Journal of
Threatened Taxa | www.threatenedtaxa.org | 26 June 2018 | 10(7):
11844–11849
Assessment on the impacts of human-tiger conflict and community-based
conservation in Bandhavgarh Tiger Reserve, Madhya
Pradesh, India
Sandeep Chouksey ¹& Somesh Singh ²
1 School of Forestry and Environment - Sam Higginbottam University of Agriculture, Technology and
Sciences, Naini, Allahabad, Uttar Pradesh 211007,
India
² School of Wildlife Forensic and
Health Unit, College of Veterinary Science and Animal Husbandry, Nanaji Deshmukh Veterinary
Science University, Rewa, Madhya Pradesh 486001,
India
1Present address: Behind Tilak College, Rafi Ahmad KidwaiWard No. 18, Katni, Madhya Pradesh 483501, India
1 sandeepchouksey@hotmail.com (corresponding
author), 2 drsomeshsingh@rediffmail.com
Abstract: BandhavgarhTiger Reserve (BTR) is one of the famous tiger reserves in India, situated in Uamria District of Madhya Pradesh. Data on human-tiger conflict were
collected from the forest record during the period from 2001 to 2011 and a
questionnaire survey was conducted to know the level of human-tiger conflict. A
total of 27 human casualties were recorded, of which 40.75% were lethal (death)
and 59.25% were injuries. A total of 1,603 livestock killing were recorded by
tiger, of which consisting of 76.54% (1227) cattle (cow/ox), 22.52% (361)
buffaloes and 0.93% (15) goats. Illegal entry into the core and buffer area for
collection of minor forest produce, daily needs, and livestock grazing were
observed to be the major reasons behind the existing conflict. Poor livestock shelter was also found
responsible for mauling of cattle by tigers. The forest department had provided
adequate compensation for the losses, but most of the respondents were
unsatisfied due to assorted reasons. Poaching and retaliation killing of tiger
is also a serious issue in and around BTR. A total of four tiger poaching and one revenge killing case was recorded. Conflicts create a negative impact on people,even then majority of the respondents (83.89%) felt the necessity for tiger
conservation. Wildlife habitat
improvement, restocking of prey base by translocation of herbivores, fencing of
protected areas, controlled grazing and rangeland management, adequate compensation,
eco-development, promoting the use of toilets in surrounding villages for
safety, proper housing of livestock, and community-based conservation are some
options for control and management of human-tiger conflict.
Keywords: Bandhavgarh Tiger Reserve,
compensation, conflict, human casualties, livestock depredation, prey base,
restocking.
doi: http://doi.org/10.11609/jott.3015.10.7.11844-11849
Editor: Hari Balasubramanian, EcoAdvisors, Nova Scotia, Canada. Date of
publication: 26 June 2018 (online & print)
Manuscript details: Ms # 3015
| Received 31 October 2017 | Final received 24 March 2018 | Finally accepted 29
May 2018
Citation: Chouksey, S. & S. Singh (2018). Assessment on the
impacts of human-tiger conflict and community-based conservation in Bandhavgarh Tiger Reserve, Madhya Pradesh, India. Journal
of Threatened Taxa 10(7): 11844–11849; http://doi.org/10.11609/jott.3015.10.7.11844-11849
Copyright: © Chouksey & Singh 2018. Creative
Commons Attribution 4.0 International License. JoTTallows unrestricted use of this article in any medium, reproduction and
distribution by providing adequate credit to the authors and the source of
publication.
Funding: Self-funded.
Competing interests: The authors
declare no competing interests.
Author Details: Sandeep Chouksey is specialized
in Wildlife Science and currently working with the State Forest Research
Institute, Jabalpur. He has been associated in the past with Vulture Safe
Zone Project, BNHS and Elephant Corridor Project, Wildlife Trust of India. The
area of interest includes Wildlife Ecology, Management and conflict
studies. Dr. Somesh Singh is a Scientist in
Wildlife Health and Management and currently associated as Inchargeof the School of Wildlife Forensic and Health Unit at College of Veterinary
Science & Animal Husbandry, Rewa affiliated to Nanaji Deshmukh Veterinary
Science University, Jabalpur. Dr. Singh has been engaged in wildlife teaching/
research/ extension for the past 11 years. His area of interest includes
wildlife health, population management, rescue and rehabilitation.
