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Human-Elephant Conflict Mitigation Measures: Lessons from Bangladesh

Authors:
  • Independent Consultant

Abstract

In Bangladesh, the Asian elephant is categorized as Critically Endangered species due to its small numbers. Now-a-days, death and injury of both humans and elephants have become a common phenomenon in elephant range areas of Bangladesh due to increased human interference in the forests for resources and elephant’s raid within the locality for searching for food. Under the recent ‘Pilot Programs to Identify Effective Measures to Reduce the HEC’ sub-project of the ‘Strengthening Regional Cooperation for Wildlife Protection (SRCWP) Project’ of Bangladesh Forest Department, nine human-elephant conflict mitigation measures have been piloted in the human-elephant conflict-prone south-eastern elephant ranges of Bangladesh (2013−2016). These options include, cultivation of non-preferred crops by farmers, bio-fencing with suitable plant species, solar electric fencing, trip alarm, chilli rope, watchtower, salt lick, plantation in elephant habitats, and creating Elephant Response Teams. This book briefly documents these mitigation technologies and captures the lessons learnt from piloting them.
Human-Elephant Conflict
Mitigation Measures:
Lessons from Bangladesh
INTERNATIONAL UNION FOR CONSERVATION OF NATURE
Human-Elephant Conflict
Mitigation Measures:
Lessons from Bangladesh
Asian Elephant (Elephus maximus)
© IUCN /Sultan Ahmed
Human-Elephant Conflict
Mitigation Measures:
Lessons from Bangladesh
Authors
Md. Ahsanul Wahed
Mohammad Rahmat Ullah
Haseeb Md. Irfanullah
Institutional Advisor
Ishtiaq Uddin Ahmad
IUCN, International Union for Conservation of Nature
Dhaka, Bangladesh
2016
The designation of geographical entitles in this book and the presentation of the material, do not imply the expression of any opinion
whatsoever on the part of IUCN, International Union for Conservation of Nature concerning the legal status of any country, territory,
administration, or concerning the delimitation of its frontiers or boundaries. The information, database and views expressed in this book
are not necessarily reflecting those of IUCN, Bangladesh Forest Department and The World Bank.
The publication has been made possible because of the funding received from The World Bank through Bangladesh Forest Department
to implement the subproject entitled ‘Pilot Programs to Identify Effective Measures to Reduce the HEC’ under the ‘Strengthening
Regional Cooperation for Wildlife Protection’ project.
Published by: IUCN Bangladesh Country Office, Dhaka
Copyright: © 2016 IUCN, International Union for Conservation of Nature and Natural Resources
Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written
permission of the copyright holders, provided that the source is fully acknowledged.
Reproduction of this publication for resale or other commercial purposes is prohibited without prior written permission
of the copyright holders.
Citation: Wahed, M.A., Ullah, M.R. and Irfanullah, H. Md. 2016. Human-Elephant Conflict Mitigation Measures: Lessons from
Bangladesh. IUCN, International Union for Conservation of Nature, Bangladesh Country Office, Dhaka, Bangladesh. 30 pp.
Design by: Sheikh Asaduzzaman
ISBN: 978-984-34-1219-5
Cover Photo: Left to Right- Non-preferred crop cultivation © IUCN/Iqram Uddin Al Amran; Bio-fencing © IUCN/Rupon Barua;
Bamboo
seedling raising at nursery for plantation at core zone of elephant
© IUCN/S.M. Rasel; Solar electric fencing ©
IUCN/Rupon Barua; Trip alarm installation © IUCN/Md. Fazlay Arafat; Watchtower © IUCN/Md. Fazlay Arafat.
Available from: IUCN, International Union for Conservation of Nature
Bangladesh Country Office
House 16, Road 2/3, Banani
Dhaka 1213, Bangladesh
www.iucn.org/bangladesh
Preface
The Asian elephant plays a crucial role in its forest ecosystem. Commonly referred to as a ‘keystone’ species, it helps to
open up forest clearings and distributes the seeds of trees and shrubs. The magnificent animal becomes threatened due to
poaching, destruction of forest and conflict with human. In recent years, the magnitude of human-elephant conflict (HEC)
has increased due to anthropogenic causes by increased population in many areas of Bangladesh. Due to fragmentation of
habitats, elephant ranges in Bangladesh have become confined to small patches occupied by a single or few small herds.
Some corridors have been abandoned due to degradation of forest cover, extension of human settlements, development of
infrastructure, intensification of agricultural practice, unsustainable slash and burn practice, and unplanned road construction,
for example.
The initiative entitled ‘Pilot Programs to Identify Effective Measures to Reduce the HEC’, a sub-project of ‘Strengthening
Regional Cooperation for Wildlife Protection (SRCWP) Project’ has been designed to address and reduce human-elephant
conflict with support from Bangladesh Forest Department and The World Bank. The project carried out research on the
nature of human-elephant conflict to come up with appropriate solutions. The initiative further piloted a number of mitigation
measures, such as non-preferred crop cultivation, trip alarm, solar electric fencing, chilli rope, establishment of watch tower,
elephant response team and bio-fencing, to identify their effectiveness for reducing human-elephant conflict. Side by side,
for habitat improvement, plantation of fodder and shade tree and establishment of salt lick have been carried out.
The production and publication of this book is intended to capture the successes and lessons learnt from the ‘Pilot Programs
to Identify Effective Measures to Reduce the HEC’ project and to document the impacts of piloted initiatives and key lessons
generated. We believe this document will be useful to policy makers, project implementers, academicians and researchers
interested in the field of elephant conservation as well as wildlife conservation in general.
Ishtiaq Uddin Ahmad
Country Representative
IUCN Bangladesh Country Office
Message
Elephants have ingrained in our culture. The importance of conserving the Asian Elephant in Bangladesh is now established.
Most Asian elephant populations are mostly fragmented and pocketed, and therefore more vulnerable to extinction. Being
one of the Asian Elephant range countries, Bangladesh holds the responsibility to lend a hand to the global effort for
conserving this majestic animal.
The population of Bangladesh has increased in course of time which contributed to land use change and increased
dependency of people over natural resources. Human interference within the forest increased conflict with wildlife in different
parts of Bangladesh. The conflict between human and resident elephant is confined in Chittagong, Chittagong Hill Tracts
and Cox’s Bazar. Conflict with the migratory elephants is a serious concern in the central-north districts, namely Sherpur,
Mymensingh and Jamalpur. Now-a-days, death and injury of both humans and elephants become common phenomenon
in elephant ranges of Bangladesh.
Conflict between humans and elephants have become an important issue for conservationists over the last two decades. To
reduce human-elephant conflict, Bangladesh Forest Department in association with IUCN Bangladesh initiated the project
entitled “Pilot Programs to Identify Effective Measures to Reduce the HEC” under “Strengthening Regional Cooperation for
Wildlife Protection” project with support from The World Bank.
The initiative has piloted innovative technologies in elephant ranges of Chittagong and Chittagong Hill Tracts that contributed
to minimise human-elephant conflict. I believe that the replication of these technologies in conflict prone-areas of Bangladesh
will assist conflict management at scale.
Md. Yunus Ali
Chief Conservator of Forests
Bangladesh Forest Department
Ministry of Environment and Forests
Acknowledgements
It gives us great pleasure to acknowledge Bangladesh Forest Department and The World Bank, for their support towards
implementation of the sub-project entitled ‘Pilot Programs to Identify Effective Measures to Reduce the HEC’ under the
‘Strengthening Regional Cooperation for Wildlife Protection (SRCWP) Project’ and capture its lessons though this publication.
