Journal of Threatened Taxa | www.threatenedtaxa.org | 26 January 2022 |
14(1): 20478–20487
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.7560.14.1.20478-20487
#7560 | Received 08
July 2021 | Final received 21 October 2021 | Finally accepted 06 December 2021
Utilization of home garden crops
by primates and current status of human-primate interface at Galigamuwa Divisional Secretariat Division in Kegalle District, Sri Lanka
Charmalie Anuradhie
Dona Nahallage 1, Dahanakge
Ayesha Madushani Dasanayake
2 , Dilan Thisaru Hewamanna 3 & Dissanayakalage Tharaka Harshani Ananda 4
1 Centre for Multidisciplinary
Research, 1,2,3,4 Department of Anthropology,
Faculty of Humanities and Social
Sciences, University of Sri Jayewardenepura, Gangodawila,
Nugegoda, 10250, Sri Lanka.
1 chamalie@sjp.ac.lk (corresponding
author), 2 madushaniayesha150@gmail.com, 3 dilanthisaru@gmail.com,
4 tharakaananda@sjp.ac.lk
Editor: Honnavalli N. Kumara,
Salim Ali Centre for Ornithology and Natural History, Coimbatore, India. Date
of publication: 26 January 2022 (online & print)
Citation: Nahallage,
C.A.D., D.A.M. Dasanayake, D.T. Hewamanna
& D.T.H. Ananda (2022). Utilization of home garden crops
by primates and current status of human-primate interface at Galigamuwa Divisional Secretariat Division in Kegalle District, Sri Lanka. Journal of Threatened Taxa 14(1): 20478–20487. https://doi.org/10.11609/jott.7560.14.1.20478-20487
Copyright: © Nahallage
et al. 2022. 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: This research was funded
under the mini research grants of the Multidisciplinary
Research Centre of the Faculty
of Humanities
and Social
Sciences, University of Sri Jayewardenepura.
Competing interests: The authors
declare no competing interests.
Author details: Charmalie Anuradhie Dona Nahallage holds a Bachelor of Science in Zoology, Master of Science and Doctor of
Science in Primatology from Primate Research Institute, Kyoto University,
Japan. She is currently the head and conducts research on primate phylogeography and human-primate interactions in Sri
Lanka. Dahanakge Ayesha Madushani Dasanayake
holds a Bachelor of Arts honours degree in Anthropology. She conducted a
research on human-primate interactions for her undergraduate dissertation and
currently awaiting to get registered for a Master of Philosophy degree to
pursue her research interest on human-primate interactions. Dilan Thisaru Hewamanna holds a Bachelor of Arts honours degree in
Anthropology. He conducted a research on human-primate interactions for his
undergraduate dissertation and currently awaiting to get registered for a MPhil
degree to pursue his research interest on the same. Dissanayakalage
Tharaka Harshani Ananda
holds a Bachelor of Arts honours degree in Anthropology and a PhD in
Anthropology from the University of Sri Jayewardenepura. She is currently a
lecturer and conducts research on human variation and primatology.
Author contributions: CADN wrote the manuscript and
DTHA, DAMD, and KKDTH contributed to data entering, analysis, and reviewing of
the manuscript. DAMD, KKDH, and CADN collected field data.
Acknowledgements: The authors thank the dean of the
Faculty of Humanities and Social Sciences, University of Sri Jayewardenepura
and the director of the Multidisciplinary Research Center
for their support. This research was funded under the mini research grants of
the Multidisciplinary Research Centre of the Faculty of Humanities and Social
Sciences. Also, we are grateful to the
reviewers for the constructive suggestions and recommendations. The manuscript
benefitted greatly from the inputs of the reviewers. We also thank Prof. M.G. Lalith Ananda for reading through the manuscript
and correcting the language errors.
Abstract: Many humans coexist with
non-human primates (NHP), and as human populations have increased so have the
pressures on natural habitats. For example, deforestation results in habitat
loss and food scarcity for NHPs. In response, NHPs sometimes enter human
habitats in search of food, which can result in negative interactions between
humans and NHPs. This study focused on human-NHP interactions in three Grama Niladhari divisions in Kegalle District, Sri Lanka. We used
interviewer-administered structured questionnaires to collect data from 500
randomly selected informants. The majority stated that they could not obtain
sufficient harvests from home gardens for their own consumption owing to crop
damage and losses caused largely by NHPs and other wild animals. This has led
many people to abandon home gardening. Toque Macaques caused the most damage to
crops, followed by Wild Boars, porcupines, and Purple-faced Leaf Langurs.
