Journal of Threatened Taxa |
www.threatenedtaxa.org | 26 April 2021 | 13(5): 18141–18147
ISSN 0974-7907 (Online) | ISSN 0974-7893
(Print)
https://doi.org/10.11609/jott.6582.13.5.18141-18147
#6582 | Received 18 August 2020 | Final
received 24 March 2021 | Finally accepted 27 March 2021
Assessment of crop and property damage caused by Semnopithecus
vetulus nestor
(Bennett, 1833) (Mammalia: Primates: Cercopithecidae)
in Gampaha District, Sri Lanka
Sunil Wijethilaka 1, Lakshani
S. Weerasekara 2, Saumya
Bandara 3 & Kithsiri
B. Ranawana 4
1 Henegama Central National
School, Henegama, Gampaha, Sri Lanka.
2 Department of
Zoology, Faculty of Science, Eastern University, Vantharamoolai,
Sri Lanka.
2 Postgraduate
Institute of Science, University of Peradeniya, Peradeniya, Sri Lanka.
3 Science Education
Unit, Faculty of Science, University of Peradeniya, Peradeniya, Sri Lanka.
4 Department of
Zoology, Faculty of Science, University of Peradeniya, Peradeniya, Sri Lanka.
1 sunilwijethilaka@gmail.com,
2 lakshaniw@esn.ac.lk (corresponding author), 3 saumyasnp@gmail.com,
4 kithsiri.r@gmail.com
Editor: Michael A. Huffman,
Primate Research Institute, Kyoto University, Japan. Date of publication: 26 April
2021 (online & print)
Citation: Wijethilaka,
S., L.S. Weerasekara, S. Bandara
& K.B. Ranawana (2021). Assessment of crop
and property damage caused by Semnopithecus
vetulus nestor
(Bennett, 1833) (Mammalia: Primates: Cercopithecidae)
in Gampaha District, Sri Lanka. Journal of Threatened Taxa 13(5): 18141–18147. https://doi.org/10.11609/jott.6582.13.5.18141-18147
Copyright: © Wijethilaka et al. 2021. Creative Commons
Attribution 4.0 International License. JoTT allows unrestricted use, reproduction, and
distribution of this article in any medium by providing adequate credit to the
author(s) and the source of publication.
Funding: No funding was
received for conducting this study.
Competing interests: The authors
declare no competing interests.
Author details: Mr. Sunil Wijethilaka is a High School
Science teacher who is an enthusiast about nature and especially interaction
between langurs and humans. Ms. Lakshani Weerasekara, BSc,
is a young graduate major in Zoology and her research interests extend to
ecology and wildlife conservation, animal behavior and primatology. Mr. Saumya Bandara, BSc, is a lecturer in the Science Education
Unit, Faculty of Science, University of Peradeniya. His research interests are
the ecology of land snails and science education of indigenous people. Prof. Kithsiri Ranawana, PhD, is a renowned ecologist in Sri Lanka
and an active naturalist. His research interests include ecology and
conservation.
Author contribution: Sunil Wijethilaka did the field work, Lakshani
Weerasekara & Kithsiri Ranawana prepared the manuscript, and Saumya
Bandara did the statistical analysis.
Acknowledgements: We convey our
gratitude to all the residents in the 12 villages, Grama
Niladhari, Agricultural officers and other government
officers of the study area for providing support to compile this project. We thank Professor M.A Huffman, all other
anonymous reviewers and editors for their constructive comments and suggestions
on the manuscript.
Abstract: In earlier times,
human-monkey interactions were not a severe problem in Sri Lanka, but has
recently intensified as a result of habitat fragmentation and
urbanization. Due to these changes, Semnopithecus vetulus
nestor has been listed among the 25 most Endangered
primates. The objective of our study was
to evaluate the intensity of human-S.v.
nestor negative interaction by identifying the
crop and property damages in villages bordering Danawkanda
Forest (7.001N & 80.049E), Gampaha, Sri Lanka. We collected data using structured
questionnaires interviewing households (N= 80) bordering the Danawkanda Forest from August 2014 to January 2015. Households were most affected by damage to
fruits, leaves, and buds of commercially important trees (93%), followed by
damage to roof tiles (76%), and frightful confrontations with the monkeys
(43%). Average monthly loss per
household from crop and property damage was estimated at between (Sri Lankan
Rupees) LKR 2,700 and LKR 1,500.