Author Contribution: SC - Study design
and Data collection. Compilation of the results, analysis and
writing the manuscript. Making all the correspondences pertaining to the
manuscript. SS - Obtaining necessary permissions for the study, designing the
synopsis, data compilation, analysis and interpretation; and drafting and
finalizing the manuscript.
Acknowledgements: We
would like to acknowledge Forest Department of Madhya Pradesh for providing
necessary permission to carry out the research work. We would like to thank all
the colleague, teachers and friends of the School of Forestry and Environment,
SHUATS, Allahabad, UP for their support. Special thanks to
the family. The study would not have been possible without their support
and assistance.
INTRODUCTION
The rising human and livestock population around tiger reserves often
leads to increasing interfaces of humans and tigers in many places across their
range often results in human-tiger conflict situations. Tigers share common land with humans
from time immemorial. The explosion
in human population with the rising demand for agricultural and grazing land,
however, has left the tiger struggling for its very survival. Tigers have two ecological requirements
that place them in direct conflict with humans. First, they need large areas of forest
habitat (Sunquist 1981; Smith et al. 1987), and
second, they require abundant large prey (Smith et al. 1987). Tigers are severely affected by
anthropogenic factors because of their involvement in conflicts with humans
historically and even today. Tigers
mostly survive in small numbers in protected areas whichare isolated due to habitat fragmentation and disturbances.
As growing human population encroaches further into natural habitats,
people and tigers are increasingly competing over living space and food. Large
forest tracts have been degraded and fragmented for constructing rail routes
and roads. Fragmentation of forest,
expansion of agriculture fields, human settlement, mining and dams not only
destroy the habitat of wild tiger but also expose tiger to straying out to
people creating conflict with humans. The human activities tend to move out the tigers from such disturbed
forests in human settlement in search of food, water and shelter, causing
conflict situations.
Human-tiger conflict is frequently associated with attacks on humans and
livestock depredation. In the past
humans hunted tiger’s prey, leaving them with less and less to eat. If tigers do not have enough
prey they will instead hunt domestic livestock, which many local
communities depend on for livelihood. When tigers kill or predate upon humans,
they are treated as enemies and declared man-eater or man killer, and humans
often kill them. Human-killingis the ultimate expression of human–tiger conflict. It is a complex issue that needs to be
addressed to maintain support for tiger conservation in areas where human
killing is prevalent (Gurang et al. 2008). Conflict with people and their livestock
is a significant source of mortality for large carnivores and there is an
urgent need to characterize and develop measures to reduce these conflicts (Nowell & Jackson 1996; Woodroffe& Ginsberg 1998; Linnell 1999). Local people might take advantage of
depredations on domestic animals as an opportunity to poach a tiger when it
returns to feed on the carcass of depredated livestock (Johnson et al. 2006).
Bandhavgarh Tiger Reserve (BTR)
is one of the famous tiger reserves in India having a large number of tigers in
a small area. The human-tiger
conflict is on the rise in the area for the past few years and several cases of
tigers attacking humans have been recorded. Without a better understanding of
human-tiger conflict and a concerted effort to proactively address the problem,
future landscape-level tiger conservation and management efforts may be
jeopardized (Nyhus & Tilson2004).
Therefore the present study was planned to estimate the level of
existing human-tiger conflict, factors associated with conflict and impacts on
the community based conservation.
MATERIALS AND METHODS
Study Area
Bandhavgarh Tiger Reserve lies
in Zone 6E - Deccan Peninsular Central Highlands. It supports a corresponding platitude of
fauna. The reserve has earned
reputation worldwide for its high density of tigers. Located between the Vindhya and the
eastern flanks of Satpura hill ranges. The reserve falls mostly in Umaria District and a chunk of 19.26km2 in Katni District of Madhya Pradesh (Fig. 1). The area of the tiger reserve is
1161.471km2 including both the units of protected area and buffer
area. The reserve lies between
23.502–23.9520N & 80.784–81.1950E. The tiger reserve has six ranges namely Tala, Kalwah, Patour,Magdhi, Khitoli and Panpatha (Fig. 2) (Prakasam2005).
