Site icon THE FIGS OF BORNEO

Overview: Fig density = Gibbon density

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North Borneo Gibbon Hylobates funereus eating ripe yellow/green Ficus variegata figs at Tabin Wildlife Reserve in E. Sabah. Note that F. variegata figs may ripen any colour from green to bright red  depending on the individual tree.

Studies show that the population of gibbons and figs is closely related both within and outside Borneo. The higher the density of figs the higher the density of gibbons.

Zoologists recognize 4 different gibbon species in Borneo but their ranges only rarely overlap  and when they do hybrids occur. So far as is known there is no difference in ecology between the different species.

After the Langurs (8 species) the 4 species of Borneo gibbons are the most common large fruit eating primate in undisturbed virgin forest.

Gibbons live in small family groups normally two adults and one to two juveniles. Adults patrol the boundaries of their forest patch daily and defend their territory with loud early morning calls. Note that the gibbon density figures below refer to individuals per km 2 based on the number of territories  and the average number of individuals per family.

 

Gibbon density in Borneo typically ranges from 4-21 individuals per 100 ha. Numerous studies have found that the density of gibbons is closely correlated to the density of figs growing in each gibbon territory. The higher the density of figs the higher the food availability and the “carrying capacity” of the forest and the smaller the territory.  Ulu Temburong, in Brunei has the highest density of gibbon families in Borneo. This may be due to the abundance of figs but also due to the the absence of orangutans.

The relationship between fig density and gibbon density was confirmed by studies carried out at Gunung Palung in SW Kalimantan by Marshall and Leighton (2006).

White-bearded Gibbons Hylobates alibabaris at Gunung Palung, West Kalimantan were researched  in the forest surrounding the Cabang Panti Research Station (CPRS) by Marshall & Leighton (2006) over 69 months between 1985 and 2002.  Gibbons typically preferred to eat ripe non-fig fruits which are prone to fruiting in one big bang and were only available 14% of the time. In the long lean period between masts (86% of the time) gibbons ate fall back foods figs, flowers and young leaves which are nearly always available.

The variations in gibbon density in 7 different habitats at Cabang Panti Research Station Gunung Palung almost exactly matched the density of figs in each habitat. The authors hypothesized that “fig densities limit gibbon populations through the effect on female condition during periods of low food availability which in turn affects birth rates”

Cline et al  (2017) also at Gunung Palung compared the diet of gibbons and Red Langurs Presbytis rubicunda between 2007- 2013. Their research showed that the gibbon population was limited by the availability of their fall back foods mainly figs whilst the population of langurs was limited by the availability of langur preferred food – unripe fruit seeds.

Overall 27% of gibbon diet came from figs whilst only 14 % of langur diet was figs.  During lean seasons gibbons eat figs  whereas langurs eat leaves which are always available.

Marshall & Leighton (2006) Gibbon & fig density correlated Gng Palung

Clink et al (2017) Diet of gibbon and langur at Gng Palung compared

Mather (1992) Phd Field Study of Hybrid Gibbons Kalimantan Chap 5 only

 

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