Damage was caused to coconuts, vegetables, bananas, and yams. NHPs also caused
property damage, with Toque Macaques causing more damage than langurs. People
commonly used firecrackers, catapults and air rifles, and wore wooden or
plastic face masks, in attempts to control crop damage by NHPs, with little
success. People are of the opinion that the NHPs should be relocated to other
forested areas or sterilized to control their numbers. In conclusion, to
address the issues pertaining to human-primate interactions in terms of
conflict due to crop utilization of primates, an integrated management plan
should be developed in cooperation with the relevant stakeholders.
Keywords: Crop raiding, deforestation and
habitat loss, economic loss, forest edge home gardens, human-primate conflict,
integrated management plan, Macaca sinica, Semnopithecus
vetulus.
Abbreviations: DSD—Divisional Secretariat
Division | GN divisions—Grama Niladhari
divisions | NHP—Non-human primate.
Introduction
Humans, macaques, and langurs are
members of the sub-order Anthropoidea in the Order
Primates. The three species share many physiological, anatomical, and behavioral characteristics and thus have similar
requirements to sustain themselves. As a result, when they share the same
environment a variety of interactions between them become inevitable. Sometimes
these interactions have negative impacts on species when they share similar
food resources (Houle 1997; Peiman & Robinson
2010). The intensity of the interactions increases with the similarity of
shared resources, creating competition within or between species, which at
times can be detrimental to one or both.
Non-human primates and humans
maintain both positive and negative interactions. The positive interactions
include deploying primates for economically beneficial activities such as
harvesting coconuts, as can be seen in Thailand and also as performers to
entertain humans (Nahallage & Huffman 2013; Nahallage 2019). In both instances, humans gain economic
benefit by employing primates in various activities, which in turn creates a
positive attitude towards them. Most crucial for the survival of the primates
and their conservation is mitigating adverse interactions that create negative
attitudes toward primates, primarily in the form of human and non-human primate
competitions over common resources.
One of the main reasons for
escalating human-primate negative interactions in Sri Lanka is the loss of
natural primate habitat due to various development projects (Nahallage et al. 2008; Cabral et al. 2018; Dittus et al. 2019). Primates become isolated in small
forest patches because of the fragmentation of forests they inhabit, which
leads to an increase in competition for food and space. When resources become
depleted in the natural habitat, primates frequent villages in search of food,
which intensifies human-primate interactions (Dela
2007; Rudran 2007; Nahallage
et al. 2008; Dittus 2012; Rudran
& Kotagama 2016, Dittus
et al. 2019; Nahallage 2019). Other reasons monkeys
are attracted to nearby settlements include improper garbage disposal, feeding
by humans, cultivation of large-scale cash crops, and scarcity of food &
water in the natural habitats during the dry season (Dittus
et al. 2019).
In Sri Lanka, the three diurnal
primate species are mainly involved in human-primate interactions: Toque Macaquea Macaca sinica, Purple–faced Leaf Langurs Semnopithecus
vetulus and Gray
Langurs Semnopithecus priam
(Nahallage & Huffman 2013; Dittus
et al. 2019). No conflicts have been reported with two resident nocturnal Loris
spp., which have little interaction with humans. Macaques are sociable animals
that interact frequently with humans and prefer to stay close to human
settlements, while langurs prefer more natural habitats and foods (Nahallage & Huffman 2013; Dittus
et al. 2019; Nahallage 2019). Purple-faced Leaf
Langurs are strictly arboreal folivores and have the least interaction with
humans in many places. This relationship, however, varies in different parts of
the country (Rudran 1973, 2007; Dela
2007; Dittus 2012; Dittus
et al. 2019; Nahallage 2019), with Purple-faced Leaf
Langurs in the Western Province considered the most prominent species living
close to humans causing crop and property damage. Food selection by Gray Langurs depends on their habitat; in natural
environments they depend mainly on plant material, while those in urban
environments and temple areas tend to consume food given to them by pilgrims,
such as leftover offerings (Nahallage et al. 2008; Nahallage & Huffman 2013; Dittus
et al. 2019). During periods of food scarcity, both Gray
Langurs and Toque Macaques obtain food forcibly from people or directly from
houses or shops, leading to intense human-primate negative interactions.