Methods
The present study was conducted between July 2011 to June 2012 in and
around Bandhavgarh Tiger Reserve. Secondary data on human casualties,
livestock depredation, poaching and compensation were collected from the forest
department archives. While primary
data was collected by direct observation and monitoring weremade by visiting conflict site/village time and date of conflict, activity of
victims and livestock-tiger interface were recorded. The evidence such as pugmark, scratch
marks, human mauling, livestock depredation, etc. wereobserved.
Questionnaire surveys were performed in peripheral villages. Twelve villages were randomly chosen for
survey from the six forest ranges (Tala, Kalwah, Patour, Magdhi, Khitoli and Panpatha) of BTR. Two villages from each range were chosen. The pre-testing of questionnaire was
also done. Total n=180 surveys were
carried out. Discussions were also
made with the village council and local residents to get the basic information
about existing conflict. Mean,
standard deviation, standard error and chi square test were calculated using MS
excel and statistical tool (R Studio).
RESULT AND DISCUSSION
Human casualties
A total of 27 human casualties were recorded, out of which 11 humans
were killed and 16 were injured by tigers from the year 2001
to 2011 (Fig. 3). No deaths
were recorded between the year 2001 to 2005. Out of 27 human casualties, 22 were male
and five were female. Maximum human injuries were recorded during the rainy
season (12) followed by summer (8) and winter (7). Among the six different forest ranges
maximum casualties were recorded in Panpatha range
(5), followed by Khitoli range (4), Patour range (3), Tala range (2)
and Kalwah range (2), with no injuries recorded in Magdhi range in any year.
Livestock depredation
in and around BTR
A total of 1,603 livestock killing cases were reported from the year
2001 to 2011 in BTR, out of which 1,227 (76.54%) were cattle (cow/ox), 361
(22.52%) were buffaloes and 15 (0.93%) were goats (Table 1; Fig. 4). The mean of livestock killing per year
by tiger attack was 204.5±29.29 for cattle; 60.17±6.44
for buffalo and 2.5±0.98 for goat. Maximum livestock killing were reported in KhitoliForest Range then Patour, Kalwah,Panpatha, Magdhi and Tala (x2=92.3, df=10,
P< 0.00001). Livestock grazing
in core and buffer area were found to be the main reasons behind livestock
depredation.
Attitudes of local
inhabitant towards conflict and conservational aspects
Discussions and surveys were conducted with affected people to know the
views about existing conflict and its alleviation. A total of 180 survey were conducted, of
which, 82 (45.55%) felt that a tiger attacks when humans approach to their
range, 61 (33.88%) believed that humans are easy prey for them, 22 (12.22%)
suggested that a tiger attacks during minor forest produce (MFPs) and timber
collection, 3 (1.67%) considered attacks while illegal hunting and 12 (6.68%) felt
livestock grazing in protected areas to be responsible for tiger attacks on
humans. Of 180, 83 (46.11%)
respondents lost their livestock due to attack of tiger, 34 (18.89%) by other
carnivores while 63 (35%) did not report such losses. Of 63 (35%) respondents believed
livestock grazing in tiger habitat being the major reason of livestock
depredation followed by 31 (17.22 %) noticed less number of natural prey in the
reserve, 51 (28.34%) considered livestock killings being an easy prey, 20
(11.11%) found these attacks by chance and 15 (8.33%) considered other reasons
behind the livestock depredation by tigers. Out of 180, 151 (83.89%) respondents
opined that tigers should be conserved, while 29 (16.11%) felt that such
conservation was not required. Among those who deny conservation measures, 16
(55.18%) stated that livestock killing are the reason for their denial, 8
(27.58%) considered the animal a threat to human life, while 5 (17.24%) stated
other reasons.
