TRAINING ON POPULATION ESTIMATION ON KOMODO MONITOR June 2, 2008Posted by ekologi in Uncategorized.
Tags: ecological methodology, Komodo monitor, krebs (2002), population estimation, training
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SHORT TRAINING FOR KSDA STAFF ON INTRODUCTION TO POPULATION ESTIMATION USING ECOLOGICAL METHODOLOGY SOFTWARE (KREBS, 2002) FOR MARK RECAPTURE DATA ON KOMODO MONITOR
Ruteng, 19 May 2008
M Jeri Imansyah, Deni Purwandana
To increase capacity of staff of KSDA NTT and to give introduction on Mark Recapture methodology and population analysis based on mark recapture data that prepared for Komodo dragon population estimation on Flores, a short training on Introduction of Mark recapture methodology and use of Ecological Methodology (Krebs, 2002) computer program to estimate animal population was carried out in the KSDA NTT Office in Ruteng.
Training was carried out during two sessions. The first session included lectures on basic of population study in animal, mark recapture, and application of “Ecological Methodology (Krebs, 2002)” computer program given by the instructor, followed by a discussion where trainees were asking questions and additional information on specific procedures. During the second session, an open discussion went through research methodology applied to animal population size estimates.
The training course was attended by 22 members of staff from Bidang II KSDA NTT. Open discussion mostly dealt with implementation of mark-recapture methods for estimating animal population size on Flores. Species of interest was the Komodo monitor Varanus komodoensis. However, since none of KSDA staff had been involved in previous field work involving mark-recapture, nor they were acquainted with data analysis, the training mostly focused on basic concepts and logistics for the implementation of methods in the field.
Conclusions and Recommendations
- The training material was perhaps too advance for KSDA NTT staff, since no one of them has been involved in mark-recapture studies before.
- Time available to explain the theory of mark-recapture methods was insufficient and further training sessions should be scheduled along with practical sessions involving KSDA staff in mark-recapture field techniques, for instance in Komodo National Park. Training sessions involving both KSDA NTT and KNP staff are therefore recommended.
- Further training sessions to consider the basics of mark-recapture methodology for the Komodo monitor in more details should be carried out, along with training on alternative census methodologies for population size estimates of other wildlife in Komodo National Park and Flores.
We thank Luhut Sihombing, the Head of Balai Besar KSDA NTT, and Suprihatna, head of Bidang II KSDA NTT, for organizing the training sessions. The course was part of an MoU between Komodo Survival Program and Balai Besar KSDA NTT. Funds were provided by the European Aquaria and Zoos Association.
RECENT STATUS, BIOLOGY, ECOLOGY, AND REPRODUCTIOn OF KOMODO DRAGONS January 12, 2008Posted by ekologi in Uncategorized.
Tags: biawak Komodo, biology, conservation, ecologu, Komodo dragon, Komodo lizard, Komodo monitor, reproduction, status, Varanus komodoensis
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M Jeri IMANSYAH
1. SystematicS and distribution of the komodo dragons
Table 1. Local names for Komodo dragon
Ora (also hora, lawora) Komodo, Rinca, West Manggarai
Buaya darat (= land crocodile) Komodo, Rinca, West Manggarai
Rugu (= Ora) Central Manggarai
Si (also ugu; = lizard) Central Manggarai
Lio (also ugu, = large monitor) Central Manggarai
Pendugu (Grandfather of Ora) Central Manggarai
Source: Auffenberg 1981
Even though the Komodo dragon is the largest lizard in the world, this species has the smallest range of any large carnivore (King & Green 1999; Mattison 1992; Pough et al. 2001). In the early studies of the Komodo dragon, this species was found in the heart of the Lesser Sunda region on the islands of Komodo, Rinca, Padar, Gili Motang, Gili Dasami (also known as Nusa Kode), and the Western coast of Flores Island (Dunn 1928; Fig. 2.1). Five of the islands are within the boundary of Komodo National Park (PHKA 2000; Fig 1). In studies conducted after 1991, this species could not be found on Padar Island (Ciofi & de Boer 2004; Jessop et al. 2004; Sastrawan & Ciofi 2002).
Figure 1. Distribution of Varanus komodoensis. Grey areas represent the curre distribution; black areas represent areas that were identified as part of the distribution by Auffenberg (1981); hatched areas indicate where V. komodoensis have been reported by villagers.