Human-primate interactions is not
a recent occurrence in the country. Robert Knox, an English traveler
who was imprisoned on the island by the Kandyan King but allowed to live in
various places freely for about 20 years, described how macaques invaded corn
fields and home gardens despite their being heavily guarded (Knox 1681). There
were even folk poems written regarding the crop raiding of primates (Ananda
2000). At present, crop raiding occurs in all 25 districts of the country. Crop
raiding by primates generally depends on the types of crops grown, seasonality,
distance to the village from the forest, availability of natural foods, and the
methods of crop guarding (Hill 2000; Marchal &
Hill 2009; Fungo 2011). In Sri Lanka, macaques
inflict more damage to crops than langurs, but all are considered pests to
varying degrees in the provinces where they are found (Nahallage
at al. 2008; Nahallage & Huffman 2013; Prasad et
al. 2016; Nahallage 2019; Dittus
et al. 2019). In places where all three diurnal primates exist, Toque Macaques
damage crops the most, followed by Gray Langurs (Nahallage et al. 2008), however, in some parts of the North
Central Province, Gray Langurs cause more damage than
Toque Macaques (Perera & Vandercone
2016).
The main objective of this study
was to determine the present status of human-primate interactions in relation
to home garden crop damage in selected areas in Kegalle
District. This study looks into the wild animals in the selected study area and
their impact on home garden crops. Home garden cultivations are very important
to these low-income rural villagers, as they supply food to meet their daily
needs and allow them to earn additional income by selling the excess harvest.
The specific objectives were to find out the extent of crop damage by non-human
primates and other wild animals, the types of crops that are mostly affected by
crop raiding primates, the types of property damage they do, the control
measures used by humans to prevent or reduce crop damage and the people’s
perception of the type of mitigative actions that should be taken to control
conflicts.
Methods
The selected study area was in
the Galigamuwa Divisional Secretariat Division (DSD)
in the Kegalle district, Sabaragamuwa
Province. Out of the 51 Grama Niladhari
Divisions (GN divisions), three GN divisions namely Aruggammana,
Hathnapitiya, and Karagala
were purposely selected as they recorded higher incidents of human primate
interactions according to the Galigamuwa DSD office
(Image 1). This was a descriptive cross-sectional study.
Galigamuwa DSD is located in the wet zone,
and receives more than 2,500 mm annual average rainfall, and has a mean
temperature of 22–27 0 C. Agriculture is the main economic sector in
the area. The land extent is 127 km2. Hapudeniya
is the highest parish in the division at 366 m above sea level and the lowest
is Helamada at 27m. The two primate sub-species
present in the area are Macaca sinica aurifrons and Semnopithecus vetulus nestor.
Location of the home gardens
Of the home gardens, 48% in Hathnapitiya, 32% in Aruggammana,
and 80% in Karagala are located less than 50 m from
the forest. Most of the home gardens in Karagala are
located at the edge of the forest.
Compared to Karagala GN divisions, most home
gardens in Hathnapitiya and Aruggammana
are located more than 100 m away from the forest edge (52% in Hathnapitiya and 68% in Aruggammana).
A total of 500 households were
surveyed (Table 1). The electoral registers lists were obtained from Grama Niladhari officers in the respective
GN Divisions to randomly select the houses for the survey. In instances where
the people were not willing to participate in the survey or had vacated these
houses, the next address was selected. The study was conducted between October
and December 2018.
We used an
interviewer-administered questionnaire method to collect data from each
household for the survey. We obtained the required information from the head of
the house or an adult (wife, parents or in- laws of the head of the house)
present in each house at the time the data collectors visited the house. The
structured questionnaire included 19 closed and open-ended questions on such
topics as: occupation of the informant; the size of the home garden; types of
crops cultivated; average monthly income; types of wild animals frequenting the
home garden; the types of crops consumed or damaged by the animals; the extent
of property damage; the measures taken to control the damage, and the peoples’
perceptions on how to control the damage caused by primates. Before collecting
these data, we explained the purpose of the survey to the participants. Those who were willing to provide information
were then given enough time to ask questions regarding the survey, and their
written consent was obtained with a signature at the bottom of each
questionnaire. On average, it took about 20 minutes to fill the questionnaire.
In addition, we conducted field observations as well.
The collected data were entered
into a Microsoft Excel sheet and analyzed using SPSS
package (version 16).
Results
Occupation of the informants
Except for Aruggammana
GN Division, the majority of the informants were housewives (Table 2). Aruggammana and Karagala have
more self–employed informants than Hathnapitiya.
