ArticlePDF Available

Observation of a fatal dog attack on a juvenile long-tailed macaque in a human-modified environment in Singapore

Authors:

Abstract and Figures

Direct observations of predation on primates are rare, in part because the presence of observers deters potential predators. We observed domestic dogs (Canis lupus familiaris) kill and take away a juvenile long-tailed macaque (Macaca fascicularis), presumably for consumption, in Singapore’s Bukit Timah Nature Reserve. We describe the event and reaction by group members in detail. We also compare our observation to reported accounts of predation on long-tailed macaques. In doing so, we discuss factors that increase predation risk for long-tailed macaques in anthropogenic environments. Dogs may not be important predators of primates in natural habitats, but currently they are important predators of long-tailed macaques in anthropogenic environments. This is because a large proportion of long-tailed macaques now live near humans. Anthropogenic environments differ from the forest environments to which long-tailed macaques are most adapted. Compared to forests, anthropogenic environments are more open, contain novel structures, and require more terrestrial locomotion. These differences pose novel ecological challenges that increase macaques’ susceptibility to predation by dogs. Features of primate juvenility leave young macaques especially vulnerable to dog predation. Young macaques have small body size and frequently play, which reduces their vigilance to predators. In sum, greater exposure to anthropogenic environments increases the risk of long-tailed macaques—especially juveniles—to predation by dogs.
Content may be subject to copyright.
57
NATURE IN SINGAPORE 2015 8: 5763
Date of Publication: 24 August 2015
© National University of Singapore
OBSERVATION OF A FATAL DOG ATTACK ON A
JUVENILE LONG-TAILED MACAQUE
IN A HUMAN-MODIFIED ENVIRONMENT IN SINGAPORE
Crystal M. Riley1*, Bryan L. Koenig2 and Michael D. Gumert3
1Department of Anthropology, Washington University in St. Louis
Campus Box 1114, 1 Brookings Drive, St. Louis, MO 63130, USA
2University College, Washington University in St. Louis, MO 63130, USA
3Division of Psychology, Nanyang Technological University
14 Nanyang Drive Singapore 637332, Republic of Singapore
(*Corresponding author: crystalmriley@wustl.edu)
ABSTRACT. Direct observations of predation on primates are rare, in part because the presence of observers deters
potential predators. We observed domestic dogs (Canis lupus familiaris) kill and take away a juvenile long-tailed
macaque (Macaca fascicularis), presumably for consumption, in Singapore’s Bukit Timah Nature Reserve. We describe
the event and reaction by group members in detail. We also compare our observation to reported accounts of predation
on long-tailed macaques. In doing so, we discuss factors that increase predation risk for long-tailed macaques in
anthropogenic environments. Dogs may not be important predators of primates in natural habitats, but currently they are
important predators of long-tailed macaques in anthropogenic environments. This is because a large proportion of long-
tailed macaques now live near humans. Anthropogenic environments differ from the forest environments to which long-
tailed macaques are most adapted. Compared to forests, anthropogenic environments are more open, contain novel
structures, and require more terrestrial locomotion. These differences pose novel ecological challenges that increase
macaques’ susceptibility to predation by dogs. Features of primate juvenility leave young macaques especially
vulnerable to dog predation. Young macaques have a small body size and frequently play, which reduces their vigilance
to predators. In sum, greater exposure to anthropogenic environments increases the risk of long-tailed macaques
especially juvenilesto predation by dogs.
KEY WORDS.Macaca fascicularis, Canis lupus familiaris, predation, prey, juvenile, Singapore
INTRODUCTION
Predation may be a key selection pressure for primate sociality (Alexander, 1974). Larger groups, for example, detect
predators at greater distances (van Schaik et al., 1983). Relatively little is known, however, about what occurs during
and after predation events. Direct observations are unfortunately rare in the literature (Isbell, 1994), perhaps because
many predators avoid humans, including scientists (Cheney & Wrangham, 1987). Although difficult to collect en masse
for publication, observations of rare events such as predation are important for understanding primate behaviour. Here,
we report an observed fatal attack on a long-tailed macaque by domestic dogs in Singapore and the immediate social
aftermath.
Long-tailed macaques (Macaca fascicularis) are a forest edge-dwelling species that regularly utilise human habitats
(Gumert, 2011). One of the most abundant and widespread non-human primate species, they are among the most
studied macaque species in the wild. Nevertheless, accounts of predation on long-tailed macaques are rare. First-hand
information from observation, necropsy, and remains found in predator faeces indicate that successful predators of wild
long-tailed macaques include the false gharial (Tomistoma schlegelii) (Galdikas & Yeager, 1984), reticulated pythons
(Malayopython reticulatus) (van Schaik et al., 1983), and domestic dogs (Canis lupus familiaris) (Hock & Sasekumar,
1979), among other predators. Table 1 summarises documented instances of predators killing long-tailed macaques
from primary literature. The table includes only accounts of killing by non-human predators.
Anderson (1986) lamented the lack of details in reports of observed predation events, so we provide a detailed account
that includes information relevant for researchers of diverse interests. We then relate our account to theory by
discussing factors that increase the risk of long-tailed macaque predation by dogs. We also address features of
anthropogenic habitats and aspects of juvenility that increase susceptibility of long-tailed macaques to dog attacks.
As part of a project focusing on social behaviour, CMR and MDG began in Sep.2009 to collect data on a group of long-
tailed macaques in Singapore’s Bukit Timah Nature Reserve. This 163-ha nature reserve includes mostly areas of
secondary forest, with fragments of primary coastal hill dipterocarp forest, contains hiking and mountain-biking trails
(National Parks Board Singapore, 2009), and has apartments and condominiums adjacent to it. The macaque
Riley et al.: Fatal Dog Attack on Macaque
58
Table 1. First-hand, confirmed incidences of predators killing long-tailed macaques (Macaca fascicularis). Instances included in the
table were either observed first hand by researchers, or inferred from necropsy remains or group composition. It excludes reports
about macaques merely reacting to the presence of predators, reports in which macaques were injured but not killed, and secondhand
reports from untrained observers to researchers.
S/No.