Out of 180, 111 (61.66%) believed the best conflict alleviation method
is to relocate the problematic tigers to other places, 38 (21.11%) suggested
creation of a physical barrier, 19 (10.56%) suggest possibility of using lethal
methods, 12 (6.67%) considered habitat improvement be the most feasible methods
to alleviate conflict.
Table 1. Human-wildlife conflict
incidents in Bandhavgarh Tiger Reserve between 2001 to 2011
|
2001 |
2002 |
2003 |
2004 |
2005 |
2006 |
2007 |
2008 |
2009 |
2010 |
2011 |
Total |
Human casualties |
|
|
|
|
|
|
|
|
|
|
|
|
Death |
0 |
0 |
0 |
0 |
0 |
2 |
1 |
2 |
2 |
1 |
3 |
11 |
Injury |
0 |
2 |
3 |
1 |
1 |
2 |
1 |
1 |
1 |
2 |
2 |
16 |
Total |
0 |
2 |
3 |
1 |
1 |
4 |
2 |
3 |
3 |
3 |
5 |
27 |
Livestock depredation |
|
|
|
|
|
|
|
|
|
|
|
|
Cattle (cow/ox) |
9 |
24 |
64 |
81 |
51 |
105 |
67 |
127 |
152 |
193 |
354 |
1227 |
Buffalo |
3 |
11 |
22 |
45 |
19 |
21 |
18 |
55 |
44 |
54 |
69 |
361 |
Goat |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
0 |
2 |
11 |
15 |
Total |
12 |
35 |
86 |
126 |
70 |
126 |
86 |
183 |
196 |
249 |
434 |
1603 |
DISCUSSION
Rising human population is creating biotic pressure in and around the Bandhavgarh Tiger Reserve that led to human mauling and
casualties. High rate of human
population growth and the successfully restored habitat in the community
forests of in BardiaNational Park, Nepal have accelerated the conflicts due to the dispersal of
tigers into these forests where they share these resources (Bhattarai2009). Human-tiger conflicts tend
to be more frequent near forest edges at the interface of human and tiger
activity, and in areas of high human density (Nyhus& Tilson 2004; Miquelleet al. 2005; Gurung et al. 2008; Nugraha& Sugardjito 2009). Lethal or serious attacks on people
often lead to retaliatory or defensive killings, which result in additional
injuries to people and/or carnivores (Sillero-Zubiriet al. 2006). In 2008 and 2009 two
tigresses were poisoned in Bandhavgarh Tiger Reserve
by villagers in an act of revenge for having allegedly killing of their cattle (Williams
& Seigal 2010).
The population of
livestock were reported more than 48,200 in villages around the reserve
including in the proposed Buffer area. Cattle rearing is a common occupation of the
people and they have large herds of unproductive and poor quality cattle which
graze in and around the tiger reserve. During summer the area becomes dry and thus water and fodder scarcity
was seen. As there is no practice
of stall feeding, villagers let loose their cattle into the forest. This huge cattle population exerted
tremendous biotic pressure on the resources of the Reserve. The study conducted in Bardia National Park reported the livestock grazing and
human intrusion into tiger habitat besides poor husbandry being the causes of
conflict. It is advocated to
improve the cattle breeds by adopting and implementing cross breeding
programmes (Bhattarai 2009). Thus, the villagers will be promoted to
focus on high yielding cattle instead of keeping large number of less
productive stock. The grazing should be controlled and strictly
prohibited. Grazing and rangeland
development practices would be a better way to reduce the grazing pressure and
entry of livestock in protected areas. The poor livestock shelter was also reported to be the reason behind
cattle lifting. Tiger often lift the animal in the night. The livestock
housings should be properly protected. Livestock insurance system can be adopted for a reasonable compensation
for livestock damages.
Though the collection
of MFP is restricted in core zones it becomes difficult to prevent the local
people from collecting MFP as it is one of the major
sources of their livelihood. People
often collect these items from the buffer zone and sometime also from the core
zone. Most of the attacks were
reported during MFP collection. Toilets need to be constructed in the villages to avoid the unnecessary
movement of peoples near forest areas for defecation.