Size of the Home Garden
All three GN divisions had many home gardens
of less than 1.0 acre (4047 m2) in size, representing 93% of home
gardens in Hathnapitiya, 66% in Aruggammana
and 82% in Karagala (Table 3). When compared with the
other two GN divisions, 33% of the home gardens in Aruggammana
were larger, ranging from 1 to 5 acres.
Types of crops cultivated in the
home gardens
The most common home gardening
crops grown in all three GN divisions were coconuts (15%), Jack fruits (13%),
areca nuts (13%), pepper (10%), and bananas (9%). More people grow coconuts in Hathnapitiya than Aruggammana and
Karagala, while tea was cultivated more in Aruggammana and Karagala areas
(Table 4).
Economic loss due to crop damage
During the time of data
collection, the informants of Hathnapitiya (50%), Aruggammana (23%), and Karagala
(21%) stated that they could not get sufficient harvest from home gardens for
their consumption. All of the Hathnapitiya, 94% of Aruggammana, and 62% of Karagala
respondents informed us that at present they cannot get sufficient additional
income from home garden crops. Of the informants, 4% from Aruggammana
and 33% from Karagala said that they get less than
SLR 10,000 income per month and only 1% of Aruggammana
and 6% of Karagala informants said they receive more
than SLR 10,000 income per month (Table 05).
Reasons for not engaging in
cultivation
In all three GN divisions people
gave various reasons for not cultivating crops in home gardens, however, the
majority of the informants stated the main reason was crop damage caused by
wild animals, mainly primates (Hathnapitiya 87%, Aruggammana 92%, Karagala 94%).
The other reasons were not enough manpower (Hathnapitiya
5%, Aruggammana 4%, Karagala
6%), inadequate land area (Hathnapitiya 5%, Aruggammana 2%), inadequate water (Hathnapitiya
2%, Aruggammana 2%), and infertility of the soil (Hathnapitiya 1%).
Animals responsible for crop
damage
In all three respective GN
divisions, the main species identified as responsible for crop damage were Toque
Macaques, Wild Boars, porcupines, and Purple-faced Leaf Langurs (Table 6).
According to informants the NHPs
frequent home gardens irrespective of the time of the day (Table 7).
The crops utilized by animals
The three main crops that the NHP
utilized most were coconuts, bananas, and different types of yams. In addition,
they consumed garden vegetables including brinjal Solanum melongina, winged beans Psophocarpus
tetragonolobus, snake gourds Trichosanthes
cucumerina, long beans Vigna unguiculata, lady’s-fingers Abelmoschus
esculentus (Table 08).
Consequences of crop damage by
animals
Decreases in harvests (Hathnapitiya 59%, Aruggammana
51%, Karagala 43%) and income (Hathnapitiya
16%, Aruggammana 22%, Karagala
28%) were the main effects of crop damage by animals. As a result, people have
discontinued home garden cultivation (Hathnapitiya
25%, Aruggammana 26%, Karagala
27%), and some have abandoned all or parts of their lands as they cannot
control animal visits (Aruggammana 1%, Karagala 2%).
Property damage caused by Toque
Macaques and langurs
In addition to crop damage, Toque
Macaques and langurs also damage property. Toque Macaques caused the most
property damage by entering houses and damaging household furniture and
utensils (Table 9).
Langurs were not reported to
cause much property damage, which was only reported in 2 GN divisions where
langurs caused damage to roofs (Table 9). There were no reports of other wild
animals causing property damage.
Methods used by people to control
crop damage by primates
Methods used to prevent primates
from entering gardens are described in Table 10. The most common methods used
to chase away monkeys were firecrackers, catapults, and wooden or plastic face
masks. During the study period some people had been using air rifles to chase
monkeys from their gardens, a new addition to control methods.
Recommendations to control crop
damage by primates.
Suggestions by informants to
reduce primate crop damage were: 46% wanted monkeys relocated into other areas;
30% suggested sterilizing them to control population growth; 9% think
government authorities should provide mitigative strategies; 10% wanted
permission to use guns; and 5% suggested killing monkeys (5%).
Discussion
Crop damage by primates and other
wild animals
Although most studies on
human-primate negative interactions were concentrated on commercial farming,
the present study mainly focused on the human-primate interactions occurring
due to crop raiding of primates on home gardens. In the semi urban and rural
areas in Sri Lanka, local people grow crops such as coconuts, banana, jack
fruits, areca nuts, vegetables, and different kinds of spices in their home
gardens to meet their daily food needs. Before the intensification of crop
raiding, people have been able to obtain their daily food needs and an
additional income from their home gardens. This way, they do not have to spend
much money to buy food items. Home gardening has been a very important means of
maintaining their economic status for generations.