Lighting firecrackers was the most common method used by the residents
(99%) to deter monkeys, where as electrified
barriers were rarely used (4%).
Households in close proximity to Danawkanda
Forest experienced a considerable loss to their monthly income due to crop and
property damage, compared to households further away. As an alternative, residents now grow
ornamental plants and short trees, eliminating the structures that attract and
facilitate damage by S.v. nestor.
Awareness and active participation of residents, authorized government,
and non-governmental organizations are needed to manage unplanned construction
and agriculture plot extensions into the forest. These two factors trigger the human-wildlife
negative interactions in general and are not limited just to monkeys.
Keywords: Danawkanda Forest, deterrent
methods, human-primate conflict, human-primate negative interactions, Western
Purple-faced Leaf Monkey.
INTRODUCTION
Crop
raiding by animals is a concern for small-scale subsistence farmers (Garriga 2014) in countries around the world like Sri Lanka,
where nearly 28.5% of the population depends on agriculture (CBSL 2014). Different animal species cause different
problems for farmers when they raid crops (Hill 2005). Not only parasitic invertebrates but also
vertebrates like birds (Bruggers et al. 1998; Maurice
et al. 2019), rodents (Lathiya et al. 2003; Sarwar
2015), Mouse Deer (Linkie et al. 2007), porcupine (Linkie et al. 2007), Wild Boar (Shafi
& Khokhar 1986; Gobosho
et al. 2015), Elephants (Sukumar 1990; Barnes 1996; Hill 1998; Chiyo et al.
2012) and non-human primates (Boulton et al. 1996; Pirta
et al. 1997; Hill 2000; Dittus et al. 2019) are
considered as crop raiding pests responsible for human-wildlife negative
interactions. Non-human primates are
often considered to be the most destructive crop raiders in many parts of the
world (Naughton-Treves et al. 1998; Hill 2000; McLennan 2008; Hill &
Wallace 2012; Hockings et al. 2012; Cabral et al. 2018). Members of the genera Macaca,
Papio, and Cercopithecus are amongst
the most frequently cited non-human primate pest species (Hill 2005). The presence of an organized social hierarchy,
co-operative behavior, communication skills, combined
with intelligence, dietary and behavioral
flexibility, manual dexterity, and extreme agility make these primate species
particularly difficult for farmers to prevent from damaging crops (Hill 2005).
The
human-monkey interaction in Sri Lanka was not a severe problem in the past, but
has intensified in recent decades due to agricultural, irrigational, &
industrial projects, increased urban expansion, and fragmentation of natural
forested areas due to an increase in the human population (Wickramagamage
1998; Rudran 2007; Marasinghe
& Nathaniel 2020). Forest
fragmentation in the wet and dry zones is a primary cause of rapid and
widespread invasion of primates into farms and agricultural lands in search of
alternative food resources (Nahallage & Huffman
2008). As a result, conflicts have
intensified. These human-wildlife conflicts
affect the survival of many endangered commensal species (Garriga
2014) like Semnopithecus vetulus nestor, as well as
undermine the local human population’s food security and tolerance for
wildlife.
S.v.
nestor (Bennett 1833) has been listed
among the 25 most endangered primates of the world (Schwitzer
et al. 2017) due to encroachment into their habitat by unplanned
urbanization. Urbanization severely
threatens the long-term survival of this endemic species (Molur
et al. 2003; Rudran et al. 2009; Mittermeier et al.
2012). While studies on its behaviour and ecology have been comprehensively
addressed, reports on human - S.v. nestor conflicts are scarce (Molur
et al. 2003; Dela 2004, 2007, 2012; Rudran 2007; Mittermeier et al. 2009, 2012; Rudran et al. 2013).
Thus, the objective of our study was to evaluate the intensity of
human-monkey conflict by identifying the crop and property damages caused by S.v. nestor,
and to quantify the loss incurred to the households caused by them in villages
bordering Danawkanda Forest, Gampaha District in the
Western Province of Sri Lanka.