Compensation is paid to villagers for human life loss and injury and
livestock predation by the forest department of Madhya Pradesh. State government of Madhya Pradesh
provides Indian Rupees (Rs.) 100,000 for human death
and Rs. 20,000 for injury. For the loss of livestock Rs. 10,000 to 5,000 is paid. Eco-development
committees were founded by the forest department in villages present in and
around BTR. Fencing is used
to reduce the intensity of human-tiger conflict but is expensive if done
properly (Image 2).
Wildlife habitat improvement has a significant role in mitigating
conflict. Tigers often come out of
the forest in search of food, water and shelter. Conservation education and
awareness of local people may be a useful tool in conflict mitigation
strategy. Conservation education
can change the attitude and behavior of people and
increases the tolerance of losses (Matarasso 2004).
References
Bhattarai, B.R. (2009). Human-Tiger (Panthera tigris tigris) conflict in Bardia National Park, Nepal. MSc Thesis, Ernst Moritz
Arndt University of Greifswald.
Gurang, B., J.L.D. Smith,
C. McDougal, J.B. Karki & A. Barlow (2008). Factors associated
with human-killing tiger in ChitwanNational Park, Nepal. Biological Conservation 141:
3069–3078.
Johnson, A., C. Vongkhamheng, M. Hedemark &
T. Saithongdam (2006). Effects of
human–carnivore conflict on Tiger (Panthera tigris) and prey populations in Lao PDR. Animal Conservation 9: 421–30.
Linnell, J.D. (1999). Large carnivores
that kill livestock: Do ‘‘problem individuals’’ really exist? Wildlife Society Bulletin 27: 698–705.
Matarasso, M. (2004). Targeting behaviour:
developing conservation education, communications and advocacy programmes with
the participation of local communities. WWF Indochina Programme, Hanoi.
Miquelle, D.G., I. Nikolaev, J.M. Goodrich, B. Litvinov, E.N. Smirnov & E.
Suvorov (2005). People and tigers in the Russian Far East: searching for the
‘coexistence recipe’, pp. 305–322. In: Woodroffe,
R., S. Thirgood & A. Rabinowitz(eds.). People and Wildlife, Conflict or Coexistence?Cambridge University Press, New York, USA.
Nowell, K. & P. Jackson
(eds.) (1996). Wild Cats: Status Survey and Conservation Action Plan. IUCN,
Gland, Switzerland.
Nugraha, R.T. & J. Sugardjito (2009). Assessment and
management options of human–tiger conflicts in Kerinci Seblat National Park, Sumatra, Indonesia. Mammal Study 34: 141–154.
Nyhus, P.J. & R. Tilson (2004). Characterizing
human–tiger conflict in Sumatra, Indonesia: implications for
conservation. Oryx 38: 68–74.
Prakasam, U. (2005). Management
Plan for Bandhavgarh Tiger Reserve, Umaria, Madhya Pradesh.
Sillero-Zubiri, C., Sukamar & A. Treves (2006). Living with
wildlife: the roots of conflict and the solutions, pp. 253–270. In:
Macdonald, D.W. & K. Service (eds.). Key Topics in
Conservation Biology. Blackwell Publishing,
Oxford, UK.
Smith, J.L.D., C.
McDougal & M.E. Sunquist (1987). Female
land tenure systems in tigers, pp. 97–109. In: Tilson,
R.L. & U.S. Seal (eds.). Tigers of the World: The Biology, Biopolitics, Management and Conservation of an Endangered
Species. Noyes Publications, Park Ridge, New Jersey.
Sunquist, M.E. (1981). The social
organization of Tigers (Panthera tigris) in Royal Chitwan National Park, Nepal. Smithsonian
Contributions to Zoology 336: 1–98.
Williams, A. &
S.R. Saigal (2010). Survey Report on Bandhavgarh National Park. http://www.dudhwalive.com/2010/12/brutal-autopsy-on-king-of-bandhavgarh.html
Woodroffe, R. & J.R.
Ginsberg (1998). Edge effects and the extinction of populations inside
protected areas. Science 280: 2126–2128.