Predator
Source
Locality
Reference
Notes
1.
false gharial
(Tomistoma
schlegelii)
Direct observation
Indonesia
Galdikas & Yeager
(1984)
Juvenile macaque
2.
reticulated python
(Malayopython
reticulatus)
Direct observation
Indonesia
van Schaik, van
Noordwijk, Warsono,
& Sutriono (1983)
Juvenile macaque
3.
Komodo monitor
(Varanus
komodoensis)
Remains in Komodo
monitor faecal pellets
Indonesia
Auffenberg (1981)
Canines in pellets indicate at least
2 adult macaques
4.
leopard (Panthera
pardus)
Remains in leopard
faecal
Indonesia
Seidensticker,
Suyono, & Thomas
(1980)
Ten instances, including "teeth of
old and young individuals," (p.
63)
5.
tiger (Panthera
tigris)
Remains in tiger faecal
Indonesia
Seidensticker,
Suyono, & Thomas
(1980)
Two instances
6.
Philippine eagle
(Pithecophaga
jefferyi)
Direct observation
Philippines
Kennedy (1977)
Prey described only as a monkey;
M. fascicularis only native
monkey
7.
Philippine eagle
Undigested monkey in
eagle’s stomach
Philippines
Clemens (1907)
Prey described as monkey; M.
fascicularis only native monkey
8.
Philippine eagle
Observation of eagle
pair's nest
Philippines
Gonzales (1968)
Three monkey carcasses brought
to nest
9.
estuarine
crocodile
(Crocodylus
porosus)
Direct observation
Malaysia
Otani, Tuuga,
Bernard, & Matsuda
(2012)
Adult male macaque
10.
domestic dog
(Canis lupus
familiaris)
Examination of
deceased juvenile
Malaysia
Hock & Sasekumar
(1979)
Juvenile macaque
11.
domestic dog
Inferred from group
composition and dog-
macaque overlap
Thailand
Gumert, Hamada, &
Malaivijitnond (2013)
Likely multiple incidences
focused on infants and juveniles
12.
domestic dog
Direct observation
Singapore
Ridley (1895)
Author's pet terriers killed a
macaque
13.
domestic dog
Direct observation
Singapore
this paper
Juvenile macaque
group had approximately 55 members, which is within the range of groups given access to human food (van Schaik et
al., 1983; Fooden, 1995). As part of that project, CMR was collecting faecal and scan samples of adult individuals (all
of whom were individually identified) and was in the process of identifying the juvenile macaques in the group. It was
on one of these data collection outings that a fatal dog attack on a macaque was observed.
OBSERVATION
On 10 Feb.2010, at 1235 hours, CMR and MDG, along with visiting researcher Ronald Noë, were watching the group
forage. Two-thirds of the macaques were in the trees and the remainder on the ground, along the Bukit Timah Nature
Reserve Chestnut Mountain Biking Trail, situated on the edge of the forest approximately 15 m behind an apartment
building. Without forewarning three large feral dogs ran silently towards the macaques, passing within 2 m in front of
the researchers. Apparently unaware of the dogs, the macaques did not respond until the dogs were about 3 m from the
closest group members. At that point, multiple macaques began alarm calling and most darted into the trees. Last on the
ground were three juveniles. A dog caught and killed one of them. The other two juveniles sprung into the trees,
narrowly evading the remaining two dogs that had rushed towards them. Within a minute of biting the juvenile to death,
the dogs abandoned its body without consuming any of it. Two dogs ran west down a hill and out of sight behind the
apartment building. The dog that had killed the macaque ran northeast toward the nearby Hindhede Quarry.
Within a couple minutes of the dogs leaving, adult male macaques made what appeared to be a perimeter in the trees at
a radius of about 5 m around the deceased juvenile. Group members made alarm calls for about 20 min. The researchers
failed to identify the deceased macaque or collect a biological sample for genetic analysis because attempts to approach
the body resulted in the adult males lunging, grunting, and baring their teeth. To avoid further disturbing the agitated
group, the researchers left at approximately 1330 hours.
NATURE IN SINGAPORE 2015
59
When the researchers returned at 1445 hours, the group resumed alarm calling. Between 13301445 hours, one of the
dogs had returned and moved the deceased macaque from the bike path to about 10 m into the forest. There the dog that
had killed the macaque lay with the body between its paws (Fig. 1). At 1505 hours, the dog stood and walked away,
leaving the body behind (Fig. 2). The group continued alarm calling for about two minutes after the dog moved out of
sight. Two researchers then departed. The other (CMR) remained to observe the group.
Soon thereafter, some group members approached the body. Uma, the 14th-ranked adult female (out of 15), moved
repeatedly back and forth between a tree and the body. She would stop about 1 m from the body, stare at it, then climb
the tree again. The third-ranked adult female, Keira, remained on the tree branch directly above where the dog had
killed the macaque, staring at the spot on the ground where the body had been before the dog moved it. Both females
periodically made distress coos. Three juveniles, together, approached the body to within about 3 m and then stopped.
At that distance for several minutes, they expressed silent-bared-teeth displays towards the body, teeth-chattered,
screamed, mounted one another, and embraced one another. Then while two of the juveniles moved away, the other
inched slowly toward the body, reached out, touched it, pulled its hand away quickly, and ran back to the other two
juveniles.
Over the next two hours, the two adult females mentioned above continued to gaze at the body periodically. Other
group members resumed foraging in the trees and on the ground. The group maintained a loose perimeter around the
body. At 1715 hours, the same dog reappeared, causing the macaques to alarm call again. The dog picked up the body
of the macaque and departed, heading back towards the quarry carrying the body of the deceased macaque in its mouth.
The entire group stayed by the location at least five hours after the event beganlonger than they would remain in one
place on an ordinary day.
We reported the observed event to the local authorities, the National Parks Board of Singapore (NParks). NParks
officers investigated the area and reported finding a “dog nest” approximately 20 m from the site of the killing. In
Singapore, owing to concerns about danger to people, feral dogs are sometimes trapped and rehomed or culled (Tan,
2011). In this case, however, the officers decided not to trap the dogs. The researchers saw these specific dogs in the
area only one more time after the event.