METHODS
Study
site
Danawkanda
Forest (7.001N & 80.049E) is a secondary wet zone forest encompassing an
area of 360ha, located in Gampaha District, Sri Lanka. The forest patch is surrounded by many
adjacent villages. Twelve villages
bordering Danawkanda Forest were randomly assessed
during the study in Mahara Divisional Secretariat
(Image 1). Danawkanda
Hill is considered a historical land mark in the region, and contains a
Buddhist monastery where people interact with the forest. The main habitat type in the study area was
village home gardens dominated by the tall fruit tree species Artocarpus heterophyllus
(Jak) (86%), Mangifera
indica (Mango) (86%), Cocos nucifera (Coconut)
(71%), and Areca catechu (Arecanut)
(34%). The dominant medium-size fruit
tree species were Nephelium lappaceum (Rambutan) (59%), Carica
papaya (Papaw) (48%), Musa paradisiaca (Banana)
(34%), and Psidium guajava (Guava) (20%).
Study
subject
Semnopithecus
vetulus is the only
endemic colobine monkey species in Sri Lanka representing four subspecies;
namely S.v. philbricki
(Northern Purple-faced Leaf Monkey), S.v.
vetulus (Southern Purple-faced Leaf
Monkey), S.v. monticola
(Bear Monkey), and S.v. nestor (Western Purple-faced Leaf Monkey) (Rudran et al. 2020).
Of which S.v. nestor is the smallest subspecies in body size (Dela 2007) (Image 2).
Its range extends across the western lowlands of Sri Lanka, in an area
of high human population density, very low forest cover (Dela
2012), extensive human settlements, and agricultural activity (Dela 2007).
Survey
A
pilot survey was carried out in July 2014 to identify the families that
experience S.v. nestor
raids. Structured questionnaires (N= 80)
were then carried out to collect data by randomly interviewing families in 12
villages bordering Danawkanda Forest from August 2014
to January 2015. The head of each
household was interviewed in the relevant native language, Sinhalese or Tamil,
to avoid omission of vital information.
The questionnaire was composed of both closed- and open-ended questions
and binary (yes/no) questions.
Data
analysis
The
data collected from interviews were presented as percentages of respondents
given for each response (Marchal & Hill
2009). Crop and property damages,
financial loss to the household, and expenditures for deterrent methods were
calculated. Pearson’s correlation test
was performed to analyze the relationship between the
money spent on firecrackers and the distance to the forest. Minitab (Version 14.0) Statistical Software
was used and the level of statistical significance was set at p≤ 0.05.
RESULTS
Economic
structure of the households in villages bordering Danawkanda
Forest
Residents
in the study area led a typical Sri Lankan lifestyle, of which 61% were
employed (21% in the government, and 40% private sector) and 39% were
unemployed, being involved in horticulture and a very few were daily-based
laborers. Despite their employabiltiy, the majority were involved in friut plant (N= 78), crop plant (N= 55), and ornamental
plant cultivation (N= 12). Monthly
income was recorded as follows: 64% of residents earned less than LKR 25,000,
19% of residents earned LKR 35,000–50,000, and 3% of residents earned more than
LKR 50,000.
Crop
and property damage caused by S.v. nestor
Damages
were categorized as crop damages, property damages, and others (Table 1). The highest number of households was affected
by damages done to fruits, leaves, & buds (93%) of commercial value,
breaking of roof tiles (76%), and frightful encounters (43%). The most preferred fruit species of the
monkeys were M. paradisiaca and C. papaya
(99%) (Table 2). The average losses
per household by crop and property damages ranged between LKR 2,700 and LKR
1,500. This loss to the household caused
by crop and property damage was higher in the dry season than the wet season
(Fig. 1).
In
addition to losses to the household caused by crop and property damages,
residents spend money to buy firecrackers for chasing monkeys away. There was a strong negative correlation
between the distance to the village and the average amount of money spent on firecrackers
(r2= -0.78 p= 0.0410).
Deterrent
methods for S.v. nestor
raids in villages bordering Danawkanda Forest
Deterrent
methods for chasing away S.v. nestor were categorized as currently used methods,
and proposed alternative methods (Table 3).
Lighting firecrackers were the most common method used by the residents
to chase away S.v. nestor
(99%). Electrified barriers
were rarely used (4%). Now most of the
residents prefer to grow ornamental plants and short trees to develop an
aesthetic appearance around the home and to eliminate the structures that
attract and facilitate S.v. nestor approaching the home and property as proposed
alternative methods.
DISCUSSION
Crop
raiding by wildlife is not a new phenomenon.
It has been occurring since humans first settled down and started
practicing agriculture (Sillero-Zubiri & Switzer
2001); however, the intensity of this problem is particularly problematic in
areas where humans are encroaching onto once undisturbed wildlife habitats (Rudran 2007; Nahallage &
Huffman 2008). It is challenging to
conduct a comprehensive assessment of the damage caused by wildlife (Garriga 2014).