We would like to express our sincere gratitude to Md. Yunus Ali, Chief Conservator of Forests, Bangladesh Forest
Department and Ishtiaq Uddin Ahmad, Country Representative, IUCN Bangladesh for their immense support and direction
for implementation of this project.
Special thanks to Dr. Aparup Chowdhury and Akbar Hossain, the former Project Directors of SRCWP Project and Md. Abdul
Mabud, Project Director, SRCWP Project, for their rigorous support during the implementation of the sub-project. Thanks
are also due to the Ashit Ranjan Paul, Conservator of Forests, Wildlife and Nature Conservation Circle and his predecessor
Dr. Tapan Kumar Dey for their continuous support and direction.
We appreciate the effort of relevant Conservator of Forests, Divisional Forest Officers and Assistant Conservator of Forests
who have led consultation workshops at the local level and helped in plantation programme. Our thanks especially go
to Abdul Latif Mia, Mohammad Abdul Awal Sarker, Md. Ali Kabir, S.M. Golam Mowla, Bipul Krishna Das, Hoq Mahbub
Morshed, Abu Naser Mohsin Hossain, and Kajal Talukder.
Thanks are also due to relevant Range Officers and Beat Officers of Bangladesh Forest Department who supported the
project team during project implementation.
Special thanks are due to IUCN Bangladesh project team who supported implementation of the project and the authors in
the creation of this document: Nasim Aziz, Md. Ahsanul Wahed, Md. Fazlay Arafat, Babla Mohajon, Rupon Barua, Iqram
Uddin Al Amran, Bokhtiar Uddin, Md. Akhter Hossain, Dr. Haseeb Md. Irfanullah, Mohammad Rahmat Ullah, Mohammed
Abdul Motaleb, Md. Ashraful Haque, Mohammad Sultan Ahmed and Zubair Hussni Fahad. Thanks are also due to Sheikh
Asaduzzaman of IUCN Bangladesh for designing this book and Ishrat Binte Mahmud for language editing.
Md. Rezaul Karim Chowdhury
Principal Investigator
Pilot Programs to Identify Effective Measures to Reduce the HEC
IUCN Bangladesh Country Office
Cultivation of Okra as non preferred crop to mitigate crop damage
© IUCN /Md. Fazlay Arafat
Table of Contents
Prologue 10
Elephants in Bangladesh 11
Nature of Human-Elephant Conflict 13
Human-Elephant Conflict Management in Bangladesh 15
Human-Elephant Conflict Mitigation Techniques 17
Non-preferred Crop Cultivation 19
Bio-fencing 20
Solar Electric Fencing 21
Trip Alarm 22
Chilli Rope 23
Watchtower 24
Salt Lick 25
Plantation in Elephant Habitat 26
Elephant Response Team 27
Way Forward 28
Prologue
Asian Elephant (Elephus maximus)
© IUCN /Rajib Mahamud
Elephants in Bangladesh
Elephants have both ecological and cultural importance. They
are known as ecosystem’s engineer and gardener. They play a
vital role in forest enhancement by disbursing seeds and creating
environment for germination. Dung of elephant plays a crucial
role in nutrient cycling by providing nutrients to the soil that is
ultimately used by the flora. It is also a good source of food for
many insect species. It is well understood that elephant is playing
a key role, particularly in maintaining diversity of flora and fauna,
and regenerating the forest environments.
Asian elephants are categorized as Critically Endangered species1
in Bangladesh due to reduction of population. The demand of
land by the increasing human population is changing the land
use system leading to encroachment and fragmentation of
forests and subsequent food scarcity for elephants and human-
elephant conflict. Results of studies indicate about 100 years
ago, elephants were apparently found in most of the forests of
Bangladesh2. Even in the middle of last century, existence of 500
elephants throughout the forest of Bangladesh was reported
by the scientists3. With start of this century, a study found the
number of Asian elephant in Bangladesh reduced to 228-3274
due to above mentioned reasons.
1 IUCN Bangladesh. 2015. Red List of Bangladesh Volume 2: Mammals. IUCN, International Union for
Conservation of Nature, Bangladesh Country Office, Dhaka, Bangladesh, pp. xvi+232.
2 Alam, M.K. 2008. Forests and Forestry in Bangladesh. In: Ahmed, Z.U., Begum, Z.N.T., Hassan, M.A.,
Khondker, M., Kabir, S.M.H., Ahmad, M., Ahmed, A.T.A., Rahman, A.K.A. and Haque, E.U. (eds). Ency-
clopedia of Flora and Fauna of Bangladesh, Vol. 1. Bangladesh Profile. Asiatic Society of Bangladesh,
Dhaka.
3 Choudhury, A. 2007. Impact of border fence along India-Bangladesh border on elephant movement.
Gajah 26: 27-30.
4 IUCN Bangladesh. 2004. Conservation of Asian Elephants in Bangladesh. IUCN, Bangladesh Country
Office, Dhaka, Bangladesh.
Human-Elephant Conflict Mitigation Measures: 11
Lessons from Bangladesh
Property damaged by elephant
© IUCN /Rupon Barua
Nature of Human-Elephant Conflict
The conflict between human and resident elephant is common in Chittagong, Chittagong Hill Tracts and Cox’s Bazar
regions of Bangladesh. On the other hand, the conflict with the migratory elephants is a serious concern in the central-
north districts, namely Sherpur, Mymensingh and Jamalpur. Now-a-days, death and injury of both humans and elephants
become common phenomenon in elephant range areas of Bangladesh due to increased human interference in the
forests for resources5 and elephant’s raid within the locality for searching for food. Examples of casualty will provide better
understanding on the nature of human-elephant conflicts. In March 2016, a resident of Chambol beat in Bashkhali upazila
(sub-district) of Chittagong district went to forest for collecting fuel wood and was killed by wild elephant in the noon.
During April-June 2015, seven people were killed by elephant in Chunati Wildlife Sanctuary, Chittagong and most of the
killings took place within the reserve forest by a single elephant. In December 2014, three people were killed and another
one was injured as raiding elephants invaded several villages at Satkania upazila of Chittagong district6. A few months
later in April 2015, dead bodies of two young elephants were discovered in this upazila without any external damage
and the reason behind death is still unknown, while local people guessed poisoning might be the reason of death. The
damage of crops is high in many elephant range areas of Bangladesh than other incidences. It was estimated that 760
conflicts were related to crop damage out of 920 conflicts occurred during January 2014−May 2016 within the project
areas, namely Rangunia, Khurusia, Jaldhi, Chunati and Bandarban Sadar Ranges.
5 Sarker, A.H.M.R. and Roskaft, E. 2011. Human-wildlife conflicts and management options in Bangladesh, with special reference to Asian elephants (Elephas maximus). International Journal
of Biodiversity Science, Ecosystem Services and Management, 6(3-4): 164-175.
6 Sarker, A.H.M.R., Hossen, A. and Roskaft, E. 2015. Fatal elephant encounters on humans in Bangladesh: Context and incidences. Environment and Natural Resources Research, 5(2): 99-
108.
Human-Elephant Conflict Mitigation Measures: 13
Lessons from Bangladesh
Crop damaged by elephant
© IUCN /Md. Fazlay Arafat
Elephant casualty
© IUCN Bangladesh
Human-Elephant Conflict Management in Bangladesh
Human-elephant conflict minimisation has become a major challenge for the Government of Bangladesh. The
Government has taken different initiatives to minimise the conflict. In 2001, Bangladesh Forest Department formed Wildlife
and Nature Conservation Circle for safeguarding biodiversity and wildlife. Formation of Co-Management Committees
(CMCs) in protected areas involving forest-dependent people for conserving forest and wildlife has been practiced by
Bangladesh Forest Department. However, elephant habitats are not confined only within the protected areas. At the
end of 2001, IUCN Bangladesh and Bangladesh Forest Department commissioned a project with support from U.S.
