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Sus verrucosus

Taxonomy (Name)

Class MAMMALIAIUCN
Order CETARTIODACTYLAIUCN
Family SUIDAEIUCN
Scientific Name Sus verrucosusIUCN
Author Boie, 1832IUCN
Synonyms  
Common Name Javan Warty Pig, Javan PigIUCN
Local name Brunei Darussalam  
Cambodia  
China  
Indonesia  
Japan  
Lao PDR  
Malaysia  
Myanmar  
Mongolia  
Philippines  
Singapore  
Republic of Korea  
Thailand  
Vietnam  

 

Picture

 

 

Distribution, Range

The Javan warty pig is endemic to Indonesia. Historically the species was present on Java, Madura Island and Bawean Islands; now the species is very fragmented into small pockets of suitable habitat (Grubb 2005). It is extinct on Madura (Semiadi and Meijaard 2006). Two subspecies are recognized. The nominate form, S. v. verrucosus, occurs on Java (and formerly Madura) where it is sympatric with Sus scrofa vittatus. The second subspecies, S. v. blouchi is confined to Bawean Island in the Java Sea where it is also sympatric with Sus scrofa vittatus. This species was widespread on Java as recently as 1982 (Semiadi and Meijaard 2006), but is now absent from most of the island, and is surviving only in highly fragmented populations.

IUCN

Map

Country

Brunei Darussalam  
Cambodia  
China  
Indonesia checkIUCN
Japan  
Lao PDR  
Malaysia  
Myanmar  
Mongolia  
Philippines  
Singapore  
Republic of Korea  
Thailand  
Vietnam  

 

Status

International Status

IUCN Red List Category

ENIUCN

Justification

Listed as Endangered because of a serious population decline, estimated to be more than 50% over the last three generations (approximately 18 years), inferred from an observed reduction in population size, probably due to hunting and in the extent and quality of its habitat.

IUCN

CITES

 

CMS

 

National Status

Country Category Reference
Brunei Darussalam    
Cambodia    
China    
Indonesia    
Japan    
Korea    
Lao PDR    
Malaysia    
Mongolia    
Myanmar    
Philippines    
Singapore    
Thailand    
Vietnam    

 

Ecology Discription

Appearance

 

Habitat

The species occurs both in cultivated landscapes and in teak forest plantations (Semiadi and Meijaard 2006), with the highest density thought to occur between Semarang and Surabaya on both sides of the border between the provinces of Central and East Java. Recent data (Semiadi 2008, unpubl data) indicate that near Banjar (West Java) there is a possibility of significant numbers of animals in a fragmented teak forest and mixed local and agricultural forest.

The vegetation in which they occur is dominated by mixed age teak (Tectona grandis) plantations interspersed with lalang grasslands (Imperata cylindrical), brush and patches of secondary forest. This apparently provides an optimum habitat for this species. Javan warty pigs are everywhere restricted to elevations below about 800 m. The reasons for this are not known, but it might be due to their being unable to tolerate low temperatures (Blouch 1993). They evidently prefer secondary or disturbed forests, though they are also often found near the coasts in remnant patches of mangrove and swamp forest such as in Pangandaran (West Java) and Cilacap (Central Java). They are rare in the few remaining lowland primary forests, and in areas with high human populations where otherwise suitable habitat is fragmented and surrounded by agricultural land. However, they do feed on crops, making nocturnal raids on fields of corn and cassava and, in common with Sus scrofa, the species is widely persecuted for such depredations (Blouch 1988).

IUCN

Population size

The species occurs in at least 10 isolated areas on mainland Java, although some additional, probably very small populations, might survive elsewhere (Semiadi and Meijaard 2006). For example, recently another pocket area was found in Banjar (West Java), though intensive survey work is needed to establish the size of the area and the population (Semiadi 2007, unpubl. data). There are no estimates of overall population size, but the species has shown a rapid population decline in recent decades. Compared to a survey conducted in 1982, 17 of the 32 (53%) populations are extinct or have dropped to low encounter rate levels (Semiadi and Meijaard 2006).