However, at present, people are
facing many problems as wild animals have started to frequently raid home
gardens to take food (Nahallage & Huffman 2013;
Cabral et al. 2016; Dela et al. 2016; Perera & Vandercone 2016;
Prasad et al. 2016; Rudran & Kotagama
2016; Cabral et al. 2018; Dittus et al. 2019). The
majority of home gardens in the study area are comparatively small (less than 1
acre) and primates cause extensive damage to these small-scale garden cultivations.
The majority of the informants of all three GN divisions complained that they
cannot get adequate harvest for their daily needs and that they had to buy
coconuts and vegetables from the market. This is creating a new economic burden
as these people are in the low-income group and face economic hardships because
of the crop damage. The crops that are mainly affected by primates and other
wildlife were coconuts, bananas, and vegetables, the key food varieties of
these communities. The animals that are causing considerable damage to coconuts
were Toque Macaques in all three study areas. According to informants, macaques
visit the gardens daily and drop the young coconuts to the ground and also peel
off the mature coconuts and eat the soft flesh inside. This way, many immature
nuts get destroyed resulting in a decrease in the total harvest. During the
field visits the authors were able to observe these young coconuts piled up by
the side of the garden. Furthermore, the macaque visits were not limited to a particular
time of the day, and they stayed for a long time which escalated the scale of
damage. This situation has led some people to abandon growing and tending
coconut trees, as they believe that it was a waste of time and money. At
present, people are buying coconuts from the nearby markets for their own
consumption. Coconuts have been one of their main additional income generating
crops. Therefore, currently the people not only have to spend money to buy
coconuts but have lost their additional income as well. However, Purple-faced
Leaf Langurs were not reported to damage coconut trees in the study area.
The other home garden crop that
was mostly affected by the primates was banana. Both Toque Macaques and
Purple-faced Leaf Langurs raid banana trees. They not only eat the banana
fruits but damage the trees which reduces future harvests as well. Of the two
primates, langurs consume the banana most. Informants stated that langurs
mostly consume the unripe fruit while the macaques eat the ripe yellow fruit. However,
in a separate study, Purple-faced Leaf Langurs were reported to eat ripe fruits
in some districts of the country (Dela 2012). Other
than bananas, both primate species were reported to consume jack fruit,
pineapple, other available fruits, vegetables, and yams, depending on the
season. In general, macaques cause more damage to crops than langurs in all the
districts in the country. The omnivorous macaques consume a diverse range of
food items including fruits, leaves, bark, flowers, seeds, roots, cereals,
insects, other invertebrates, eggs, small mammals, birds, and food prepared by
humans. Owing to these diverse food habits and larger group sizes, macaques can
adapt to any environmental condition and hence cause more damage than the two
langur species. According to the study conducted by Prasad et al. (2016), of
the complaints received by the Wildlife Department, 54% were against macaques
and 29% against Purple-faced Leaf Langurs. Out of these, 70% were related to
crop damages; however, the primate species responsible for crop damage was
different in different parts of the country. According to the study of Perera & Vandercone (2016),
in Mihintale Kaludiyapokuna
forest edge farms, Gray Langurs and Toque Macaques
were responsible for 78% and 22% of the reported crop damages, respectively.
Purple-faced Leaf Langurs were not recorded to damage crops in that area. A
study carried out by Dittus et al. (2019) in Polonnaruwa reported similar results indicating that
macaques and Gray Langurs were responsible for
human-primate interactions rather than the Purple-faced Leaf Langurs. In
Western province, it is the Purple- faced Leaf Langurs that cause the most
damage to home garden crops (Dela 2007; Rudran 2007; Nahallage et al.
2008; Cabral et al. 2016; Prasad et al. 2016; Nahallage
2019). The other factors that are responsible for crop damage are the
availability of natural foods, the variety of crops grown, seasonality,
distance from the forest and the people’s perceptions (Hill 2005). According to some informants in Hathnapitiya GN division, the frequency of primate visits
was less during the months of January to July as it was the fruiting season and
monkeys could find food in the forests where they live.
In addition to primates, the
other wild animal species that are responsible for crop damage in the study
area are the two nocturnal mammals: the Wild Boars and porcupines. These
animals mainly damage the vegetables and the yams that people grow. Next to
macaques, Wild Boars caused the most damage to cultivations followed by
porcupines. Most of the people in the three GN divisions have stopped
cultivating home garden crops due to the crop damage caused by wildlife
resulting in the decrease of the harvest and income as well.
