A Comprehensive Study of Human-Elephant Conflict in the ... · investigated to get a broader...
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International Journal of Interdisciplinary Research in Science Society and Culture(IJIRSSC) Vol: 2, Issue:1, (June Issue), 2016 ISSN: (P) 2395-4345, (O) 2455-2909 © IJIRSSC
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A Comprehensive Study of Human-Elephant Conflict
in the Bordering Areas of the Three Reserve Forests
of Lakhimpur District, Assam.
Ranjan Kr. Borah1, Nabami Bhuyan
2
1Associate Professor, Deptt.of zoology, North Lakhimpur College.
2Head, Deptt. of Geography, Lakhimpur Girls’ College.
ABSTRACT : A study was carried out for assessment of human-elephant conflict in the fringe villages
around three major reserve forests of Lakhimpur District of Assam, viz, Dulung, Kakoi and Ranga
reserve forest from 2012 to 2015. The records whatsoever available on human elephant conflicts of
forest department since 2001 onwards were also took into consideration during analysis. Conflict was
intense in the months from October to January and was mostly concentrated along the forest boundary
areas (fringed villages), decreasing with distance from the reserve forests. Crop damage occurred
during two seasons; paddy (the major crop) suffered the most due to raiding. Crop maturity and
frequency of raiding were positively correlated. Single bull elephants were involved in conflicts more
frequently than female herds while herds were involved in majority of crop raiding cases. Of the single
elephants were makhnas and tuskers. The average herd size recorded was 56 individuals, with group
size ranging up to 9. Mitigation measures presently adopted involve traditional drive-away techniques
including making noise by shouting, drum beating, bursting fire crackers and firing gun shots into the
air, and using torch light, and throwing burning torches. Some of the Tea Gardens along the boundary
have constructed concrete walls. Kunkis have been used in some cases. Machans are used for guarding
the crops. Combinations of methods are most effective. Family herds were easily deflected, while single
bulls were difficult to ward off. Affected villagers have suggested methods like regular patrolling by the
Forest Department officials along the forest boundary, erection of a concrete wall and electric fencing
along the boundaries.
Keywords: Alternative crop, Bio-fence, Conflict, Dulung, Kakoi, and Ranga reserve forest.
____________________________________________________________________________
I. Introduction:
The Asian Elephant (Elephas maximus), the giant pachyderm is on of the top categorized
mammalian species that falls in the list of scheduled I species. It was originally found from the
Tigris Euphrates valley in West Asia to Northern China in East Asia. India is the single country
that has the largest surviving population of elephants. There are at least about 25,000 wild
elephants in the forests of India. The distribution of wild elephants in India can be described
under four regions- Northern, North-eastern, central & Southern India [1]. The second highest
population is 12,000 in Myanmar & Sri Lanka [2]. The North-eastern India houses high bio-
diversity that has become part of a global biodiversity hotspot .The estimated population of
elephants is about 11,000, one of the largest populations in the Indian subcontinent [3]. On the
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other hand only Assam is the abode of almost 20% of total elephant population of India. The
Himalayan foothills from northern west Bengal, to Arunachal Pradesh , through Assam
touching southern Bhutan, & Manas is the key conservation area in the north bank landscape,
along which one large population of about 4800-5800 elephants keep roaming .[4].
Almost 20% of total elephant populations of India are found in Assam out of which 35%
are spotted in Sonitpur & Lakhimpur district. Lakhimpur & Sonitpur districts bear 3 Elephant
Protected Areas out of a sum of 64 Elephant Protected Areas of India.
Therefore present distribution of this species is limited only to some tropical forest
areas of a few countries of Asia. Along with explosion of human population, deforestation and
shifting cultivation, fragmentation of its migratory route i.e. elephant corridor is also
influencing in the declination of the population.
Human-Elephant conflict refers to a range of direct & indirect negative interaction
between people and elephant which potentially harm both. The most exposed are crop damage
by elephant, injury & death to people and killing of the animal in turn
Human elephant conflict is a closely related problem of elephant conservation scenario.