Fish and Wildlife Service for elephant census and threat identification and prioritisation. In the following decade, these
three organisations continued their efforts in conserving Asian elephants in Bangladesh where human-elephant conflict
minimisation remained an important aspect.
In 2013, Bangladesh Forest Department took three
sub-projects under The World Bank-supported
‘Strengthening Regional Cooperation for Wildlife
Protection (SRCWP) Project’ to count elephant,
identify elephant routes and corridors, and to minimise
human-elephant conflicts in Sherpur, Chittagong and
Bandarban areas. Bangladesh Forest Department, in
association with IUCN Bangladesh and HEDS, has
taken pragmatic initiatives to reduce human-elephant
conflict. The Department, in collaboration with IUCN
Bangladesh, has formalised Elephant Response
Teams for minimising conflicts in the central-north and
south-eastern conflict-prone areas.
In addition to the formation of Elephant Response
Teams, IUCN Bangladesh has introduced a range of
conflict management techniques at the grassroots
level under the ‘Pilot Programs to Identify Effective
Measures to Reduce the HEC’ sub-project of the
SRCWP Project. These human-elephant conflict
mitigation technologies include, cultivation of non-
preferred crops by farmers, bio-fencing, solar electric
Human-Elephant Conflict Mitigation Measures: 15
Lessons from Bangladesh
Bio-fencing
© IUCN/ Rupon Barua
fencing, chilli rope, watchtower, and setting up early warning systems,
which have been piloted in different conflict-prone areas of the south-
eastern part of Bangladesh. In addition, for enriching habitats for wild
elephants, the sub-project has planted suitable species in around 260
hectares of land in Sherpur, Chittagong and Cox’s Bazaar districts. Salt lick
has been established to meet demand of minerals by the wild elephant.
Awareness raising initiatives have been taken to change mind set and
knowledge of people for minimising conflicts. For trans-boundary elephant
management, the first dialogue took place between the Forest Departments
of Bangladesh and India with an aim to secure elephant habitats and
the free movement of this mega-fauna. Capacities building of Elephant
Response Teams on techniques to stray elephants from the locality and
cultivation of non-preferred crop have also been done.
Before piloting the human-elephant conflict mitigation technologies in
the field, secondary literature was reviewed to select appropriate o
ptions.
The short-listed options were then consulted with the local stakeholders,
like affected communities, local government representatives and officials of
Bangladesh Forest Department for piloting. Selection of people and sites for
piloting of options was done through consultation with these stakeholders. This
gave them an opportunity to accept these technologies and to get involved in
the piloting. Monitoring has been done by the stakeholders and project team
regularly to find out the impacts created in the field. Along with the piloting,
people have been engaged in awareness programmes and data collection for
knowing the nature of human-elephant conflict.
This book briefly documents nine mitigation technologies and captures
the lessons learnt from piloting them under the ‘Pilot Programs to Identify
Effective Measures to Reduce the HEC’ sub-project in the south-eastern
elephant range in Bangladesh. It is expected that the knowledge generated
from this pilot intervention will help wildlife biologists, wildlife managers,
policy-makers, and other stakeholders in minimising human-elephant
conflicts in Bangladesh and elsewhere with similar social, environmental and
wildlife management contexts.
16 Human-Elephant Conflict Mitigation Measures:
Lessons from Bangladesh
Cane plant (Daemonorops jenkinsiana)
© IUCN /Rupon Barua
Human-Elephant
Conflict Mitigation
Techniques
Bio-fencing with cane
© IUCN /Md. Fazlay Arafat
The techniques piloted to mitigate human-elephant conflicts can be divided into three broad categories. The first group
includes innovations like i) non-preferred crop cultivation, ii) bio-fencing, iii) solar electric fencing, iv) trip alarm, v) chilli
rope, and vi) watchtowers. The second group is about improving elephant habitat through establishing i) salt lick and ii)
plantation for elephants. The final category includes organising community people living in elephant ranges into smaller
groups − Elephant Response Teams – and building their capacity to mitigate human-elephant conflict not only for pushing
away elephants invade their localities, but also helping their communities with above mitigation technologies and by
raising their awareness. Piloting of these mitigation measures in the field has created a scope to identify the effectiveness
of these techniques in conflict mitigation for scaling up.
18 Human-Elephant Conflict Mitigation Measures:
Lessons from Bangladesh
Non-preferred crop (Chilli) cultivation
© IUCN /Iqram Uddin Al Amran
Chilli rope demonstration
© IUCN /Md. Fazlay Arafat
Watchtower
© IUCN /Iqram Uddin Al Amran
Plantation at Chunati site
© IUCN /Babla Mohajon
Machineries of solar electric fencing
© IUCN /Rupon Barua
Elephant sign within salt lick
© IUCN /Md. Fazlay Arafat
Non-preferred Crop Cultivation
Under natural conditions, elephants mostly prefer
plants, like paddy, grass, bamboo, jackfruit, mango,
and banana. Some unpalatable crops, for example
chilli, citrus, bitter gourd, okra, taro and teasel gourd are
considered as non-preferred crops for elephants as they
do not like these crops because of their tastes. Literature
review and consultations with local farmers helped to
identify non-preferred crops suitable for the project
sites. Through local level consultation, project team also
identified suitable sites to grow these non-preferred
crops to pilot if these can reduce crop loss and elephant
disturbance in the locality. Before piloting, affected
farmers were selected and subsidised with cultivation
materials.
Piloting has shown that only 3% area of 36 non-preferred
crop plots got damaged by elephants trampling. The
figure is much less than the damage faced by adjacent
preferred crop plots where 22% area of 102 crop plots
got damaged by elephants. The positive impact of
non-preferred crop cultivation needs to be extensively
channeled through Department of Agricultural Extension
so that farmers of the human-elephant conflict zones of
Bangladesh can adopt the technology and reduce crop
and economic losses.
Human-Elephant Conflict Mitigation Measures: 19
Lessons from Bangladesh
Okra cultivation
© IUCN /Md. Fazlay Arafat
Taro cultivation
© IUCN /Md. Fazlay Arafat
Chilli cultiation
© IUCN //Iqram Uddin Al Amran
Teasel gourd cultiation
© IUCN //Iqram Uddin Al Amran
Bio-fencing
Bio-fences are lines of trees or shrubs planted on the boundaries of farms or human settlements that provide protection
against wildlife. For elephants, bio-fencing technique involves grow cane/rattan (with sharp spines on the stem) on human
settlement boundaries to deter elephants from entering human habitations and crop fields. This technique is environment-
friendly, cost-effective and more useful than fences made of wood, barbed wire, or stone masonry; and effectively
prevents elephants from intruding into villages. Project team in consultation with Bangladesh Forest Department and
local people selected sites and established bio-fences in Kodukhola of Bandarban, Harbang of Chakaria, Cox’s Bazar,
and Chambol of Bashkhali, Chittagong. Moreover, to reduce human-elephant conflicts and to stop elephant coming
from forest to locality, responsibility has been given to Bangladesh Forest Department, local communities and Elephant
Response Teams for monitoring of the bio-fences. To protect these bio-fences, such regular monitoring is essential and
crucial. Sustainable harvesting of bio-fence could be introduced involving community since cane has many uses. Such
closely monitored harvesting system can improve community ownership and enhance community’s interest in protecting
the bio-fences.