In addition to crop damage,
primates were the only wildlife species reported to damage property. Macaques
were reported to have damaged the household goods such as pots, pans, plates,
rice cookers, and furniture. When they are able to enter into a house in an
unguarded moment, they consume the foods stored inside cupboards and racks,
runaway with the cooked and other types of dry foods, defecate inside the house
and damage roofs as well. Similar incidence was reported in Kandy district
where macaques were responsible for taking food by force, damaged the roof, and
damaged the infrastructure (Cabral et al. 2016). Compared to macaques, langurs
cause less property damage and the only reported damage by the langurs (PFL –
present study and Gray Langur – Dittus
et al. 2019) was to roofs due to their large body size. In the study area,
people used wire meshes and wood planks to cover their windows and spaces
between the roof and the walls. This successfully cut down the multiple entry
points of the monkeys to one’s house (CN personal observation). This leaves the
monkeys to come into the house either from the back or front door, which only
the boldest ones would try.
Methods used by people to reduce
crop damage
People believe that over the
years the primate populations have increased and many now consider them as
pests due to crop damage. The methods used by people in the study area to
reduce primate crop damage were similar within the country as well as in other
countries. The most common methods were the use of stones, firecrackers,
shouting, and catapults to chase the primates away from their properties with
very little success (Nahallage et al. 2008; Hill
& Webber 2010; Dittus et al. 2019). The monkeys
get used to or learn to avoid these methods and with time the methods become
less effective. People abstain from hunting, killing or poisoning monkeys due
to their religious beliefs and most of the time are tolerant of their behaviors (Nahallage &
Huffman 2013), or they employ methods just to chase the monkeys from their home
gardens. The people in the study area wear long black cloths with a wooden or
plastic face mask and carry a stick to scare the monkeys, or point a gun shaped
wooden stick at them. This seems to work better compared to other methods. In
the study area, the most effective technique was air rifles. The monkeys were
afraid of them. However, since the air rifles were expensive most people cannot
afford to buy them. In addition, people wrap thorny branches of jackal jujube Ziziphus oenoplia
and lime Citrus aurantifolia around banana
bunches or on the fronds to prevent monkeys from getting to the fruits or they
cover the banana bunches with nylon nets or bags. To protect coconuts, they
wrap aluminium sheets around coconut trees to prevent macaques climbing the
trees. Further they sprinkle cow dung mixed with water on coconuts and the
informants believed that macaques dislike the smell of cow dung. During a
survey in the Northwestern province CN observed that
in some coconut plantations, people covered the young coconut bunch with iron
mesh so macaques could not reach the coconuts. However, the owner of the
plantation informed this was both time consuming as well as costly and that
they must increase the mesh size when the coconuts increase in size (CN
personal observation). This is not practical to implement in large coconut
estates. The use of dogs to chase the monkeys has not been much in practice in
the present study areas. The most effective method the informants used to
protect crop damage by wild boar was to cover the vegetable beds with sarees to
keep the wild boars away. To protect the vegetables from porcupines, people
sprinkled human hair around the vegetable beds. They reported that the
porcupines dislike this and try to evade such vegetable beds. This method too was
not practical in the long run because the hairs get blown away with the wind
and the rain dampens it reducing its effectiveness.
Mitigative actions to control the
damage caused by monkeys
To reduce the damage caused by
primates to home garden crops, the majority of people wanted the monkeys to be
relocated to another area or sterilized them to control population growth.
Relocation of monkeys has detrimental effects to the monkeys if not managed
properly. For the relocation to be effective, the monkeys have to be
transported to a similar environment or ecological zone that they were used to.
Otherwise, it will not be possible for them to adapt to the new environment
successfully and will have trouble finding necessary food sources and might die
of starvation. Therefore, effective post translocation monitoring mechanisms
should be implemented. Further, translocation of monkeys who were used to
living close to human settlements (and utilize human grown crops) to remote
areas also will not be effective as the monkeys will go in search of nearby
human habitats. Thus, relocation might temporarily solve the problem in one
location but will spread the problem to other parts of the country (Nahallage 2019; Dittus et al.
2019).