Source: Redrawn from Sastrawan & Ciofi 2002.
2. Present status of the komodo dragonS
Table 2. Average density of Varanus komodoensis in Komodo National Park (KNP) and Flores Island.
KNP 1 / 33.25 km 4
Komodo 13.7 ± 1.67 / km
Rinca 19.6 ± 3.13 / km
Nusa Kode 5.1 ± 0.61 / km
Gili Motang 3.2 ± 0.23 / km
Source: Modified from Ciofi & de Boer 2004; Jessop et al. 2006 unpublished data.
The Komodo dragon is protected by international conventions; it is listed in Appendix I of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) and is classified by the International Union for the Conservation of Nature Resources (IUCN) as “vulnerable” due to its demographic decline and limited distribution (Ciofi et al. 2002). The World Conservation Monitoring Center (WCMC) also listed the Komodo dragon as “Rare” due to it’s restricted distribution (Ellis 1998). This species is protected in Indonesia under Act no. 5, on Conservation of Biological Resources and Their Ecosystems,1990,; and Government regulation no. 7, on Protected Wild Flora and Fauna, 1998. Primack (2004) included the Komodo dragon in his discussion on “conservation priorities” as he considered that this species met all the criteria of distinctiveness, endangerment, and utility3. Biology, ecology, and reproduction of the Komodo dragonS
Compared to other species in the family Varanidae, Varanus komodoenis has an extremely large body size. Adults can reach up to 304 cm in total body length and weigh up to 81.5 kg (Jessop et al. 2006 unpublished data). Sastrawan and Ciofi (2002) recorded the largest Komodo dragon in their field study as being about 300 cm in length and weighing about 69 kg. Auffenberg (1981) recorded his largest specimen caught as being 260 cm in length and 54 kg in weight. This is similar in length to the largest specimens of its sister species, the Papuan monitor V. salvadorii, which reached about 265 cm in length (Horn 2004). Another large varanid species, occuring on the islands of Java, Bali and throughout Lesser Sunda region, V. salvator may reach up to 218 cm in length and weigh up to 25 kg (Gaulke & Horn 2004; Horne & Gaulke 2004).Hatchlings of V. komodoensis average 30.4 cm in total length and 0.08 kg in weight, and are considerably longer at hatching than other large varanid species (Auffenberg 1981). Ciofi (2004) recorded that hatchling V. komodoensis average 42 cm in total length and 0.10 kg in weight. Hatchling V. salvadorii possibly reach up to 49 cm in total length and 0.55 kg in weight (King & Green 1999).
Komodo dragons can be found from sea level up to about 800 meters in altitude, mainly in tropical dry and moist deciduous monsoon forests (Ciofi 2004). Indeed, this species is generally distributed over entire islands within KNP and western coastal on Flores but is rarely found above 500 meters (Auffenberg 1981).
All varanids are insectivores or carnivores. Unlike other varanids that rely on smaller prey species, Komodo dragons are able to feed on larger vertebrate species, such as the Timor Deer (Cervus timorensis), water buffalo (Bubalus bubalis), or small wild boars (Sus scrofa). Adult Komodo dragons mostly rely on a sit-and-wait hunting strategy to catch their prey (Auffenberg 1981; Green et al. 1990; King & Green 1999; Pough et al. 2001). Hatchlings and juveniles, however, feed on a diverse diet of insects, small lizards, snakes and birds, and use more active hunting strategies than adults (Auffenberg 1981; Ciofi 1999; Mattison 1992).Female Komodo dragons are known to breed when they reach a body weight of around 20 kgs (King & Green 1999). Females begin nesting in August, as determined by the presence of recent digging activity on the nest, or by repeated observation of individuals in association with the nest during the nesting period. The nesting period is from August through November, with egg deposition occurring in September (Ciofi 1999; Jessop et al. 2004). Up to 38 hatchlings will emerge from the nest at the beginning of the dry season (Auffenberg 1981; Jessop et al. 2006 unpublished data). This early life-stage is dominated by high mortality. Cannibalism among Komodo dragons has been observed and was calculated to comprise 8% of adult dragon scats (Auffenberg 1981). Cannibalism has also been recorded in other Varanids, such as V. griseus, V. gouldii and V. gigantheus (King & Green 1999). 4. Biology and ecology of juveniles Generally, mortality in lizards is highest during the first phase of their life because they are more vulnerable to predation (Mattison 1992). Poor maternal body condition and stress can decrease the dispersal tendency of juveniles (Meylan et al. 2002). Typically, natural populations show substantial variation, in locomotor performance and body size, which is related to offspring survivorship (Clobert et al. 2000). Thus, the growth and survivorship of offspring in reptiles is greatly affected by the animal’s environment (i.e. Brockelman 1975; Gans & Pough 1982).