20 Human-Elephant Conflict Mitigation Measures:
Lessons from Bangladesh
Establishment of bio-fencing
© IUCN /Rupon Barua
Plantation of cane seedlings
© IUCN /Rupon Barua
Solar Electric Fencing
A solar electric fence is a barrier that uses electric shocks (solar panels to
absorb and convert sunlight into electricity) to deter animals or people from
crossing a boundary. Seven kilometers of solar electric fencing has been
established in Borohatia and Sufinagar of Lohagora upazila, Chittagong and
Vaggokul village of Sadar Upazila, Bandarban to protect human settlement
from elephant attack. Human settlements of those areas were surrounded
by solar electric fences with a voltage of 10 Kilo Volt and 0.0025 ampere.
This technology is simple and definitely deters elephants – if it is
continuously kept under good management. The project team engaged
villagers and officials of Bangladesh Forest Department in all aspects of
decision making and establishment, such as site selection, the electric fence
assembly, construction of concrete posts, clearing the fence line, digging
holes for fence post, erecting fence posts and lines, and operating the
system. Major equipment and the system have been tested by Bureau of
Research, Testing and Consultation of Bangladesh University of Engineering
and Technology. Villagers have been trained to maintain, repair and operate
the electric fence. Three committees have been formed by Bangladesh
Forest Department engaging Elephant Response Teams, representatives
of Co-Management Committees, local elites along with the officials of the
Department in three sites for monitoring and maintenance of the solar
electric fences. A modality of role was also developed for the committee in
consultation with local people and Bangladesh Forest Department to ensure
effective management of solar electric fences, which will help in managing
future human-elephant conflicts.
The technique found to be effective to produce sufficient electric shock to
deter elephants from entering human settlement. It has been observed that
after establishing the solar electric fences in June 2016, elephants did not
enter the human settlements, which never happened in the past.
Human-Elephant Conflict Mitigation Measures: 21
Lessons from Bangladesh
Establishment of solar fencing
© IUCN /Rupon Barua
Trip Alarm
Trip alarm is a warning system to prevent elephants
from damaging the crop fields or human settlements. A
thin wire is installed around a field or a settlement at the
usual entrance of elephants; whenever the wired circuit
is broken, it makes a loud sound. The noise alerts people
and irritates elephants tending them to go back without
entering the human territory. The installation of this cost-
effective early warning system is easy, requiring regular
maintenance without frequent replacements.
The project team piloted 20 trip alarms in the project sites
which were found very effective in repelling elephants.
The team engaged the local communities for selecting
sites in consultation with the officials of Bangladesh
Forest Department. While setting up trip alarms, these
communities were involved in practical training on how
to install and maintain this system. During the period of
February 2015 to March 2016, 13 raids were prevented
by trip alarms at different sites which saved crops and
lives of people. This economical method can be utilized
in a simple way around a large area. Replication of
this initiative in other areas of Bangladesh can help in
reducing human-elephant conflicts.
22 Human-Elephant Conflict Mitigation Measures:
Lessons from Bangladesh
Establishment of trip alarm
© IUCN /Md. Fazlay Arafat
Trip alarm set-up by community
© IUCN /Md. Fazlay Arafat
Setting of trip alarm
© IUCN /Md. Fazlay Arafat
Chilli Rope
Chilli rope is a technique where chilli powder is mixed with grease and dry tobacco leaf, and then applied on ropes along
the perimeter of a crop field for repelling elephants. This technique uses locally available and affordable materials and a
recommended variety of locally grown hottest chilli as elephants do not like the smell of chilli.
This technique was so much interesting for the communities that they participated in the installation and maintenance
without charging for their labour. Both the project team and the community purchased sun-dried chillies from the local
market to prepare the sticky paste by mixing the chilli powder with tobacco leaf and grease. The paste was then smeared
on ropes and put up around selected plots. The project provided materials to pilot a total length of 10 kilometer chilli rope
fence in the project sites. The low-cost, relative to other barriers, has made chilli rope technique an attractive option to be
used in the dry season as rain washes out the effectiveness of the chilli-tobacco-grease rope fence.
Human-Elephant Conflict Mitigation Measures: 23
Lessons from Bangladesh
Setting of chilly rope
© IUCN /Babla Mohajon
Materials for chilly rope
© IUCN /Md. Fazlay Arafat
Chilly rope
© IUCN /Babla Mohajon
Preparation of chilly paste
© IUCN /Md. Fazlay Arafat
Watchtower
Watchtower is a place from where people can do surveillance. Monitoring
elephant activities give an opportunity to take proper action for minimising
loss. Watchtowers for elephant were built with wood, bamboo and
plastic cover/tin-sheet in tall trees (usually 6-9 meters high) with an easy
to climb ladder near the forest boundary and used by guards at night to
detect elephants from a distance. These low cost and simple to construct
watchtowers provide guards the ability to see across the entire farm with
a powerful torch; can be an effective warning system.
A total of 13 watchtowers have been made in different conflict-prone
areas. Site selection and construction of watchtower have been done
through consultation with respective communities and Bangladesh Forest
Department officials of the forest range. The community-based crop
protection scouts have been formed by community themselves who use
the watchtowers. They have been rotationally guarding for the protection
of crops and property from elephant in all seasons. This option improves
the performance of other farm-based deterrent techniques and reduces
crop damage on vulnerable farms.
24 Human-Elephant Conflict Mitigation Measures:
Lessons from Bangladesh
Watchtower
© IUCN /Md. Fazlay Arafat
Salt Lick
Salt licks are artificial deposit of mineral
salts used by elephants to supplement their
nutrition, ensuring enough minerals in their
diets. A wide range of animals, primarily
herbivores use salt licks to get essential
nutrients, like calcium, magnesium, sodium
and zinc. Elephant digs up the licks content
using their tusks and take materials with
the trunk. Site for salt lick preparation was
selected after consultation with officials
of Bangladesh Forest Department and
the communities. All bushes were cleared
keeping only mature trees. Different
proportionate of normal and rock salts were
mixed and spread on the area with watering.
From field data, it was observed that
elephants frequently visited the salt lick area
(0.02 hectare area – an experimental plot in
south-eastern Bangladesh). Salt lick reduces
the demand of minerals by elephants and
in turn reduces damage of household
properties for search of minerals. These also
become a sort of rally points where lots of
elephants can be observed and monitored.
Human-Elephant Conflict Mitigation Measures: 25
Lessons from Bangladesh
Sign of elephant within salt lick area and different steps to prepare salt lick
© IUCN /Md. Fazlay Arafat
Plantation in Elephant Habitat
Not getting enough food in the forests, elephants often come to human territory in search of food. Enrichment of
denuded hills with fodder and shade tree species for ensuring a favourable environment for elephant is termed as habitat
improvement. A total 160 hectares of land have been improved with Bangladesh Forest Department in Cox’s Bazar and
Chittagong. While creating new plantations, the Department has given priority to elephant-preferred species, like bamboo,
banana, jackfruit, mango and chapalish. The maintenance responsibility of these plantations has also been given to the
Department as they are the custodian of those forest lands. Establishment of such forest patches help elephants to
survive by providing them with foods and shelter.