Fig. 1. Dog and the juvenile macaque it killed. (Photograph by: Crystal M. Riley).
Riley et al.: Fatal Dog Attack on Macaque
60
Fig. 2. Temporarily abandoned body of juvenile macaque. (Photograph by: Crystal M. Riley).
DISCUSSION
Many aspects of the observed event are notable. Regarding the aftermath, macaques responded differently depending on
their demographics. Adult males took what looked like a protective stance. Two adult females seemed especially
concerned about the dead macaque; perhaps they were relatives. Three juveniles acted curious but scared regarding the
dead body. However, our discussion identified elements of the event that might be considered typical and shows how
they relate to key themes in literature. The three feral dogs were undeterred by humans nearby. The event occurred on a
man-made bike path with a fence on one side, an evolutionarily-novel context for macaques. The individual killed was
young and interacting with other juveniles and therefore particularly vulnerable to predation. We consider these
interrelated topics in turn.
Dogs are important predators of long-tailed macaques in human-modified environments. We witnessed a dog kill,
but not eat, a macaquebut canid predatory behaviour suggests the dog likely consumed it later. The consumption of
prey is an important aspect of predation, which is broadly defined as “an organism killing another organism for
nutritional purposes” (Bengston, 2002: 289). Some predators, particularly canids, take prey to a secluded location
before consuming them (Fox, 1969; Fox, 1971). Based on such patterns of canine behaviour following the killing of
prey, we assume the dog later ate some portion of the macaque in the event we observed. The dog moved the macaque
away from where it was killed, possibly because the dog was uncomfortable consuming the macaque in the researchers’
presence. Given the later discovery of a dog nest20 m away, it seems likely that the dog carried the macaque there (a
known location secluded from people) to eat it. There is evidence of dogs killing animals and not eating them (e.g.,
Coppinger & Coppinger, 2001); however, those reports were by dog owners. Feral dogs obtain their own food so they
seem unlikely to kill prey simply to abandon it. Thus we conclude that what we observed was a predation event. This is
consistent with other published accounts that refer to dogs killing wildlife as predation, despite the researchers not
observing the dogs consuming their kills (e.g., Young et al., 2011). Even if the dog abandoned its kill, the evolutionary
effect is the same for the deceased individual. As Bengston (2002) pointed out, “The central aspect of the definition of
predation is that it kills the victim” (p. 289).
NATURE IN SINGAPORE 2015
61
In an overview of dog predation on primates, Anderson (1986) concluded that dogs are unimportant predators of
primates generally; however, they might be important predators of long-tailed macaques. This is because both dogs and
long-tailed macaques are commonly found around human settlements in Southeast Asia (Anderson, 1986). Moreover,
long-tailed macaques on the ground (like the macaque reported in our observation) are more susceptible to predation by
dogs than macaques in trees, and macaques utilising open spaces spend up to a quarter of their time on the ground
significantly more than when in the forest (Fooden, 1995). Long-tailed macaques therefore likely face increased
susceptibility to dog attacks in open anthropogenic habitats as compared to in more forested environments.
Indeed, a literature review suggested that dogs are important predators of long-tailed macaques. Of 25 confirmed
instances of long-tailed macaques being killed by a total of eight predator species (see Table 1), three were by dogs
(12% of the total). This makes the dog the third most reported long-tailed macaque predator, after the leopard (10
instances, 40% of the total), and the Philippine eagle (five instances, 20% of the total). These estimates are imprecise, of
course, owing to the aforementioned infrequency of researchers observing predation events. Our estimate of dog
predation is likely low, for example, given the evidence of Gumert et al. (2013) that dog predation can significantly
affect group composition.
In Singapore, stray dogs are a common and significant part of the anthropogenic environment. As of 2012, Singapore
had an estimated 8,000 stray dogs (Tan, 2012), a substantially larger number than the long-tailed macaque population
estimated at 1,900 individuals (Riley et al., 2013). Domestic dogs thus have potential to be a key predator of long-tailed
macaques in Singapore and similar anthropogenic habitats where distributions of dogs and macaques overlap, as occurs
regularly in Southeast Asia (Anderson, 1986). Macaques living in such environments risk death and injury due to
predation by domestic dogs, but the mere presence of dogs as potential predators entails costs, including disruptions of
group composition, habitat use, and group activity patterns (Anderson, 1986; Young et al., 2011; Gumert et al., 2013).
A recent study found this to hold for long-tailed macaques on Piak Nam Yai Island in Thailand. Macaques there have
been largely undisturbed by anthropogenic influence, but humans recently encroached on macaque habitat and
introduced domestic dogs. Those dogs chase macaques, potentially disrupting their unique tradition of stone tool use
(Gumert et al., 2013). Gumert and colleagues observed 15 interactions between dogs and macaques but did not directly
observe predation. They noted, however, that macaque groups whose ranges overlapped with locations where dogs were
seen most frequently had fewer juveniles and more regularly had younger animals disappear, suggesting predation.
Furthermore, macaque groups whose ranges overlapped with those of dogs spent less time foraging on open shores.
This may have been a response to dog predation because being on open shores made the macaques more vulnerable to
dogs.
Long-tailed macaques living in modern anthropogenic habitats face challenges to which they were not necessarily
adapted. Human-modified environments are generally more exposed and open, likely increasing terrestrial locomotion
(Fooden, 1995). They also contain evolutionarily novel structures (e.g., buildings, roads, and fences) that would have no
adaptive relevance to macaques’ historical environments. Anthropogenic habitats indeed differ substantially from
swamp or riverine forest habitats to which long-tailed macaques are most adapted (Gumert, 2011). This mismatch
between the novel ecological setting of a human-altered environment and macaque history of adaptation in less
disturbed environmentsmight make long-tailed macaques more vulnerable to predator species such as dogs that are
well adapted to human environments.
Through artificial and natural selection, humans transformed wolves into dogs. Dogs rapidly evolved traits to make
them suitable to live near humans and in human environments (Coppinger & Coppinger, 2001). Macaques have
likewise lived near humans for a long time (Gumert, 2011), and they too likely face selection pressures from humans
and human environments (Gumert et al., 2011). Despite this, macaques (and other wildlife) probably have experienced
less anthropogenic selection pressure than have dogs, and are less well suited to human-modified environments than are
dogs. Therefore, they likely suffer a disadvantage relative to dogs in human-modified environments.