Incubation temperature is known to contribute greatly to the quality of emerging hatchlings and affects their survivorship. Cold temperature during incubation can negatively effect hatchlings and hot temperatures can positively effect hatchlings (Elphick & Shine 1998; Phillips & Packard 1994; Qualls & Andrews 1998). This pattern is complex, however, as higher incubation temperature will result in earlier hatching but produce lighter and smaller hatchlings than lower temperature, which produce larger offspring that tend to survive better (King & Green 1999). Du and Ji (2003) reported that moderate temperatures produced optimum size, locomotor ability and success of hatchlings in soft-shelled turtle, while Ji and Du (2000) reported a similar pattern in colubrid snakes. In a further study on lizards, the only discernible influence on juvenile phenotypes was their rearing environment (Qualls & Shine, 2000). Brockelman (1975) found that a wide variety of factors can affect optimal body size and the ability to process energy effectively, and these were also affected by the process of competition, which the offspring must face before and during maturity.
Most juvenile reptiles leave the natal area in which they were born and move into new habitats that are not already occupied or to avoid cannibalism by adults (Pough et al. 2001). Greenwood(1984) noted that natal dispersal among juveniles is also considered as a mechanism to avoid future inbreeding. Heatwole (1976) and Sarno et al. (2003) described natal dispersal as being driven by the competition for food resources and territories with adult.Dispersal is a mechanism for survival and is a consequence of permanent movement away from the natal site (Brown & Downhower 1988). Animals will exploit available resources once they are out of their natal sites (Greenwood & Swingland 1984). Pelletier et al. (2003) described how immature turtles immediately swam towards the ocean and steadily traveled long distances once released into the water. Hatchling of varanids tend to climb trees and spend most of their time in the upper strata of trees once they emerged from the underground nests (Auffenberg 1981; Bohme et al. 2004; Ciofi 2004; King & Green 1999).
5. Previous ecological studIES on the KOMODO DRAGONS The first scientific study on the Komodo dragon was conducted by Major Peter A. Ouwen, director of the Zoological Museum in Buitenzorg (now Bogor), Java, in 1912 (Auffenberg & Auffenberg 2002). Ouwen described the species for the first time. Later, Dunn (1927 & 1928) conducted the first significant observations and gave the initial information on the habitat and distribution of Komodo dragons. Auffenberg (1981) contributed to the first comprehensive study on the ecology and behavior of this species. On the basis of 13 months of field observations, Auffenberg (1981) provided the base line information on aspects of the Komodo dragon’s ecology and behavior. The most recent field study on the Komodo dragon was conducted by Jessop et al. (2006 unpublished data). Since 2002, they undertook a broad scale investigation in the ecologyl and demography of the Komodo dragon, which has provided important information and instigated a program to monitor population trends. Although numerous field studies on the ecology of Komodo dragons have been conducted, yet there are no detailed studies on the ecology on juvenile Komodo dragons (Auffenberg & Auffenberg 2002). Walsh et al. (2002) studied growth in juvenile Komodo dragons, whilst Lemm (2004) reported a relationship between growth and nutritional treatment in captivity. Field and captive studies on this creature, including work on growth, chromosomes, physiology, genetics, ecology and social behaviour, parasites, microbiology, conservation and management, have provided valuable information to science and to ensure effective management of the species (Ciofi et al. 2002). The long-term management and conservation objectives underpinning survival of this species will be to maintain a genetically viable, self-sustaining, and free-living Komodo dragon population. Information on reproduction and broad scale ecology of this species is needed to support the management authority responsible to protect it, and, as pointed out by Jessop et al. (2004), information on offspring survivorship are vital for management planning to ensure the maintenance of this unique species in the wild.