26 Human-Elephant Conflict Mitigation Measures:
Lessons from Bangladesh
Banana Plantation at Dhopachar
© IUCN /Md. Fazlay Arafat
Nursery at Napura beat
© IUCN /Iqram Uddin Al Amran
Plantation at Napura beat
© IUCN /Iqram Uddin Al Amran
Plantation site at Chunati
© IUCN /Babla Mohajon
Elephant Response Team
An Elephant Response Team (ERT) is a group of people (usually 10 persons in a group) working to mitigate human-
elephant conflicts with an active role in conflict incidents and raising human-elephant co-existence related awareness
activities at local level. The project team trained seven Elephant Response Teams and equipped them with hand mikes,
search lights, torchlights, bee sound machines and whistles. These teams were formed upon consultation with local
communities, officials of Bangladesh Forest Department and local government representatives.
Each team is comprised of a team leader and general members. Elephant Response Team members were trained in
the methods on how to stop elephant raid without causing any injury to the elephants to fulfill their roles; for example,
the method to chase elephants from villages or crop fields. Trained members of Elephant Response Team were also
motivated to regulate human-elephant conflict to lessen the property losses and death rate. Elephant Response Team
together with Bangladesh Forest Department have been working to support conservation of the natural habitats of
elephant and to control anthropogenic activities in the forest areas.
After formation of Elephant Response Teams in July 2015, 133 raids were stopped in different project areas of Chittagong
and Chittagong Hill Tracts till September 2016. Regular follow-up and coordination by the Bangladesh Forest Department
is indispensable to enhance capacity of this team and to ensure their effectiveness.
Human-Elephant Conflict Mitigation Measures: 27
Lessons from Bangladesh
Elephant Response Team
© IUCN /Zubair Hussni Fahad
Way Forward
Elephant in wild
© IUCN /Sultan Ahmed
The piloted mitigation measures
have shown improvement in
human-elephant conflict mitigation
in the selected elephant ranges
of south-eastern Bangladesh.
Combination of mitigation measures
may help in conflict minimisation
in the future. Based on acquired
knowledge from the field, the
following areas need substantial
focus for further improvement in
conflict mitigation.
Human-Elephant Conflict Mitigation Measures: 29
Lessons from Bangladesh
Elephant roaming in the forest
© IUCN /Sultan Ahmed
Recognising and strengthening Elephant Response
Teams
The involvement of the Elephant Response Team in conflict
minimisation showed better results. So these novice
Elephant Response Teams need further nursing and
support for the continuation of their effective performance.
Coordination with regular monitoring by Bangladesh Forest
Department is still required for the functioning of these
teams. Initiatives to engage the members of these teams
in social safety net and social forestry programmes need to
be taken as they are volunteering in conflict management.
Recognition of their effort by the Government will encourage
them to work for the community. More teams need to be
formed with proper training in other human-elephant conflict-
prone areas.
Monitoring, maintenance and replication of installed
measures
Installed technologies like, solar electric fencing, trip alarm
and watchtower are found to be effective tools for conflict
minimisation. For the maintenance of these measures,
formation of a community-managed fund is needed to bear
the cost of repair, especially after the warranty period of
electronic devices. Assistance from government or non-
government organizations is required in the formation of
the community-managed fund. Regular monitoring from
Bangladesh Forest Department is required for the better
management of these technologies. Replication of these
technologies in other human-elephant conflict-prone areas,
like in central-north of Bangladesh, can help in reducing
similar conflicts at larger scale.
30 Human-Elephant Conflict Mitigation Measures:
Lessons from Bangladesh
Training of Elephant Response Team
© IUCN /Zubair Hussni Fahad
Solar electric fencing technology
© IUCN /Rupon Barua
Scaling up of nature-based solutions
Maintenance and replication of nature-based initiatives, like plantation, salt lick
and bio-fencing are needed to be carried out by Bangladesh Forest Department
in collaboration with local communities and other appropriate stakeholders. In
designing future plantation programmes, the prerequisite is to consider those tree
species that are favourable for elephant as well as for other wildlife. Capacity building
of farmers on cultivation of non-preferred crops and protection of crop fields using
chilli rope will lead to reduce the number of conflict in conflict-prone areas. For
non-preferred crop cultivation, selection of appropriate crops and marketing of the
produces at competitive price are crucial to reduce economic losses and to keep
farmers’ interest alive. The Government needs to focus on replication of nature-
based solutions involving appropriate stakeholders of other human-elephant conflict-
prone areas.
Public awareness and capacity building
To improve the understanding of the stakeholders who are establishing
infrastructures in or around the forest areas and the people dependent on forest
resources, it is very crucial to engage them in awareness raising programmes on
wildlife conservation and its importance in maintaining ecosystems. In the human-
wildlife conflict-prone areas, the conflict mitigation opportunities is also a vital agenda
of such awareness campaigns, which may need to be followed by capacity building
initiatives.
Human-Elephant Conflict Mitigation Measures: 31
Lessons from Bangladesh
Non-preferred crop cultivation
© IUCN / Iqram Uddin Al Amran
Knowledge sharing with community
© IUCN /S M Rasel
Meeting with Co-management Committee
© IUCN /Md. Fazlay Arafat
© IUCN /Abu Huraira
Given the dynamic nature of human-wildlife conflict, continued research and investigations can build our
understanding of the changing nature of these conflicts and can help us to identify measures to minimise the
negative impacts of conflict on both human and wildlife. As this book has shown, technological innovation can
be a crucial part of minimizing human-elephant conflicts. It is very important first to test an innovation at a small
scale, to evaluate its impacts and challenges, and, based on these results, to spread it for wider benefits through
scaling up. While promoting innovations, we need to remember the fact that innovation is essentially a continuous
process. We need to modify or improve a system, a tool or a technology to respond to new challenges in new
times and reinvent accordingly.
International Union for Conservation of Nature
Bangladesh Country Office
House 16, Road 2/3, Banani
Dhaka 1213, Bangladesh
Tel: +8802 55040938, 55040939, 55040940
Fax: +8802 55040932
www.iucn.org/bangladesh
... Severe HECs have also occurred (Desai and Riddle 2015;Mishra et al. 2015;Senthilkumar 2016). Sumatran elephants are considered critically endangered by the IUCN, similar to elephants in Borneo, which are also close to extinction (Wahed et al. 2016). Furthermore, the population of Bornean elephants (Elephas maximus borneensis) was bottlenecked and separated from the mainland population at the end of the Pleistocene epoch, approximately 11,000-18,000 years ago (Sharmar et al. 2018;. ...
... The number of wild elephants in protected areas and the number of conservation areas where wild elephants live were assessed in Thailand while considering the forest groups and the level of severity of conflicts between humans and wild elephants by the DNP (2023) Consequently, Asian elephants have been classified as endangered since 1986 ). Some elephant populations will be categorized as critically endangered by the IUCN in 2023, such as elephants in Bangladesh (Wahed et al. 2016) and Sumatran elephants (Elephas maximus sumatranus) (Ardiantiono et al. 2021). Extinct populations of elephants include those in Java and much of their range in Western Asia, along with most of the population residing in China . ...
... This was due to the increasing tendency of wild elephants to roam outside protected agricultural and residential areas (Wettasin et al. 2022;. The alleviation of humanwildlife conflicts, especially involving large wild animals that could be dangerous and damaging (Mekonen 2020), presents a significant challenge for global wildlife conservation (Karanth et al. 2013;Madden and McQuinn 2014;Goswami et al. 2017; Van de Water and Matteson 2018) Wahed et al. (2016) addressed the importance of continuous research and investigation into the causes of conflicts between humans and wild elephants. Therefore, solutions can be formulated to address conflicts by understanding their evolving nature. ...