Macaques are not the only animals affected by sharing their habitat with dogs. Other wildlife is also at risk of predation
and social disruption by dogs. A monkey that was presumed to be the last banded leaf monkey (Presbytis femoralis) in
the Bukit Timah Nature Reserve in Singapore was killed by dogs (Yang & Lua, 1988). Singapore is home to many
other mammals upon which feral dogs could potentially prey, such as civets, mousedeer, colugo, and squirrels. In
addition to impacting wildlife through predation and altered behavioural patterns, dogs may also transmit pathogens to
native wildlife and even to humans (Young et al., 2011).
Juveniles are especially at risk for predation by dogs in human-modified environments. A review of primate
predation shows that for primates, including long-tailed macaques (van Schaik et al., 1983), infants and juveniles are at
greater risk of being preyed upon than adults (Cheney & Wrangham, 1987), as smaller immature animals are more
vulnerable than adults. Juvenile primates are less vigilant and less adept at detecting predators than adults (Janson &
van Schaik, 1993). Galdikas & Yeager (1984) observed that young macaques were more careless and less vigilant than
adults.
Riley et al.: Fatal Dog Attack on Macaque
62
Play also entails increased predation risk for younger primates (Fagen, 1993). During social play immature primates
focus attention towards conspecifics, which diminishes attention available for predator detection. Owing to increased
vulnerability of the young, adults in many primate species are more vigilant near playing infants and juveniles (Fagen,
1993). In our observed event, the juvenile victim was close to two other juveniles, likely interacting with one another
and therefore perhaps less aware of their surroundings. The environment was human-modified, so perhaps its openness
or other features made it harder for adults to monitor and/or to rescue juveniles from danger.
We suggest that juvenile primates in anthropogenic environments with domestic dogs may be at especially high risk.
This is because the effects of the human-modified ecology are compounded by the greater vulnerability of immature
animals. For example, we observed an event on 13 Jan.2010 that demonstrated these factors. At Hindhede Place, just
outside the Bukit Timah Nature Reserve, CMR and MDG saw a woman release her small pet dog from a fenced yard.
The dog immediately chased a group of several immature monkeys that were playing in the street. These young
macaques were unaware of the dog running at them, despite adult alarm calls. The dog ran directly towards an infant,
picked it up in its mouth, and shook it. The adults immediately ran to the defence of the infant. During the mobbing one
female jumped on the dog and bit it. The dog dropped the infant and retreated. The infant fled to a nearby gate, leapt,
lost hold of the gate and fell to the ground, leapt again, and clung onto the gate at about a foot off the ground. The infant
was then retrieved by an adult femalelikely the infant’s motherthat had earlier bitten the dog. This event illustrates
risks for young macaques: The dog went after the smallest individuals and play distracted young macaques from the
threat.
The relationship between dogs and primates in human-modified environments is an underexplored aspect of
commensal-living primates, such as long-tailed macaques. To better understand how human environments influence the
behaviour and evolution of primates and other wildlife attracted to anthropogenic environments, we would do well to
understand selection pressures in these habitats, such as enhanced vulnerability to predators. Dogs are indeed a
significant predator of long-tailed macaques in human-modified environments, but to what degree are they a selective
pressure? Future research can answer this question and improve our understanding of the role of human-modified
environments on non-human primate evolution.
ACKNOWLEDGEMENTS
We thank the National Parks Board of Singapore for their assistance and support, and Crickette Sanz and Ronald Noë
for their helpful comments on a previous version of this manuscript. This research was funded by a Tier One grant
RG95/07 from Singapore’s Ministry of Education.
LITERATURE CITED
Alexander, R. D., 1974. The evolution of social behavior. Annual Review of Ecology and Systematics, 5: 325–383.
Anderson, J. R., 1986. Encounters between domestic dogs and free-ranging non-human primates. Applied Animal
Behaviour Science, 15: 71–86.
Auffenberg, W., 1981. The Behavioral Ecology of the Komodo Monitor. University of Florida Press, Gainesville,
Florida. 406 pp.
Bengston, S., 2002. Origins and early evolution of predation. Paleontological Society Papers, 8: 289–317.
Cheney, D. L. & R. W. Wrangham, 1987. Predation. In: Smuts, B. B., D. L. Cheney, R. M. Seyfarth & R. W.
Wrangham (eds.), Primate Societies. University of Chicago Press, Chicago. Pp. 227–239.
Clemens, J., 1907. Notes from the Philippines. Condor, 9: 9293.
Coppinger, R. & L. Coppinger, 2001. Dogs: A Startling New Understanding of Canine Origin, Behavior & Evolution.
Scribner, New York, 352 pp.
Fagen, R., 1993. Primate juveniles and primate play. In: Pereira, M. E. & L. A. Fairbanks (eds.), Juvenile Primates: Life
History, Development and Behavior. University of Chicago Press, Chicago. Pp. 183196.
Fooden, J., 1995. Systematic review of Southeast Asian longtail macaques, Macaca fascicularis, (Raffles, [1821]).
Fieldiana Zoology New Series, 81: i–206.
Fox, M. W., 1969. Ontogeny of prey-killing behavior in Canidae. Behaviour, 35: 259272.
Fox, M. W., 1971. Behaviour of Wolves, Dogs and Related Canids. Harper Collins, New York. 220 pp.
Galdikas, B. M. F. & C. P. Yeager, 1984. Crocodile predation on a crab-eating macaque in Borneo. American Journal
of Primatology, 6: 4951.
Gonzales, R. B., 1968. A study of the breeding biology and ecology of the monkey-eating eagle. Silliman Journal, 15:
461491.
Gumert, M. D., 2011. The common monkey of Southeast Asia: Long-tailed macaque populations, ethnophoresy, and
their occurrence in human environments. In: Gumert, M. D., A. Fuentes, & L. Jones-Engel (eds.), Monkeys on the
Edge: Ecology and Management of Long-tailed Macaques and Their Interface with Humans. Cambridge University
Press, Cambridge, UK. Pp. 344.
