This species is found on the northern coast of Australia and all around Papua New Guinea and is generally confined to areas of intertidal influence (S. Sweet pers. comm.). It is also found on islands in eastern Indonesia and western Oceania (Dryden and Ziegler 2004), and has been reported from the Bonin Islands (Philipp et al. 1999). It has been introduced to the Marshall Islands and various of the Mariana islands (Ziegler et al. 2007).
Continent: Oceania Asia Australia Distribution: Australia (North Territory, Queensland) Sulawesi, Moluccas, Aru Islands, Talaud, Irian Jaya, Timor (Indonesia), Solomon Islands, Papua New Guinea, Bismarck Archipelago, Caroline Islands, Mariana Islands, Marshall Islands Type locality: Ambon, Moluccas, Indonesia. Type locality: Fofak (as Offack) Bay, N coast of Waigeu, Indonesia [Monitor kalabek] Type locality: Praslin Harbour, New Ireland (as New Mecklenberg), Papua New Guinea [Monitor douarrha] Type locality: Rawack Is., N of Waigeu, Indonesia [Monitor chlorostigma] Type locality: Doreh, Berou Peninsula, NW New Guinea [doreanus] Type locality: Saipan, Caroline Ils. [tsukawotoi] Type locality: from George's Is., Solomon Ils. [indicus spinulosus]
This species is eurytopic, inhabiting open or closed vegetation areas. Its preferred habitats are those influenced by salt water, and it may also be associated with human settlements (Bhme et al. 1994, Dryden and Ziegler 2004). It is most commonly found along shorelines and in mangrove forests, but it has also adapted well to coconut and oil palm plantations. In closed forest environments and beyond tidal influence on larger islands, it is usually replaced by related species, such as V. doreanus and V. jobiensis.
Bhm, M., Collen, B. & Ram, M. (Sampled Red List Index Coordinating Team)
De Silva, R., Milligan, H.T., Wearn, O.R., Wren, S., Zamin, T., Sears, J., Wilson, P., Lewis, S., Lintott, P. & Powney, G.
Varanus indicus has been assessed as Least Concern because it has a large distribution and is common in a variety of habitats. However, this Varanid is harvested for many reasons and may become threatened in the future. Furthermore, the likely future discovery of new species within this species complex will affect the conservation status of this species, as island endemics within the complex may receive species status. Therefore, research into its population status and harvest levels is suggested to check population declines in V. indicus.
There are no known species-specific conservation measures in place for this species. Research into the harvest levels and population status of this species is suggested to establish if current harvest levels are sustainable.
The mangrove monitor was first described by the French herpetologistFrançois Marie Daudin in 1802. Daudin's original holotype of a subadult specimen was collected on Ambon, Indonesia, and has since disappeared from the museum in Paris. Daudin's original name for the species was Tupinambis indicus, an appellation it would carry for 100 years until being renamed as a Varanus.
The mangrove monitor's range extends throughout northern Australia, New Guinea, the Solomon Islands, the Marshall Islands, the Caroline Islands, and the Mariana Islands, where it inhabits damp forests near coastal rivers, mangroves, and permanent inland lakes. It also occurs on the Moluccan islands of Morotai, Ternate, Halmahera, Obi, Buru, Ambon, Haruku and Seram. Within this range of thousands of miles across hundreds of islands are large variations in size, pattern, and scalation. The monitors have also been introduced to Japan since the 1940s. Like the introduction to Japan, some herpetologists believe this animal's dispersal from the East Indies to smaller Pacific islands was facilitated by Polynesians to provide a meat supply. However, other scientists maintain this is not likely, as the monitors would compete with man for food, grow slowly, and yield little meat.
The monitor's body is dark green or black in color and covered with golden-yellow spots, with light coloration on the top of its head and a solid, cream-colored belly lacking dark markings. It has a distinct dark purple tongue and serrated teeth. The mangrove monitor attains different sizes in different parts of its range, but seldom if ever exceeds 1.5 m in total length. Australian herpetologist Harold Cogger gives a total length of 100 cm for Australian specimens. The tail is almost twice the length of the body and laterally compressed to aid in swimming. Like the rest of the lizard's body, it is covered with small, oval, keeled scales.
This monitor has the ability to increase the size of its mouth by spreading the hyoid apparatus and dropping the lower jaw to eat large prey, a process similar in appearance to that of snakes, although the jaw of the mangrove monitor remains rigid. The mangrove monitor possesses a Jacobson's organ, which it uses to detect prey, sticking its tongue out to gather scents and touching it to the opening of the organ when the tongue is retracted.