Article
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This study comprehensively reviewed various aspects of population status, distribution, conflict situations, and conservation strategies for managing human-elephant conflicts (HECs). The primary goal is to foster a clear understanding of the current status, issues, and problem-solving approaches to benefit elephant conservation and management. The key element in elephant conservation is the acceptance of the coexistence between humans and elephants in their respective areas. Managing overlapping areas between humans and elephants is crucial for conservation efforts. A major concern is that elephants venture outside protected areas, increasing risk to both human and elephant populations. Therefore, enhancing the efficiency of conflict management is of the utmost importance to the long-term survival of elephants. This study revealed that vital approaches for managing elephant populations in Thailand include designating conservation areas as the foundation for long-term elephant conservation. In addition, habitat management at the population level, implementing compensation schemes, establishing community-based monitoring groups in conflict areas, improving conflict management practices, and decentralizing decision-making processes in conservation efforts are critical. Other essential elements of successful conservation and management in Thailand include setting population targets for elephants in each conservation area, with the goal of effective management. This was supported by research, community collaboration, decentralization, and performance evaluation to gauge the success of implemented measures in reducing HECs by assessing the number of conflict incidents and fatalities for both humans and elephants. This suggests the need for a fundamental reform of the elephant conservation policy.
... An elephant watch tower, also known as a guard house, is a secure location for surveillance where a person can monitor elephant activities, and take appropriate precautions to prevent loss (Madzimure 2017). Elephant watch towers or guard houses are structures designed to provide elevated observation points for monitoring elephant movements and preventing HEC. ...
... Elephant watch towers or guard houses are structures designed to provide elevated observation points for monitoring elephant movements and preventing HEC. Elephant watch towers are constructed in tall trees around six to nine meters high near the forest boundary, using wood, bamboo, a plastic cover, and tin sheeting with an easily climbable ladder (Madzimure 2017;Nakandala et al. 2014). At night villagers use these to detect elephants from a distance (Madzimure 2017;Nakandala et al. 2014). ...
... Elephant watch towers are constructed in tall trees around six to nine meters high near the forest boundary, using wood, bamboo, a plastic cover, and tin sheeting with an easily climbable ladder (Madzimure 2017;Nakandala et al. 2014). At night villagers use these to detect elephants from a distance (Madzimure 2017;Nakandala et al. 2014). ...
Article
Full-text available
Human-elephant conflict (HEC) is a severe conservation, socio-economic and environmental issue of forests and ecosystems in elephant inhabiting countries, including Sri Lanka. Due to the rapid growth of human and elephant populations, both struggles to share limited land resources. The major causes and contexts of HEC in Sri Lanka include land use change, habitat loss due to human population growth, crop raiding behavior, problem elephants, and changes in agriculture practices. Since 2019, 125 people and 370 elephants have killed annually on average due to the conflict. Also, Sri Lanka has recorded the highest annual elephant deaths and second-highest human deaths due to HEC. The human death rate has increased by approximately 42% over previous three decades. The Sri Lankan government provides compensation for death and disability of the human caused by elephants and for elephant-damaged houses or properties. The Sri Lankan elephant (Elephas maximus maximus) is an endangered subspecies. It’s home range is restricted to 50–150 km² and depends on the availability of food, water, and shelter of the habitat in which they live. Various management strategies have been developed by the government and villagers to prevent and mitigate HEC. Today, Sri Lankan elephants are protected under Sri Lankan law, with punishment by fines and jail terms. This article reviews the history, present status, and traditional conflict management of HEC in Sri Lanka. We suggest a satellite data fusion approach with GIS modeling to identify risk zones of HEC to develop further protective measures for humans and elephants.
... Therefore, the perception of the farmers was that crop raiding reduced inside the fences after the introduction of the fences in the Mambova wildlife corridor. Similar to Wahed et al. [55] findings, after the establishment of solar-electric fences in Bangladesh, elephants avoided human settlements. Respondents from unfenced gardens advised that they have seen the fences work effectively and they would appreciate being supported. ...
... Respondents with solar-electric poliwire fences advised that they had more crop damage from elephants before they were supported with an electric fence, and after the fence was installed, they no longer experienced any crop raids compared to their counterparts without electric fences. This outcome underscores the effectiveness of well-managed functional solar-electric fences [55]. However, with the changing behaviours of elephants, there is a need to constantly innovate mitigation measures to reduce the risk of crop damage. ...
Article
Full-text available
Human-elephant conflict (HEC) poses a major challenge for communities living within large transboundary corridors, affecting livelihoods and personal safety. Elephant-restraining solar-electric poliwire fences were implemented as HEC mitigation from 2017 to 2022 for 17 mixed-produce multi-farmer gardens in Mambova farming community in southern Zambia. To assess the knowledge and perceptions of farmers towards elephants and the newly established solar-electric poliwire fences, we conducted 60 semi-structured interviews (22 females, 38 males) with farmers from both fenced and unfenced gardens. The study found that community perceptions varied, and elephants and hippos caused significant crop damage to unfenced vegetable gardens, particularly during the dry season (95-96.3% of incidents occurring between July and November). Farmers reported elephants mainly damaged their gardens at night (21:00-03:00 h.), affecting crops like maize (Zea mays) and rape plants (Brassica napus). Most respondents (96.7%) found the solar-electric poliwire fence more effective in preventing crop damage than traditional mitigation measures, such as drumming and guarding. While some farmers were uncomfortable with elephants in their area (50%), others valued their presence for tourism and education (47%). A holistic approach, combining education, awareness campaigns, and conservation initiatives, is needed to manage HEC effectively. Understanding farmer perspectives and local knowledge about elephant behaviour and migration is vital for sustainable coexistence of humans with elephants.
... Killing of problem elephants • Identified problem individuals known to cause frequent HEC incidents may be killed, aiming to eliminate the problem from the area [75] • Degrade the genetic diversity of a population and impractical depending on the scale of HEC [108] • Using lethal methods to resolve HEC is controversial and considered ethically unacceptable in most contexts [108,111] 3. Early warning systems i. Traditional early warning systems e.g., watch huts and iron watch towers [76,82,112,113] • Places from where people can monitor elephants and alert farmers and villages to scare and chase elephants away and prevent crop damage ...
... ii. Improving habitat quality inside protected areas [55,82,131,132] • Increasing carrying capacity inside protected areas by creating and maintaining salt licks, managing water sources, planting fodder species, maintaining grassland areas and removing invasive species etc. to attract elephants, thereby managing their distribution • Increased densities of elephants resulting from improved habitat quality may not be sustainable due to overutilisation [133] • Selectively bred cultivated crops are also known to be more palatable and attractive for elephants regardless of the availability of other food [134] • Require regular monitoring and maintenance of salt licks and water holes as well as plants until they are established [81] Exclusion of elephants from conflict areas or restricting elephants to protected areas aims to keep elephants away from humans and their interests and is ostensibly intended to avoid the need for the direct killing of elephants in accordance with cultural and societal expectations. Exclusion is often achieved by aversive conditioning where animals learn to associate a particular behaviour with an unpleasant stimuli, and hence cease or modify that behaviour [135][136][137]. ...