NATURE IN SINGAPORE 2015
63
Gumert, M. D., A. Fuentes, G. Engel & L. Jones-Engel, 2011. Future directions for research and conservation of long-
tailed macaque populations. In: Gumert, M. D., A. Fuentes, & L. Jones-Engel (eds.), Monkeys on the Edge: Ecology
and Management of Long-tailed Macaques and Their Interface with Humans. Cambridge University Press,
Cambridge, UK. Pp. 328353.
Gumert, M. D., Y. Hamada & S. Malaivijitnond, 2013. Human activity negatively affects stone tool-using Burmese
long-tailed macaques Macaca fascicularis aurea in Laem Son National Park, Thailand. Oryx, 47: 535543.
Hock, L. B. & A. Sasekumar, 1979. A preliminary study on the feeding biology of mangrove forest primates, Kuala
Selangor. The Malayan Nature Journal, 33: 105112.
Isbell, L. A., 1994. Predation on primates: Ecological patterns and evolutionary consequences. Evolutionary
Anthropology, 3: 6171.
Janson, C. H. & C. P. van Schaik, 1993. Ecological risk aversion in juvenile primates: Slow and steady wins the race. In:
Pereira, M. E. & L. A. Fairbanks (eds.), Juvenile Primates: Life History, Development and Behavior. University of
Chicago Press, Chicago. Pp. 5774.
Kennedy, R. S., 1977. Notes on the biology and population status of the monkey-eating eagle of the Philippines. The
Wilson Bulletin, 89: 120.
National Parks Board, Singapore, 2009. Bukit Timah Nature Reserve. National Parks Board, Singapore.
http://www.nparks.gov.sg/cms/index.php?option=com_visitorsguide&task=naturereserves&id=46&Itemid=75.
(Accessed 10 Oct.2013).
Otani, Y., A. Tuuga, H. Bernard & I. Matsuda, 2012. Opportunistic predation and predation-related events on long-
tailed macaque and proboscis monkey in Kinabatangan, Sabah, Malaysia. Journal of Tropical Biology and
Conservation, 9: 214218.
Riley, C. M., S. L. Jayasri & M. D. Gumert, 2013. Singaporean long-tailed macaque (Macaca fascicularis) population
census and status assessment: 2012. Report to the National Parks Board, Singapore. 75 + xii pp.
Ridley, H. N., 1895. The mammals of the Malay Peninsula. Natural Science, 6: 2329.
Seidensticker, J., I. Suyono & T. Thomas, 1980. The Javan Tiger and the Meru-Betiri Reserve: A Plan for Management,
International Union for the Conservation of Nature and Natural Resources, Gland, Switzerland. 167 pp.
Tan, A., 2011. No Blanket Culling of Strays, AVA Assures Dog Lovers; It’ll Continue to Work with Welfare Groups to
Rehome Stray Dogs. The Straits Times, 24 Dec.2011.
Tan, J., 2012. NParks to Trap Stray Dogs in Pilot Project; It Will Work with Animal Groups to Rehabilitate Ang Mo
Kio Pack of 20. The Straits Times, 1 May 2012.
van Schaik, C. P., M. A. van Noordwijk, B. Warsono & E. Sutriono, 1983. Party size and early detection of predators in
Sumatran forest primates. Primates, 24: 211221.
Yang, C. M. & H. K. Lua, 1988. A report of a banded leaf monkey found dying near the Bukit Timah Nature Reserve.
The Pangolin, 1: 23.
Young, J. K., K. A. Olson, R. P. Reading, S. Amgalanbaatar & J. Berger, 2011. Is wildlife going to the dogs? Impacts
of feral and free-roaming dogs on wildlife populations. BioScience, 61: 125–132.
... However, aggression between rhesus macaques and smaller predators such as dogs is commonly observed, and predation on rhesus macaque infants and unknown individuals by dogs has been reported (Anderson 1986;Chetry et al. 2005). There are several cases of dogs preying on or harassing other nonhuman primates species, including brown howler monkeys (Alouatta guariba) (da Silva et al. 2021), black howler monkeys (Aloutta pigra) (Franquesa-Soler et al. 2023), Japanese macaques (Macaca fuscata) (Hill 2014), young female and infant barbary macaques (Macaca sylvanus) (Waters et al. 2017), juvenile long tailed macaques (Macaca fascicularis) (Riley et al. 2015), and Central Himalayan langurs (Semnopithecus schistaceus) (Nautiyal et al. 2023), among others (see an early review by Anderson 1986, and recent review by Waters et al. 2023). Perhaps surprisingly, there are few published reports about rhesus macaque-dog interactions (Anderson 1986;Chetry et al. 2005), yet detailed records of such interactions are needed to understand how dogs might shape the socioecology of nonhuman primates in human-impacted landscapes (Gompper 2014). ...
... Moreover, injured or handicapped individuals (such as the first female from our study group) might also be especially likely to get attacked, owing to limited mobility. Reports exist of smaller and more vulnerable age-sex classes in other macaque species falling prey to dogs (Riley et al. 2015;Waters et al. 2023;Nautiyal et al. 2023). On the other hand, given their larger body size and well-developed canines, males often engage in predator defense strategies, such as alarm-calling or attacking the dogs (Nautiyal et al. 2023), which is a pattern that we also noticed at our study site. ...
... Not only mortality from dog attacks, but the mere presence of dogs can substantially impact the socioecology of nonhuman primates, for example, negatively affecting social behavior and foraging activities (Gumert et al. 2013;Riley et al. 2015). Direct interactions with dogs and heightened anti-predator vigilance can cause physiological stress (Rangel-Negrín et al. 2023), which might eventually even have fitness effects. ...