The mangrove monitor is one of only two species of monitor lizards, the other being V. semiremex, that possess salt-excreting nasal glands, which enable them to survive in saltwater conditions and to consume marine prey. The presence of this gland probably enabled the monitors to reach new islands and aid in its dispersal throughout the Pacific.
The mangrove monitor is an opportunistic carnivore, feeding on the eggs of reptiles and birds, mollusks, rodents, insects, crabs, smaller lizards, fish, and carrion. Mangrove monitors are the only monitor capable of catching fish in deep water. In some parts of its range, it is known to eat juvenile crocodiles.
Mangrove monitors in the Southern Mariana Islands shifted major prey classes when their regular prey began declining. The monitors were known for eating shrews on Guam, but the introduction of the brown tree snake (Boiga irregularis) led to decreased shrew numbers, prompting the monitors to switch to eating invertebrates and foraging through human garbage.
The species lacks distinct sexual dimorphism, but mature male monitors on Guam have been reported to be three times the mass of mature females. Males fight for females, and in one observation, after mounting the female, the male used his chin to rub the dorsum of the female's head and forequarters. While mounted and oriented head to head, the male and female slowly rotated in a clockwise direction through 360°, with the male remaining superior.
Female mangrove monitors lay two to 12 eggs that measure 3.5 to 5 cm in length. The oblong eggs are white, and hatch in about seven to eight months.
The first successful captive breeding of this species was at the Philadelphia Zoo in 1993.
The Reptilian Zoo in Vlissingen, the Netherlands, was reported to have successfully hatched eggs by a female animal which was not in any contact with a male of the same species.
Humans have introduced the mangrove monitor to a number of Pacific Islands since the 1930s. They have been present on Ifaluk in the western Caroline Islands since the Second World War. The Japanese introduced the lizards to the Marshall Islands prior to World War II to eliminate rats; the lizards flourished and soon began to raid the local chicken houses. When American troops arrived, the locals asked them for help in getting rid of the mangrove monitors. The US response was to introduce the marine toad (Bufo marinus) which proved toxic to the lizards. As the monitor population dropped, however, the rat population began to rise. Marine toads were introduced to the Palau Islands for a similar reason, and the demise of the mangrove monitors led to an increase in numbers of beetles known to be harmful to coconuts.
The mangrove monitor is hunted in many places for its skin, which is used for leather in making drum heads. Although international trade in this species is small, Mertens referred to it as one of the most heavily exploited monitor lizards. In 1980, trade in over 13,000 monitors was declared. However, in many remote places, they are used as a food source and are killed because of their reputation for preying on domestic animals. An ethnic group on Guam eats the monitors as a traditional food, and a business there sells monitors for food.
The United States Department of Agriculture’s Animal and Plant Inspection Service announced it will use a combination of two poisons, diphacinone and brodifacoum, to kill off the rodents on Cocos Island. They will also attempt to lower the mangrove monitor population on Cocos Island by 80%, using a myriad of trapping methods proposed by herpetologist Seamus Ehrhard, as the lizard is believed to prey upon the endangered Guam rail (Gallirallus owstoni). Most locals, however, do not see the monitor as an invasive species and a few activists are opposed to the attempt to lower the population there.
Mangrove monitors are often kept in zoos and private collections, as they are an active and alert, and generally can be handled if tamed properly. Most specimens defecate on their handlers when stressed. With proper care they can live up to 20 years in captivity.
Head of a mangrove monitor, Muséum National d'Histoire Naturelle, Paris
^ abDaudin, F.M. (1802). Histoire Naturelle, génerale et particulièredes reptiles, ouvrage faisant suite, a l'histoiure naturelle, générale et particulière composée par Leclerc de Buffon, et redigée par C. S. Sonnini (in French) 3. Paris.
^ abcUchida, T. (1967). Observations on the monitor lizard, Varanus indicus (Daudin) as a rat control agent on Ifaluk, Western Caroline Islands. Micronesica 3(1):17-18
^Love, J.W. (2/1/2008). "Australia and the Pacific Islands". Garland encyclopedia of World Music (Routledge) 9: 1008. ISBN0-8240-6038-5.Check date values in: |date= (help);|accessdate= requires |url= (help)
^ abSprackland, R. G. (1993). Rediscovery of a Solomon Islands monitor lizard (Varanus indicus spinulous) Mertens, 1941. Vivarium 4(5):25-27.