Farmers’ perceptions of loss are often greater than the actual loss, and
this becomes more accentuated if the plantations are in close proximity to a
protected wildlife area (Hill 2004). In
the present study, we found that residents near the Danawkanda
Forest are experiencing a considerable financial loss due to crop and property
damage by S.v. nestor
compared to their monthly income. Twelve
villages are located within a 4km radius of Danawkanda
Forest, of which 75% are located within a radius of 2km. Hence, S.v.
nestor can easily exploit the available
food resources of these villages via continuous arboreal pathways that connect
the villages to the forest (Rudran 2007). Villages that are located relatively close to
the forest largely experience a high frequency of crop and property damages
compared to more distant villages.
Similarly, previous studies have also shown that S.v.
nestor is involved in the exploitation of
human modified habitats, and that often results in crop damage and consumption
and other forms of property damage (Rudran 2007; Dela 2012).
Similarly, studies carried out in African countries like Uganda and in
some regions in India show that farms closer to forests do actually suffer
significantly more crop raiding than farms situated further away (Saj et al. 2001; Baranga et al.
2012; Karanth et al. 2013).
The
vegetation structure of home gardens was the key element in attracting S.v. nestor. They mostly preferred taller
fruit-trees that facilitated their arboreal movements, hence, home gardens with
more tall trees were raided more frequently.
Food sources like fruit plants were very common in home gardens in the
study sites. Dela (2012) stated that S.v. nestor
living in environments modified by humans and with abundant sources of
cultivated fruits had actively adopted a more frugivorous dietary strategy,
unlike that of any other colobine monkeys.
Though fruits vary widely in biochemistry and quality, they are in
general easily digested and contain energy-rich sugars and nonstructural
carbohydrates (Kay & Davies 1994; Waterman & Kool 1994). Human edible fruits from cultivars seem to
have these features (Dela 2007). Similar to Rudran
(2007) in the present study, S.v. nestor commonly preferred fruits such as banana and
papaw over other available fruits, and this might be due to their availability
throughout the year, unlike most seasonal fruits. Chimpanzees are also known to cause
significant damage to banana plantations (Naughton-Treves 1996). In the present study, the highest percentage
of damage is done to leaves, fruits and their buds (93%), because mature leaves
are generally high in fiber and protein, are more
nutritious, and have lower processing costs (Oates et al. 1980; Waterman &
Kool 1994). S.v.
nestor commonly preferred both raw and ripe
fruits (29%), and vegetable crops and their flowers (13%). On the other hand, roof tiles (76%) and roof
sheets (13%) were frequently damaged by removing and destroying them. On occasion, they jump down on the roofs from
tall trees as they move and chase one another, causing substantial damage to
the roof. Unrepaired damages can lead to
roof degradation.
Fear
of S.v. nestor
was common in the study area. Small
children are the most common victims.
Some monkeys were relatively more aggressive than others, with a
few reports of people being bitten.
Other primates like chimpanzees have even been known to kill children on
more than 10 occasions in the Kibale Forest of
western Uganda (Naughton-Treves pers. comm. 1996; Hill 2005) and baboons have
caused injury and death to humans (Hill 2000; Nchanji
2002). Other prevailing problems include
breaking fences, spoiling water in storage tanks and food, and the carrying off
of small household items.
More
than two-thirds of the residents interviewed face financial difficulties and
the majority find selling of horticulture as a good remedy. They cultivate fruits and vegetables in their
home gardens. Monkey foraging incursions
into their home gardens cause a direct economic impact to the household. Damage to crops and property was higher in
the dry season compared to the wet season.
The wet season triggers flushing and fruiting of food sources in the
forest, so the monkeys are able to get enough natural food at this time of year
within the Danawkanda Forest. But in the dry season, food sources are
scarce inside the forest. This might be
the reason for intensified foraging in the adjacent home gardens, resulting in
high crop and property damages at this time of the year. Conversely, many colobine species in other
parts of the world feed selectively on seasonal plant parts (Davies 1991;
Stanford 1991).