Article
Full-text available
For nonhuman primates living in anthropogenic areas, predation by larger predators is relatively rare. However, smaller predators, such as free-ranging as well as domesticated dogs, can shape the socioecology of urban nonhuman primates, either directly by attacking and killing them or indirectly by modifying their activity patterns. Here, we describe three (two probably fatal) cases of dog attacks on adult rhesus macaques inhabiting an anthropogenic landscape in Northern India and the circumstances surrounding these incidents. We discuss the importance of considering human presence and intervention in dog–nonhuman primate relationships while studying nonhuman primate populations across anthropogenic gradients, and its potential influences on group social dynamics and transmission of zoonotic agents.
... Roads are an important cause of forest discontinuity and pose a variety of threats to wildlife by restricting movement and/or causing direct mortality (Beckman et al., 2010;Teixeira et al., 2013). Studies in many countries have reported such threats to primate species, such as in India (Das et al., 2009), Brazil (Gordo et al., 2013), Singapore (Riley et al., 2015), Mexico (Hernandez-Perez, 2016); and Kenya (Katsis et al., 2018). Wildlife crossing structures can mitigate some of these effects by simultaneously connecting fragmented habitat and reducing negative interactions between animals and human-made infrastructure (Downs and Horner, 2011;Teixeira et al., 2013). ...
... Wildlife crossing structures can mitigate some of these effects by simultaneously connecting fragmented habitat and reducing negative interactions between animals and human-made infrastructure (Downs and Horner, 2011;Teixeira et al., 2013). Canopy bridges have been found to reduce disease transmission from wild to domestic animals, predation events by dogs, electrocutions, and roadkills (Printes, 1999;Lokschin et al., 2007;Teixeira et al., 2013;Riley et al., 2015;Azofeifa-Rojas et al., 2021). ...
Article
Full-text available
The combination of urbanization and destruction of native forests commonly has forced wild animals to search for food and shelter in urban areas. Groups of black and gold howler monkeys ( Alouatta caraya ) are moving into urban areas in Northern Argentina as a consequence of rapid alteration and degradation of their habitats. In general, local people in the area are unaware of and disconnected from conservation actions, such as the protection of local biodiversity. We aimed to address this issue by organizing a group of high school students from both the city of Corrientes and outlying rural areas with the objective of transforming their perceptions on local non-human primates and to build the inaugural canopy bridge to instill biodiversity appreciation. With the students, we identified a location to install a bridge to facilitate the movement of Alouatta caraya across areas of discontinuous canopy. The students worked to build awareness within their community, obtained the necessary permission, and designed the bridge. From the beginning of the awareness campaign to the bridge installation, the process took four years. Afterwards, we installed two more bridges in the same region. From this single case study, we learned that participatory actions are a very important tool for residents of local communities to act collectively to promote biodiversity conservation.
... Domestic dogs (Canidae) are the most globally abundant and widely distributed carnivore species, and India has one of the largest dog populations of any country (Gompper 2014;Doherty et al. 2017;Ritchie et al. 2013). Dog predation on primates is mostly reported in areas where primate species live in close proximity to humans, e.g., macaques and langurs in Asia (Anderson 1986;Riley et al. 2015;Najmuddin et al. 2019) and gelada (Theropithecus gelada) in the open highland grasslands of Ethiopia (Iwamoto et al. 1996). These landscapes are defined as being humanmodified and are comprised of forest patches surrounded by agricultural land and settlements. ...
Article
The evolution of predator-prey relationships is an important topic in primatology. Many aspects of primate society have been explained as a response to predation pressure. While predation has been discussed in broad theoretical terms, few systematically collected data exist on the subject. Furthermore, little information exists regarding the inter-male variation in responses to predators. To address this data gap, predatory dog-primate interactions were studied in a 78-member group of habituated, individually recognized Central Himalayan Langurs (CHL) (Semnopithecus schistaceus) living in a high-altitude subsistence agricultural landscape of northern India. We recorded 312 langur-dog interactions over 2 years. These predation events resulted in 15 serious attacks on adult females, infants, juveniles and sub-adults, in eight of which the prey was killed and consumed on the spot. In response to dog predation, adult males performed three types of anti-predator response behaviors: direct fighting with a predator, emitting alarm calls, fleeing and/or freezing. Differences were noted in each male's response to village dogs. The results showed that the likelihood of CHL adult males engaging in more costly counterattacks or attention getting alarm calls were better predicted by the level of investment in the group (genetic relatedness, duration of residency, social relationships), but not rank and mating rate. Long-duration resident adult males performed high and/or intermediate cost behaviors to protect vulnerable members of the group; their potential offspring, maternal siblings or cousins, and adult female social partners. Short-term residents or recent immigrant males exhibited two less energetically costly, more self-preserving behaviors, depending on their rank: (1) high-ranking short-tenure duration males, with high mating frequencies, performed flee and freeze responses; (2) low-ranking, low-mating-frequency males performed more alarm calls. Counterattacks and alarm calls were performed by adult males with relatively more experience with village dogs and were directed towards dogs with predatory histories significantly more often than dogs with non-predatory histories. Natural selection and kin selection have both contributed to the evolution of CHL anti-predator tactics.
... Many domestic animals of non-native taxa serve as human-subsidized predators and cause substantial wildlife mortality annually [9][10][11][12]. Domestic dogs (Canis lupus familiaris) in particular, including owned and feral, threaten a wide variety of species globally [13][14][15][16][17][18][19][20][21][22][23][24][25][26]. These canids have become a notable and ubiquitous conservation challenge, ranking just below cats and rats as the third most-damaging invasive predator [8]. ...
Article
Full-text available
Human-introduced predators, primarily the domestic dog (Canis lupus familiaris), and human-modified landscapes conjointly threaten wildlife across Costa Rica. For arboreal species, including the two-fingered sloth (Choloepus hoffmani), the impact of domestic dogs is amplified in areas of habitat fragmentation. In efforts to navigate discontinuous canopies associated with urban development and human encroachment, C. hoffmani is forced to utilize terrestrial locomotion. This unnatural behavior leaves sloths increasingly vulnerable to predation by domestic dogs, which occupy altered landscapes in high densities. In this report, we detail the ante and postmortem findings associated with C. hoffmani following an extensive attack by three large-breed dogs. The patient sustained severe and fatal polytraumatic injuries targeting the abdominothoracic region. Gross lesions were not readily evident, obscured by unique anatomical characteristics of the species. This report aims to highlight the threat imposed by dogs to sloths and the severity of injuries, with considerations for clinical management in light of C. hoffmani morphology. We review the scope of domestic dog–wildlife conflict in Costa Rica, and propose collaborative mitigation strategies including habitat preservation, domestic dog population control, installation of wildlife corridors, policy initiatives, and dog owner education and public outreach.
