichoglossus ornatus |
|
Sulawesi Hanging-Parrot |
Loriculus stigmatus |
|
Golden-mantled Racket-tail |
Prioniturus platurus |
|
Blue-backed Parrot |
Tanygnathus sumatranus |
|
Plaintive Cuckoo |
Cacomantis merulinus |
|
Drongo Cuckoo |
Surniculus lugubris |
|
Black-billed Koel |
Eudynamys melanorhyncha |
|
Fiery-billed Malkoha |
Phaenicophaeus calyorhynchus |
|
Lesser Coucal |
Centropus bengalensis |
|
Sulawesi Owl |
Tyto rosenbergii |
|
Sulawesi Scops-Owl |
Otus manadensis |
|
Great-eared Nightjar |
Eurostropodus macrotis |
|
Grey-rumped Tree-Swift |
Hemiprocne longipennis |
|
White-bellied Swiftlet |
Collocalia esculenta |
|
Moluccan Swiftlet |
Aerodramus infuscatus |
|
Ruddy Kingfisher |
Halcyon coromanda |
|
Collared Kingfisher |
Halcyon chloris |
|
Blue-eared Kingfisher |
Alcedo meninting |
|
Rainbow Bee-eater |
Merops ornatus |
|
Ashy Woodpecker |
Mulleripicus fulvus |
|
Pacific Swallow |
Hirundo tahitica |
|
Sulawesi Cicadabird |
Coracina morio |
|
Sulawesi Pied Triller |
Lalage (nigra) leucopygialis |
|
Hair-crested Drongo |
Dicrurus hottentottus |
|
Black-naped Oriole |
Oriolus chinensis |
|
Slender-billed Crow |
Corvus enca |
|
Sulawesi Babbler |
Trichastoma celebense |
|
Pied Bushchat |
Saxicola caprata |
|
Red-backed Thrush |
Zootherea erythronota |
|
Zitting Cisticola |
Cisticola juncidis |
|
Black-naped Monarch |
Hypothymis azurea puella |
|
Citrine Flycatcher |
Culicicapa helianthea |
|
Grey Wagtail |
Moticilla cinerea |
|
Ivory-backed Woodswallow |
Artamus monachus |
|
Asian Glossy Starling |
Aplonis panayensis |
|
Finch-billed Myna |
Scissirostrum dubium |
|
Brown-throated Sunbird |
Anthreptes malacensis |
|
Black Sunbird |
Nectarinia aspasia |
|
Olive-backed Sunbird |
Nectarinia jugularis |
|
Crimson Sunbird |
Aethopyga siparaja |
|
Yellow-sided Flowerpecker |
Dicaeum aureolimbatum |
|
Grey-sided Flowerpecker |
Dicaeum celebicum |
|
Pale-bellied White-Eye |
Zosterops consobrinorum |
|
Eurasian Tree Sparrow |
Passer montanus |
|
Black-faced Munia |
Lonchura molucca |
|
Scaly-breasted Munia |
Lonchura punctulata |
|
Chestnut Munia |
Lonchura malacca |
|
Pale-headed Munia |
Lonchura pallida |