Semiadi and Meijaard (2004), as a result of widespread interviews, reported the species from the following areas:
1. S. verrucosus occurs in the area between Malingping and Rangkasbitung, but is rarely encountered. There were no reports of recent kills of verrucosus, but some were shot several years ago. Semiadi and Meijaard (2006) considered that that a small population probably remains. However, because S. scrofa is a major agricultural pest, hunting intensity is high
2. Pigs are common in the area between Sukabumi and the coastal nature reserve of Cikepuh, and are considered a major agricultural pest. S. verrucosus, however, is rarely encountered, with two hunters reporting that they had not shot one since 1998. One hunter suggested that over-hunting was the most likely cause of the species' decline.
3. Interviewees in the area near Purwakarta reported the presence of S. verrucosus between the 1960s and 1990s, with steady declines of the weight of killed animals and numbers of pigs encountered. They now consider verrucosus to be very rare, the latest report being a specimen that was shot in 2001.
4. Near and south of Garut several small populations remain, with reported sightings of S. verrucosus in 2002 and 2001.
5. Around Majalengka and towards Sumedang interviewees reported recent sightings or killings of S. verrucosus, but all emphasize that the species is now much rarer than in the past. Pigs are much sought after here for illegally organized fights with dogs.
6. A population of S. verrucosus still exists east of Tasikmalaya towards Ciamis. There were several reports of recent sightings or killings. Still, people consider S. verrucosus to be rare in comparison to S. scrofa.
7. Several interviewees reported recent sightings of verrucosus from the area around Cilacap, Cipatujuh, and Nusakambangan Nature Reserve, including some from the Nusakambangan Nature Reserve offshore Cilacap, but the species seems to be rare and fragmented into many small populations.
8. S. verrucosus is still relatively common around Subah, generally seen in small groups of 1?2 animals, but in up to 4?6 animals/group during mating season. Females with young are seen between August and December. S. verrucosus has not declined as much as S. scrofa, but one interviewee expected rapid population declines of the former because teak forests, its prime habitat, are disappearing.
9. S. verrucosus appears to be relatively common around Blora and Bojonegoro, and every interviewee was familiar with the species and confirmed its local presence. Still, according to one interviewee, the species used to occur in groups of 10?20 animals, but now only 1?3 animals/group are encountered. Five to seven years ago, every hunt resulted in the capture of 1?2 S. verrucosus, or 2?3 according to another informant, but now the species is rarely caught; the most recent one in April/May 2003. One interviewee reported that pigs have especially declined since the fall of President Suharto in 1998, because then local people started to log the state-owned teak forests.
10. Bawean island is the only area where the subspecies S. v. blouchi occurs. Several interviewees reported the presence of S. verrucosus on the island, but all sightings predated 2002, and the reports gave the impression that the species was now rare. A recent (c. 2004) survey of Bawean deer Axis kuhli on Bawean Island also yielded disturbing reports of the likely dramatic diminution of this species and all wild pig populations (including S. v. blouchi) on Bawean Island, reputedly as a consequence of severe hunting pressure following the transmigration settlement of Christian communities from Sumatra (these animals having been previously left mostly undisturbed by the formerly predominant Moslem communities; R. Ratajszsak, unpubl; pers. comm. to W. Oliver).

IUCN

Behavior

 

Diet

 

Reproduction

 

 

Threat

Major Threat(s)

Semiadi and Meijaard (2006) hypothesized that the population decline observed in this species is primarily caused by a decline in suitable habitat, especially of stands of teak Tectona grandis forest or similar forest plantations, and by high hunting pressure. With the imposed regulation by the government for teak plantation forests to adopt a mixed agriculture system (agroforestry system) by cultivating agricultural products in between the young teak plantations, teak plantation forests become suitable S. verrucosus habitat. However, a 35-50 year cycle of teak forest harvest remains a threat for the availability of this habitat. In any case, there is extensive illegal logging of teak plantations, no doubt to the detriment of S. verrucosus. These animals are killed both by sport hunters and by farmers protecting their crops (Blouch 1995). Many animals are killed by poisoning (Semiadi and Meijaard, 2006). As yet unpublished reports of the recent dramatic reduction in numbers, possibly resulting in the extirpation, of S. v. blouchi, on Bawean Island have been attributed to correspondingly increased hunting pressure following the recent settlement of Christian immigrants from Sumatra; these animals having been previously left largely unharmed by the predominantly Moslem inhabitants. Competition from and hybridization with the Eurasian wild pig, Sus scrofa has been speculated as a further threat to S. verrucosus, especially in areas where human induced habitat changes have favoured S. scrofa, though there is little direct evidence for this and the two species evidently occur sympatrically in some areas, including Bawean Island.

IUCN

 

Conservation and Measurement

International

 

National

 

Conservation law

Country Status Reference
Brunei Darussalam    
Cambodia    
China    
Indonesia    
Japan    
Korea    
Lao PDR    
Malaysia    
Mongolia    
Myanmar    
Philippines    
Singapore    
Thailand    
Vietnam    

Protected Area

 

Other Coservation Projects

Javan warty pigs are poorly represented in existing protected areas. Creation of three new nature reserves and expansion of two existing reserves of importance to the taxon were recommended (Blouch 1993). In addition, surveys of the extent of market hunting should be undertaken with the objective of formulating means to regulate or eliminate the practice, and ecological research and investigation on crop damage should be conducted. Captive animals need to be administered under a properly structured plan for the long term genetic and demographic benefit of the species.

Efforts to corroborate and document recent reports of the dramatic reduction in the numbers of S. v. blouchi and other threatened endemic taxa on Bawean Island are also required as a matter of urgency and with view to the institution of more effective protective measures being implemented in the Bawean Island Wildlife Reserve and other parts of this island, especially against hunting by recent immigrant communities.

Currently (2008) a project to establish a captive breeding population of S. v. verrucosus is underway by collecting founders from zoos and from the wild. The aim is to establish a captive population that reliably produces offspring later to be reintroduced in selected protected habitats.

IUCN

 

Citation

Blouch, R. A. 1993. The Javan warty pig (Sus verrucosus). In: W. L. R. Oliver (ed.), Pigs, Peccaries, and Hippos: Status Survey and Conservation Action Plan, IUCN, Gland, Switzerland.

Blouch, R. A. 1995. Conservation and research priorities for threatened suids of south and southeast Asia. Ibex - Journal of Mountain Ecology 3: 21-25.

Grubb, P. 2005. Artiodactyla. In: D. E. Wilson and D. M. Reeder (eds), Mammal Species of the World. A Taxonomic and Geographic Reference (3rd ed), pp. 637-722. Johns Hopkins University Press, Baltimore, USA.

Semiadi, G. and Meijaard, E. 2004. Survey of the Javan Warty Pig (Sus verrucosus) on Java and Bawean Island. Pusat Penelitian Biologi-LIPI and IUCN/SSC Pigs, Peccaries and Hippos Specialist Group, Bogor, Indonesia.

Semiadi, G. and Meijaard, E. 2006. Declining populations of the Javan warty pig Sus verrucosus. Oryx 40: 50-56.

IUCN