... Primate infants and juveniles are generally not vigilant towards predators, likely leaving them susceptible to fatal interactions with dogs (e.g. Chetry et al., 2005;Riley et al., 2015;Waters et al., 2017). Such a lack of vigilance in response to dogs may substantially affect Central American howler infant and juvenile survival in Mexico (Bonilla-Sanchez et al., 2010). ...
Chapter
People are assisted by dogs in many activities which may bring them into contact with primates, often leading to negative interactions and outcomes for one or other species. People’s perceptions and behaviour towards dogs vary and are influenced by cultural and other factors. We present incidents of dog-primate harassment and predation found during a literature review. We found that dog-primate contact can result in negative interactions and outcomes for one or other species, and we discuss how dogs influence primate populations globally via indirect interactions such as the transmission of disease. Observing direct interactions between dogs and primates is exceedingly rare due to the difficulty associated with observing these encounters, and we introduce single-species occupancy modelling as a method to conduct non-invasive research to investigate the effects of dogs on primates. We explore methods for mitigating dog-primate interactions. Finding effective ways to manage dog populations in collaboration with their owners and/or changing those owners’ behaviour in relation to their dogs is emerging as yet another challenge for primate conservation practitioners.
... Primate infants and juveniles are generally not vigilant towards predators, likely leaving them susceptible to fatal interactions with dogs (e.g. Chetry et al., 2005;Riley et al., 2015;Waters et al., 2017). Such a lack of vigilance in response to dogs may substantially affect Central American howler infant and juvenile survival in Mexico (Bonilla-Sanchez et al., 2010). ...
Chapter
Across the globe and across time, primates have been used in live performances and depicted through imagery to entertain audiences and tell stories. Technological advances have led to a proliferation of ways in which we consume media and with that, audiences for primates in entertainment have flourished. Here we review some of the ways primates are used as entertainers and examine representations of primates in contemporary media. We provide an overview of the role of primates in the entertainment industry and discuss issues of animal welfare and conservation. An understanding of the history primates in media and entertainment is critical to regulating these practices and ensuring the health and welfare of both humans and animals.
... Primate infants and juveniles are generally not vigilant towards predators, likely leaving them susceptible to fatal interactions with dogs (e.g. Chetry et al., 2005;Riley et al., 2015;Waters et al., 2017). Such a lack of vigilance in response to dogs may substantially affect Central American howler infant and juvenile survival in Mexico (Bonilla-Sanchez et al., 2010). ...
Chapter
Pet primates are those kept typically for companionship, enjoyment, and status, although their uses as pets may extend beyond these parameters. The trade in pet primates is historically rooted, with many primates playing important roles in human cultures and religions. Thus, it is not surprising that current sociocultural trends reveal an ongoing fascination with primates and their purchase as status pets. Recent reports from various regions are presented in this chapter, demonstrating the need for drastic interventions to avoid further losses. Capture of animals for the pet trade may be intentional or opportunistic and is often exacerbated by internet trade and social media. This situation is complicated by the difficulty of obtaining accurate numbers of primates bought and sold illegally. The health and welfare of primates captured or kept as pets is another area of great concern. Long-term solutions will require attention from governmental, professional, and public actors on local and international levels.
Article
Full-text available
Simple Summary: Each of the five primate species inhabiting Argentina faces various threats in terms of conservation that hamper their ability to coexist with human populations. These threats have in common that they are the result of human actions and changes in the landscape, and they all have consequences that may result in human-primate conflict. Furthermore, these changes surely present remarkable challenges for slow-life primates, as they happen too quickly for genetic adaptations to evolve within a timeframe compatible with population viability. Hence, it becomes imperative to delve into the consequences of the different threats that the different species face and the conflicts that are derived from them. We present a detailed compilation of what we consider to be the most relevant and current conflicts between humans and non-human primates in Argentina and describe ongoing national and regional educational, research, and conservation approaches to mitigate those effects. Abstract: There are five different primate species inhabiting widely distinct ecoregions in Ar-gentina. Each of them faces various threats in terms of conservation and conflicts that hamper their ability to coexist with human populations. We present here some of the drivers known to be the causes of conflicts between humans and primates in the southernmost area of distribution of Latin American primates. We focus our synthesis on two of the biggest sources of conflict: the effects of different anthropogenic disturbances, and human misconceptions concerning the role of primates in the ecosystem. In each section, we briefly characterize the conflicts worldwide and then provide specific cases and examples from Argentina. In the last part of the manuscript, we further describe some ongoing national and regional educational, research, and conservation approaches to mitigate those effects.
Preprint
Full-text available
For nonhuman primates living in anthropogenic areas, predation by larger predators is relatively rare. However, smaller predators such as free-ranging as well as domesticated dogs can shape the socioecology of urban nonhuman primates, directly by attacking and predating upon them, or indirectly by modifying their activity patterns. Here, we describe 3 (2 potentially lethal) cases of dog attacks on adult rhesus macaques inhabiting an anthropogenic landscape in Northern India, and the circumstances surrounding these incidents. We discuss the importance of considering the presence of dogs while studying nonhuman primate populations across the anthropogenic gradient and its implications for understanding how human presence can directly and indirectly affect predator-prey relationship in these areas, as well as its potential role in modifying group social dynamics as well as in transmission of zoonotic agents.