Sterilization of the monkeys will
be effective to some extent. Though sterilization requires manpower, veterinary
expertise, and money, it is a permanent solution for population control (Jayalath & Dangolla 2011). In
addition, some countries use birth control as an effective strategy of fertility
control (Shimizu 2012). This is most applicable to monkeys that are seasonal
breeders, making the process reversible, allowing them to resume their normal
cycles and normal pregnancies later. With further studies and investigations
there is a high possibility to apply this method successfully in Sri Lanka as
well.
Further, the informants want the
government to take some initiatives for control and advise them on how they
could best control the situation. So far, the authorities have not conducted awareness
programs for the villagers. According to the discussions the authors had with
the villagers during data collection and field visits, it was obvious that they
do not know much about the primates in their area or even that the primate
species are endemic to the country. Thus, it is important that the villagers
understand the behaviors, life histories and the
factors that drive these primates to the villages. This awareness would give
them an insight into the issue and help them to act accordingly. During the
field visits, intentional provision of food to primates and keeping primates as
pets were not observed in the study area. However, garbage dumping sites and
macaques feeding on garbage dumping sites were observed in all three divisions
Therefore, the authors recommend
the following mitigative actions to control the situation; conduct awareness
programs, introduce proper garbage disposal mechanisms, enrichment of the
natural habitats of the primates and to facilitate long term research to gather
more information.
Conclusion
For decades, scientists and
primatologists across the world have been conducting research studies related
to human primate interactions to find ways to minimize damage to both parties
concerned, such as damage to crops and properties of humans and killing and
wounding of primates. Though these studies provide many useful recommendations,
none of them were able to provide plausible long-term solutions to mitigate
this problem. Nahallage et al. (2018), proposed to
use an integrated management plan (IMP) to minimize the damage to the
conflicted parties. The integrated management plan is mainly based on the: a)
biology and the behavior of the primate; b)
occurrence and the level of damage; c) habitats; and d) interaction between the
primates and the humans. With this method, the local authorities, with the help
of the experts have to decide the control strategies for each of the
above-mentioned components and select control methods that are suitable to
local conditions and implement them with the cooperation of relevant
stakeholders. However, future research is needed to test this plan with
different primate species and under different environmental conditions.
Table 1. Selected sample sizes in
each GN Division.
GN Division |
Total No. of houses in each GN
Division |
Number of houses surveyed |
Aruggammana |
368 |
214 |
Hathnapitiya |
303 |
136 |
Karagala |
232 |
150 |
Table 2. Occupation of the
informants in each GN divisions.
Occupation |
Hathnapitiya |
Aruggammana |
Karagala |
|||
Frequency |
% |
Frequency |
% |
Frequency |
% |
|
No occupation (housewives) |
67 |
49 |
54 |
25 |
72 |
48 |
Government sector |
27 |
20 |
60 |
28 |
21 |
14 |
Private sector |
24 |
18 |
33 |
15 |
21 |
14 |
Commercial farming |
3 |
2 |
1 |
0.5 |
2 |
1 |
Self-employment |
13 |
10 |
66 |
31 |
31 |
21 |
Security service |
2 |
2 |
0 |
0 |
3 |
2 |
Total |
136 |
100 |
214 |
100 |
150 |
100 |
Table 3. Size of the Home garden.
GN Division |
Hathnapitiya |
Aruggammana |
Karagala |
|||
Size of home garden |
N |
Valid Percent |
N |
Valid Percent |
N |
Valid Percent |
Less than 1 acre (less than
4,047 m2) |
103 |
93 |
126 |
66 |
116 |
82 |
Between 1.1 to 5 acres
(4,047–20,234 m2) |
5 |
5 |
63 |
33 |
22 |
15 |
More than 5 acres (more than
20,234 m2) |
3 |
3 |
3 |
2 |
4 |
3 |
Total |
111 |
100 |
192 |
100 |
143 |
100 |
Not responded |
25 |
|
22 |
|
8 |
|
Total |
136 |
|
214 |
|
150 |
|
Table 4. Types of home garden
crops cultivated in the respective GN divisions.
Types of crops |
Hathanapitiya (%) |
Aruggammana (%) |
Karagala (%) |
Coconut |
18 |
14 |
13 |
Banana |
12 |
9 |
7 |
Jack Fruit |
11 |
14 |
13 |
Areca nut |
11 |
13 |
13 |
Pepper |
8 |
11 |
10 |
Avocado |
5 |
6 |
4 |
Vegetables |
5 |
1 |
3 |
Tea |
4 |
8 |
11 |
Clove |
3 |
8 |
6 |
Rubber |
2 |
3 |
3 |
Yams |
2 |
2 |
3 |
Pineapple |
1 |
1 |
1 |
Durian |
1 |
2 |
1 |
Breadfruit |
1 |
1 |
1 |
Magnus |
1 |
0 |
2 |
Betel |
1 |
1 |
2 |
Nutmeg |
0 |
0 |
1 |
Cardamon |
0 |
0 |
0 |
Other |
12 |
7 |
7 |
Table 5. Monthly income obtained
from home gardening.