Most
of the deterrent methods used are not harmful to the monkeys, but
electrocution, shooting, poisoning, and hitting with stones are injurious. More traditional protection strategies used
against other species such as creating barriers (electric fences, living
fences, walls, and ditches) between wildlife and farming areas are ineffective
where primates are concerned (Garriga 2014). Lighting firecrackers was the most common
deterrent method used by the residents near the Danawkanda
Forest. As the distance from the forest
to the villages increases, the amount of money that had to be spent on
firecrackers to deter S.v. nestor decreased.
This is because the villages located more closely to the Danawkanda Forest are more frequently raided by S.v. nestor
than the villages further away.
Apart
from the currently used methods, we recommended seven alternative methods to
residents in the area (see Table 3). The
majority (99%) preferred to grow shorter trees instead of taller trees, because
they give an aesthetic appearance to the home garden, and grow more ornamental
plants instead of crop plants. This
will, however, reduce the opportunities for growing valuable timber species and
crop plants that can increase the monthly income of these residents.
Our
study can be regarded as a baseline survey, which provides an initiative to
address this rising problem in the area.
We propose that S.v. nestor causes crop and property damages in the
villages bordering Danawkanda Forest as a result of
their search for nutritious food sources in home gardens at times of food
scarcity in the forest. Residents who
are living in close proximity to the forest, having low income, experienced a
considerable economic loss to the household, leading to conflicts between
humans and S.v. nestor. Perhaps compensatory mechanisms can help
alleviate the financial losses to households.
Awareness can play a vital role in encouraging villages to tolerate and
mitigate crop and property damages caused by S.v.
nestor.
More efforts are needed to educate people on the importance of
biodiversity and effective ways of mitigating the wildlife problem without
engaging in constant conflict with them.
Importantly, active participation of authorized government and
non-governmental organizations needs to be involved to manage unplanned
construction and agriculture extensions into the forest, which triggers
negativity towards not only monkeys, but many other wildlife species as well.
Table 1. Damage
caused by Semnopithecus vetulus
nestor in villages bordering the Danawkanda Forest, Sri Lanka.
|
Damage type |
Number of families
affected (%) |
|
Crop damage |
|
|
Damage fruits,
leaves and buds (leaf and flower buds) |
93 |
|
Consume ripe and
raw fruits |
29 |
|
Consume crop and
flowers of vegetable plants |
13 |
|
Uprooting plants |
13 |
|
Property damage |
|
|
Break the roof
tiles |
76 |
|
frightful
encounters |
|
|
Scaring adults and
children |
43 |
|
Biting adults and
children |
31 |
|
Noise annoyance |
41 |
Table 2. Fruit
species ingested by Semnopithecus vetulus nestor in
home gardens bordering the Danawkanda Forest, Sri
Lanka.
|
Family |
Species |
Common name |
Reported frequency
of use (%) |
|
Musaceae |
Musa paradisiaca |
Banana |
99 |
|
Caricaceae |
Carica papaya |
Papaw |
99 |
|
Sapindales |
Nephelium lappaceum |
Rambutan |
44 |
|
Anacardiaceae |
Mangifera indica |
Mango |
31 |
|
Arecaceae |
Cocos nucifera |
Coconut |
20 |
|
Euphorbiaceae |
Manihot esculenta |
Manioc |
08 |
|
Dioscoreaceae |
|
Yams |
08 |
|
Arecaceae |
Cocos nucifera “king” |
King coconut |
05 |
|
Malvaceae |
Durio kutejensis |
Durian |
04 |
|
Dipterocarpaceae |
Dipterocarpus zeylanicus |
Kiripalu |
02 |
Table
3. Deterrent methods for raiding by Semnopithecus
vetulus nestor into
home gardens bordering the Danawkanda Forest, Sri
Lanka.
|
Deterrent method |
Households (%)
employing these techniques |
|
Currently practiced
methods |
|
|
Lighting fire
crackers |
99 |
|
Throwing and/or
thrashing stones |
41 |
|
Shooting by pellet
guns and catapults |
18 |
|
Creating
noises/shouting |
26 |
|
Electricity
fence/wires |
04 |
|
Proposed
alternative methods |
|
|
Growing decorative
plants |
99 |
|
Addition of short
trees |
99 |
|
Creating an esthetic landscape |
99 |
|
Growing ornamental
plants instead of crop plants |
98 |
|
Elimination of
structures that attract and facilitate monkeys |
92 |
|
Reducing the food
sources |
84 |
|
Removal of tall
trees |
78 |
For figure
& images - - click here
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