Article
Full-text available
Animal-borne aversive geofencing devices (AGDs, or satellite-linked shock collars) are commercially available and used on livestock to restrict their movement within a virtual boundary. This technology has potential application as a human-wildlife conflict mitigation tool, where problem animals might be conditioned to avoid human-dominated habitats by associating an audio warning with a subsequent electric shock, which is delivered if the audio warning is ignored. Ensuring that high standards of animal welfare are maintained when implementing such tools is important for acquiring manager and community acceptance of such approaches. We conducted two pilot experiments with eight captive Asian elephants using mild electric shocks from a modified dogtraining collar fitted around the neck, as part of an ongoing effort to develop AGDs suitable for mitigating human-elephant conflict. As part of these experiments, we assessed elephants' behavioural and physiological stress before, during and after our experiments. During the experiments elephants wore collars up to nine consecutive days and received a small number of electric shocks on 1–3 consecutive days. Bootstrapped principal component analysis showed that daily activity budgets of individual elephants on experiment days were not different to the pre-experiment days. Generalised linear mixed-effect model (GLMM) showed that anxiety/stress behaviours increased on the first day of acclimatising to the collar and on testing days (i.e. days they received shocks) of the first experiment, but not during the second experiment relative to pre-experiment days. Analysis of faecal cortisol metabolite (FCM) concentrations using GLMM showed that FCM concentrations were higher in samples collected ~24 hrs and ~48 hrs after testing days compared to baseline levels as expected given the lag time for excretion of cortisol metabolites. These elevated anxiety/stress behaviours and FCM concentrations returned to baseline levels shortly after the experiment. Therefore, we conclude that AGDs did not produce lasting behavioural or physiological stress effects in elephants during this short term study but recommend further studies with a larger sample of elephants to confirm the transferability of these findings.
... Killing of problem elephants • Identified problem individuals known to cause frequent HEC incidents may be killed, aiming to eliminate the problem from the area [75] • Degrade the genetic diversity of a population and impractical depending on the scale of HEC [108] • Using lethal methods to resolve HEC is controversial and considered ethically unacceptable in most contexts [108,111] 3. Early warning systems i. Traditional early warning systems e.g., watch huts and iron watch towers [76,82,112,113] • Places from where people can monitor elephants and alert farmers and villages to scare and chase elephants away and prevent crop damage ...
... ii. Improving habitat quality inside protected areas [55,82,131,132] • Increasing carrying capacity inside protected areas by creating and maintaining salt licks, managing water sources, planting fodder species, maintaining grassland areas and removing invasive species etc. to attract elephants, thereby managing their distribution • Increased densities of elephants resulting from improved habitat quality may not be sustainable due to overutilisation [133] • Selectively bred cultivated crops are also known to be more palatable and attractive for elephants regardless of the availability of other food [134] • Require regular monitoring and maintenance of salt licks and water holes as well as plants until they are established [81] Exclusion of elephants from conflict areas or restricting elephants to protected areas aims to keep elephants away from humans and their interests and is ostensibly intended to avoid the need for the direct killing of elephants in accordance with cultural and societal expectations. Exclusion is often achieved by aversive conditioning where animals learn to associate a particular behaviour with an unpleasant stimuli, and hence cease or modify that behaviour [135][136][137]. ...
Article
Full-text available
Asian elephants are a principal cause of human-wildlife conflict. This results in the death/injury of elephants and humans and large-scale crop and property damage. Most current human-elephant conflict (HEC) mitigation tools lack the flexibility to accommodate the ecological needs of elephants and are ineffective at reducing HEC in the long-term. Here we review common HEC mitigation tools used in Asia and the potential of Aversive Geofencing Devices (AGDs) to manage problem elephants. AGDs can be configured to monitor animal movements in real-time and deliver auditory warnings followed by electric stimuli whenever animals attempt to move across user-specified virtual boundaries. Thus, AGDs are expected to condition elephants to avoid receiving shocks and keep them away from virtually fenced areas, while providing alternative routes that can be modified if required. Studies conducted using AGDs with other species provide an overview of their potential in conditioning wild animals. We recommend that the efficacy and welfare impact of AGDs be evaluated using captive elephants along with public perception of using AGDs on elephants as a means of addressing the inherent deficiencies of common HEC mitigation tools. If elephants could be successfully conditioned to avoid virtual fences, then AGDs could resolve many HEC incidents throughout Asia.
... A temporary remedy can be implemented by an active elephant response team, watchtower guarding, and paying compensation to victims. Additionally, crop guarding, physical barriers, and deterrents, as well as buffer crops, can be a temporary remedy to dissolve the negative and retaliatory attitudes toward elephants (Choudhury et al., 2008;Dixon et al., 2009;Ogra, 2009;Jadhav and Barua, 2012;Wahed et al., 2016). Relocating Rohingya refugees to a suitable place outside the forest, relocating and rehabilitating illegal forest settlers, and building awareness among forest-adjacent villagers involved in forest-damaging activities can be permanent solutions. ...
Article
Full-text available
Humans' and elephants' conflict is considered a common phenomenon in Bangladesh due to extreme anthropogenic interferences on elephant habitats. Concurrently, the landless people were encouraged to encroach on forest land due to their financial hardship and poor and weak forest management systems. We conducted our research work through frequent field visits, site-oriented positioned research correspondents, and an adopted semistructured questionnaire. We recorded a total of 903 conflict-related cases between humans and elephants, including crop raids (N = 337), house raids (N = 200), homestead garden raids (N = 263), and accidental attacks (N = 103), across sites, during August 2018 to July 2019, in Teknaf Wildlife Sanctuary (TWS). Elephant attack rates varied significantly between traditional forest dwellers (N = 179), illegal settlers (N = 370), villagers nearest forest (N = 212), Rohingya refugees (N = 53), and traditional forest different tribes (N = 89). It also varied along a space gradient, including inside forests (N = 423), buffer zones (N = 297), and outside forest villages (N = 183). The number of conflicts possessed by elephants varied discriminately and was unparalleled among different professions such as cattle ranchers (N = 104), gardeners (N = 112), paddy cultivators (N = 236), vegetable growers (N = 158), betel-leaf growers (N = 163), and forest resources collectors (N = 130). Most conflicts between humans and elephants occurred significantly during the night (N = 592), many during the morning (N = 154), evening (N = 138), and much less during midday (N = 19). The conflict intensity was also higher on the east coast (N = 552) than on the west coast (N = 351). The seasonal variation, including summer (N = 367), monsoon (N = 274), and winter (N = 262), was also significant. The elephant herd size was also an important factor triggering the conflict in TWS. We conclude that conflict intensity between humans and elephants is driven by settlers' location, forest gradient, the profession of forest-dependent people, their household size and income level, attack time, and season. KEYWORDS forest intruder, season, elephant herd, crop raid, house raid, homestead garden raid, accidental attack, human-elephant conflict Frontiers in Conservation Science
... Positive reinforcement is always preferred over punishment-based training of animals. This may be accomplished alongside AGDs, by increasing attraction to areas outside human habitats through habitat enrichment and improving connectivity of elephant habitats (Bakri et al., 2019;Menon and Tiwari, 2017;Wahed et al., 2016). Compared to elimination, translocation and domestication of elephants (Desai and Riddle, 2015;Fernando et al., 2015;Lahdenperä et al., 2018), AGDs may still be a more ethically acceptable non-lethal HEC mitigation method. ...