GN Division |
Hathnapitiya |
Aruggammana |
Karagala |
|||
Income |
Present |
Present |
Present |
|||
N |
% |
N |
% |
N |
% |
|
No income |
136 |
100 |
202 |
94 |
92 |
62 |
Less than SLR 10,000 |
0 |
0 |
9 |
4 |
49 |
32 |
More than SLR 10,000 |
0 |
0 |
3 |
2 |
9 |
6 |
Total |
136 |
100 |
214 |
100 |
150 |
100 |
Table 6. Animals that are
responsible for crop damage.
GN Division |
Hathnapitiya (%) |
Aruggammana (%) |
Karagala (%) |
Toque Macaque |
40 |
34 |
29 |
Wild Boar |
25 |
30 |
25 |
Porcupine |
14 |
23 |
21 |
Purple-faced Leaf Langur |
18 |
7 |
16 |
Giant Squirrel |
1 |
2 |
3 |
Rat |
0 |
1 |
1 |
Snail |
0 |
1 |
1 |
Coconut Beetle |
1 |
0 |
0 |
Peacock |
1 |
1 |
1 |
Parrot |
0 |
0 |
1 |
Grey Hornbill |
0 |
0 |
1 |
Other |
0 |
1 |
1 |
Table 7. The time of animal
visits to home gardens.
GN Division |
Hathnapitiya (%) |
Aruggammana (%) |
Karagala (%) |
Moring only |
6 |
1 |
3 |
Evening only |
6 |
1 |
3 |
Night only |
15 |
0 |
5 |
Anytime of the day |
67 |
96 |
82 |
Cannot say |
6 |
2 |
7 |
Table 8. The crops utilized by
animals.
GN Division |
Hathnapitiya (%) |
Aruggammana (%) |
Karagala (%) |
Coconut |
22 |
29 |
21 |
Vegetables |
19 |
4 |
9 |
Banana |
15 |
12 |
12 |
Yams (kiri
ala, casava) |
12 |
16 |
15 |
Pepper |
4 |
9 |
10 |
Areca nut |
3 |
6 |
8 |
Jack Fruit |
4 |
6 |
5 |
Pineapple |
2 |
1 |
1 |
Tea |
1 |
4 |
5 |
Avocado |
1 |
1 |
1 |
Rubber |
1 |
2 |
1 |
Bread Fruit |
1 |
1 |
1 |
Betel |
1 |
2 |
3 |
Durian |
1 |
1 |
0 |
Nutmeg |
1 |
0 |
1 |
Cardamom |
1 |
0 |
0 |
Clove |
0 |
0 |
1 |
Other |
11 |
6 |
6 |
Table 9. Types of property damage
caused by Toque Macaques and Purple-faced Leaf Langur.
Type of Damage |
Hathnapitiya (%) |
Aruggammana (%) |
Karagala (%) |
Macaques |
|||
Damage household goods |
15 |
25 |
27 |
Consume foods that are inside
the house |
35 |
31 |
37 |
Defecate inside the house |
25 |
22 |
23 |
Damage roofs |
24 |
17 |
10 |
Other types of damages |
1 |
5 |
3 |
Purple-faced Leaf Langur |
|||
Damage roof |
15 |
1 |
0 |
No damage |
85 |
99 |
100 |
Table 10.
Methods used to reduce the crop damage by Toque Macaques.
GN Division |
Hathnapitiya (%) |
Aruggammana (%) |
Karagala (%) |
Catapult |
21 |
33 |
30 |
Firecrackers |
42 |
36 |
30 |
Masks |
10 |
7 |
10 |
Hanging tin cans |
1 |
0 |
0 |
Nets to cover crops |
2 |
3 |
6 |
Boards |
1 |
1 |
6 |
Shouting |
11 |
4 |
4 |
Black cloth |
1 |
1 |
1 |
Air rifles |
0 |
1 |
1 |
Use of dogs |
0 |
1 |
1 |
Clapper board |
0 |
1 |
1 |
Others |
11 |
12 |
10 |
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