Chapter
Long-tailed macaques (Macaca fascicularis umbrosa Miller, 1902) are the only non-human primate community on the Andaman and Nicobar Islands. They are currently considered to be at low risk of extinction; however, habitat fragmentation or loss, inbreeding or outbreeding depression and hybridization pose threats. At the moment, no management measures have been implemented, and current information on their situation and status is desperately needed. From December 2008 to December 2021, research studies were conducted in 26 localities where positive responses to questionnaires on long-tailed macaques were obtained, and long-tailed macaques were found in 26 locations ranging from the northern and south-western to the southernmost part of the Great Nicobar Biosphere Reserve. Long-tailed macaques’ current distribution is similar to that reported 30 years ago; however, their habitats have shifted from natural forests to temples or recreation parks. Furthermore, the troops are frequently overcrowded. Despite the fact that many troops of long-tailed macaques in Great Nicobar Biosphere Reserve have inflated population densities, some local troops have morphological, genetic, and behavioural uniqueness that may be important to conserve. As a result, management plans and conservation strategies for the Great Nicobar Biosphere Reserve’s long-tailed macaque population is needs to be developed.KeywordsLong-tailed macaqueNicobarBiosphere reserveDistribution
Chapter
Full-text available
Long-tailed macaques are an edge species, preferring to live along the forest borders of many habitat types (Gumert, Chapter 1). The result of this preference is that long-tailed macaques are adaptable generalists that are frequently found along the edges of human settlements across Southeast Asia. Another consequence is that long-tailed macaques can adjust quickly to living with other species, and thus have commonly expanded beyond the edge to overlap with humans in numerous contexts (see Part II). Due to the close association with humans, macaque populations can be powerfully impacted by human activity. In some cases they have been carried and introduced to areas beyond their normal range (see Part III). The overlap of macaques and humans, and the consequences of this overlap, needs to be better understood. While the basis of our relationship with long-tailed macaques is becoming apparent, much more research will be needed to fully understand their population and the causes and consequences of our interface with them. This chapter is an attempt to focus future research in a few important areas that will be necessary for better understanding the population, ecology, and synanthropic nature of long-tailed macaques. This chapter focuses on three subject areas that warrant special consideration for future scientifi c research on M. fascicularis : population-level research, the issue of ethnophoresy and introduced populations, and the causes and consequences of human-macaque overlap. Directions for population-level research Long-tailed macaques perhaps have the greatest amount of intraspecifi c variation of any primate species (Fooden, 2006). The large variation is not yet well
Article
Full-text available
We report two cases of predation and predation-related events on long-tailed macaques and proboscis monkeys sympatrically living in the lower Kinabatangan, Sabah, Malaysia. An adult male long-tailed macaque was preyed by an estuarine crocodile when he feed fruits on the low branches above river. We found a solitary male proboscis monkey who has large wounds on the cheek and left thigh. It would appear that the male was injured by a large predator such as Sunda clouded leopard. These cases indicate the strong predation pressure on primates who habit in riverine forest as it has been previously indicated. For better understanding of primates’ anti-predation strategy, more accumulation of information on predation events is necessary.
Article
Full-text available
Animal traditions can affect survival by improving how individuals use their environment. They are inherited through social learning and are restricted to small subpopulations. As a result, traditions are rare and their preservation needs to be considered in biodiversity conservation. We studied Burmese long-tailed macaques Macaca fascicularis aurea living on Piak Nam Yai Island in Laem Son National Park, Thailand, which maintain a rare stone tool-using tradition for processing hard-shelled invertebrate prey along the island's shores. We found the population had 192 individuals in nine groups and most individuals used stone tools. This population is under pressure from the local human community through the development of farms and release of domestic dogs Canis familiaris onto the island. The level of anthropogenic impact varied in each macaque groups' range and juvenile–infant composition varied with impact. The proportion of young was smaller in groups overlapping farms and was negatively correlated with the amount of dog activity in their range. We also found that coastal use by macaques was negatively related to living near plantations and that the dogs displaced macaques from the shores in 93% of their encounters. We conclude that human impact is negatively affecting Piak Nam Yai's macaques and are concerned this could disrupt the persistence of their stone-use tradition. we discuss the impact and the potential consequences, and we recommend better protection of coastal areas within Laem Son National Park.
Article
Full-text available
Our current knowledge on the origin and early evolution of large predators is summarized by Simon Conway Morris (1999, 153–154) as follows: ...for many years it was claimed that Cambrian marine communities were almost entirely free of predators… the seas were [thought to be] full of suspension-feeders gently swaying in the sea water and deposit feeders calmly digging their way through the sediment. This view is now seen to be far too idyllic, but the story of the rise of predators is still quite tentative. It does appear, however, that in contrast to Cambrian communities those of the Ediacaran were largely free of predators.
Article
The longtail macaque is systematically reviewed, based on examination of 2049 museum specimens, study of relevant literature, and observation of natural populations. M. fascicularis inhabits tropical Southeast Asia. This review of M. fascicularis includes analyses of geographic variation in pelage characters, external measurements and proportions, cranial characters, molecular and genetic characters, and disease susceptibility. Evidence concerning natural history, reproduction, and paleontology also is investigated. Ten subspecies of M. fascicularis are recognized, and a key to these subspecies is provided. -from Author
Chapter
Long-tailed macaques (Macaca fascicularis) have a wide geographical distribution and extensively overlap with human societies across southeast Asia, regularly utilizing the edges of secondary forest and inhabiting numerous anthropogenic environments, including temple grounds, cities and farmlands. Yet despite their apparent ubiquity across the region, there are striking gaps in our understanding of long-tailed macaque population ecology. This timely volume, a key resource for primatologists, anthropologists and conservationists, underlines the urgent need for comprehensive population studies on common macaques. Providing the first detailed look at research on this underexplored species, it unveils what is currently known about the population of M. fascicularis, explores the contexts and consequences of human-macaque sympatry and discusses the innovative programs being initiated to resolve human-macaque conflict across Asia. Spread throughout the book are boxed case studies that supplement the chapters and give a valuable insight into specific field studies on wild M. fascicularis populations.
Article
Records of responses of free-ranging primates to domestic dogs are summarized and evaluated. Although dogs are often considered as potential predators of primates, members of only 7 species of monkey are reported as actually having been killed by dogs. Most injurious or fatal attacks by dogs on primates occur near human settlements in Asia. It is suggested that neither domestic dogs nor wild canids are important predators of primates. Since dogs are often used by hunters, primates probably have a conditioned aversion to them, which is expressed through alarm responses, fleeing, and sometimes aggression.