Article
Aversive Geofencing Devices (AGDs) are designed to emit audible warning signals followed by electric shocks when animals reach virtual fences (VFs) with the intent that animals will learn to turn away at audio warnings and thereby avoid receiving shocks. AGDs are a potentially useful tool for mitigating human-elephant conflict, but a greater understanding of captive elephant responses to AGDs is required before they might be confidently used on wild elephants. We conducted experiments with eight, female captive Asian elephants using a modified dog-training collar to deliver mild electric shocks (4 kV) of varying strength (pulse frequencies) to determine the ideal location on the neck to deliver the stimuli and the optimum strength of the shock required to generate desired aversive responses. Ten shocks (<1 s duration) of different strengths were delivered during a 10 min session (i.e., one shock per minute) at two positions on one side of the elephant’s neck. Results indicated that elephants were more likely to display desirable aversive behaviours at the upper position tested on the neck (odds ratio=0.47, 95% CI 0.25–0.87, P = 0.018) and at higher stimuli strengths (odds ratio=1.03, 95% CI 1.01–1.04, P ≤ 0.001). A conditioning experiment was then conducted several months later with five of the same elephants. These were individually trained to walk along a ~100 m path to a food reward on three consecutive days, wearing a dummy collar. On the next three days and on one other day few months later, the elephants were fitted with a similar shock collar (positioned at the upper neck location, and with the highest strength tested earlier) to determine if the AGD could prevent the elephants from accessing the food reward. Three VFs were established at ~30 m, ~50 m and ~60 m points along the path. As the elephant approached the food, a mild audio warning, a more aggressive audio warning, and an electric shock was administered at the first, second and third VFs respectively. Warnings and shocks were not delivered if elephants heeded earlier warnings. A maximum of five such trials were attempted. The VFs successfully kept elephants from reaching the food 77.8% of the time, with elephants responding to the audio warnings and avoiding electric stimulation 47.2% of the trials. These findings suggest that AGDs are a promising method to manage elephant movement, but further research is needed to develop a reliable approach for wild elephants.
... The needs of the growing human population, such as land use for human habitations and cultivation, have been influencing many species in close proximity to human habitats over the past few decades (Khan 2015). In Bangladesh, wildlife research has mainly emphasized megafauna such as tigers (Azad et al. 2005;Inskip et al. 2013Inskip et al. , 2016Reza et al. 2002), elephants (Palash et al. 2018;Sarker and Roskaft 2010;Wahed et al. 2016), and langurs (Green 1980;Jaman 2015;Khatun et al. 2012Khatun et al. , 2013. Research on the herpetofauna is still inadequate in Bangladesh and this has led to controversy among researchers regarding the exact number of species . ...
Article
Full-text available
Species diversity is an important parameter for monitoring ecology that can accelerate conservation planning. A study on the diversity, composition, and distribution of the herpetofauna in four districts of northwestern Bangladesh was conducted through direct field observations and plot counting during day and night from April 2017 to March 2018. A total of 33 species of herpetofauna were recorded, representing 20 reptiles and 13 amphibians, and the estimated species richness was 37. The highest number of species (22) was found in both Kornai (Thakurgaon) and Mollapara (Nilphamari), while the lowest (10) was in Nolabari (Nilphamari) and Koyagolahat (Nilphamari). The highest number of amphibian species (11) was recorded in Singra forest and Kornai, while Mollapara harbored the most reptilian species (12). Based on the Shannon-Wiener index of diversity, the highest diversity was in Kornai (H' = 2.562) while the lowest was in Singra forest (H' = 1.304). The Jaccard similarity index varied from 0.33 to 0.71, indicating the variations of species compositions among different sites. Among the 2,421 herpetofauanal individuals recorded, Common Toad, Duttaphrynus melanostictus (n = 639) represented the highest number among the amphibians and Yellow-green House Gecko, Hemidactylus flaviviridis (n = 130) represented the highest number among reptiles. The baseline data on herpetofaunal diversity reported here will help the scientific community and policymakers to effectively accelerate the conservation plans for this region.
... Between 2003 to 2016, a total of 227 people and 63 elephants was killed in the conflicts; while 24 people and four elephants were killed in 2016 alone ( IUCN Bangladesh 2016).To reduce the number of human vs. elephant conflict occurrences in the centralnorth and south-east conflict-prone areas of Bangladesh, Bangladesh Forest Department (BFD) and IUCN (International Union for Conservation of Nature) has been engaged the local communities in the protection and conservation of wild E. maximus. They have formalised 'Elephant Response Team (ERT)' and introduced a range of conflict management techniques including cultivation of nonpreferred crops of farmers, salt lick establishment, bio-fencing by rattan plant, plantation of elephant fodder and shade tree species, solar electric fencing, chilli rope, watchtower, and setting up trip alarms as early warning system, etc. at the grass roots level (Wahed et al. 2016). These measures have demonstrated improvement in human-elephant conflict mitigation in the selected regions of Bangladesh. ...
Article
Full-text available
About 930,000 Rohingya people were migrated in the Cox's Bazar district of Bangladesh following the ethnic cleansing violence in the Rakhine State of Myanmar. They built their camps by clearing the natural forests and social forestry plantations which was one of the important natural habitat and corridor of critically endangered wild Asian elephant (Elephas maximus) in Bangladesh. The Rohingya people extensively collected timber and fuelwood for construction and cooking from the forests and destroyed nearly 2,000 hectares of forest land. As a result, in search of food and route for natural movement, E. maximus entered into the camps, destroyed the settlements and a severe human-elephant conflicts arose resulted in 13 refugees were killed and nearly 50 people were injured. Studies revealed that there are 48 E. maximus is roaming around the camps, and all most all the incidents occurred during the dawn time where male and children were the main victims. Government, aid agencies and NGOs are operating in the field to take on the state of affairs. They commenced to enhance consciousness, setting up 56 watchtowers and 30 volunteer elephant response teams to warn residents when elephants enter the camp. Reduction in demand of fuelwood through supplementing the alternative fuel, reforestation with native and fruit-bearing tree species, agroforestry practices, plantation of elephant preferred fodder species, ensure safe trans-boundary corridors, and non-forestry income-generating activities can reduce and mitigate the Rohingya and. E. maximus conflicts.
Article
Full-text available
Physical barriers, like solar fences, elephant-proof trenches, stone, or rubble walls, are installed as conflict mitigation interventions in India’s major Asian elephant ( Elephas maximus ) ranges. However, installations lacking a priori scientific assessment of site specificity for reducing elephant incursion in the human settlements often fail in the intended goals of the resource-intensive management interventions. Since humans are central to conflict issues, research focusing on social aspects is essential for devising solutions. Despite the use of barriers in the Golaghat district in Assam, human–elephant conflict (HEC) cases are increasing, which offers an opportunity to evaluate their efficacy. Optimized hotspot analysis of the historic HEC records from 2010 to 2019 was done to check the spatial extent of the conflict and its dispersion in the district. We also assessed the efficiency of a 4.2-km long solar fence and a 2-km long elephant-proof trench through generalized linear modeling. We evaluated the encounter rates of elephant signs and other site covariates at the barrier and non-barrier sites. Multinomial logistic regression was applied to assess the perception of local people on the barriers and overall HEC in their areas based on their willingness to pay (WTP) for maintenance of the barriers. The highest cases occurred between 2016 and 2017, making up 25% of the total conflict cases. It was noticed that the extent of these hotspots was concentrated, and there was no dispersion of the conflict to other areas. Furthermore, a significant difference in the encounter rates of elephant signs between barriers and no barrier sites was observed. Solar fenced areas showed relatively lower encounter rates than areas with the trench, suggesting better efficiency of solar fencing than trench in the landscape. In addition, only five out of seven explanatory variables, viz. , the persistence of HEC cases, amount of ex-gratia compensation, time taken in getting compensation, change in elephant behavior (incursion), and crop-raiding frequency significantly explained people’s perception of the barrier and non-barrier sites. According to local people, physical barriers are essential in managing HEC; hence, installing and maintaining solar fences in the high conflict hotspots is crucial for this landscape.
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