With the decrease in forest cover, the conflict is becoming more serious by the day . Growing
human population, demands for cultivable lands & destruction of forest habitat for human
habitation all have resulted in serious human-elephant conflict in Assam [5].
Habitat loss is the single greatest threat to the survival of substantial numbers of wild
Asian elephant. The forest cover in NE India is disappearing at an alarming rate. More than
1000 km2 of forest are being destroyed annually. This has resulted in increasing incidence of
human elephant conflict to alarming an rate in Asian in the recent time [5].
The conflict problem is a cause for concern because it threatens to erode local support for
conservation in areas where human life & property are at high risk for destructions by wild
elephants.
Usually elephants do not confine to a particular area for a longtime. They tend to
migrate in a fixed route called the Elephant Corridor. They use this permanent path year after
year and sometimes generation after generation. These corridors always locate in deep forest
areas except for rare exceptions. But now these elephant corridors are in a great threat.
Fragmentation on the elephant corridor is now a huge problem, effect of which now results in
the modification of characters of the pachyderms.
II. Objectives of the Study: 1. The main objective of the proposed work aims to:
2. asses the present status of the corridors vis a vis elephant usage, land use pattern and biotic
interference
3. Identify the status of human-elephant conflict in and around the corridors.
4. Impact of human-elephant conflict on certain socio-economic aspects of the inhabitant, those
facing this problem.
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5. formulate action plan for the protection of the corridors and reduction of human-wildlife
conflict
III. Study Area:
The study area comprises the fringe area towards the southern side of the three
contiguous reserve forests in the Lakhimpur district of Assam viz. (a) Kakoi RF(b) Dulung RF
and(c) Ranga RF, which lies between 93o
54’27.38”E and 94o
15’58.23”E which are situated
to the northern most side of the district. The area mostly falls under the Himalayan foothills
region.
(a) Kakoi RF:- Covers an area of 4415.03 ha. Covering mostly riverrine and hilly terrain with
vegetation type ranging from riverrine grassland toT.R.F.
(b) Dulung RF:- Covers an area of 9900.03 ha. Covering mostly hilly terrain with vegetation
type ranging from deciduous toT.R.F.
(c) Ranga RF:- Covers an area of 8529.71 ha. Covering mostly riverrine and hilly terrain
with vegetation type ranging from riverrine grassland toT.R.F.
The villages selected for study are, Tarioni, padumani and Lalpani in Dulung R.F,Bokanallah,
Dirgha naharbari and kakoi Rajgarh in kakoi R.F and Kachajuli,Dhunaguri,Bhuyanpara and
Chensa Rajgarh in Ranga R.F.
Figure: 1. Lakhimpur District showing the location of reserve forests.
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Fig: 2- Map of Dulung Reserve Forest. Fig:3- Map of Kakoi Reserve Forest.
Fig:3- Map of Ranga Reserve Forest.
III.Methodology:
Every conflict incident was considered as a sampling unit. Villages affected by elephant
depredation were visited. On the basis of raiding, a total of 10 villages within 3 K.M. range
from the reserve boundary were identified. The information of these conflicts was collected by
interviewing the local people or the farmers using Rapid rural Appraisal approach (chambers-
1994). The questionnaire sought information on Location of raided crops, types of crops
cultivated, extent of different crops cultivated, month of cultivation, composition of raiding
herds, frequency of raiding, extent of damage to the crop, mitigation methods used to deter
elephants and attitudes and expectations of local people towards human –elephant conflict
situations. During analysis, available historic incidents from 1999 onwards were also
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investigated to get a broader picture of the nature of conflict [5].Details of such incidents were
obtained from the Divisional Forest Office, North Lakhimpur.
IV. Results and Discussion:
The intensity of conflict occurrence in the study area seems to be comparatively high in
contrast to other human elephant conflict areas of Assam. This is because the current paces of
disturbance factors like timber smuggling, grazing, and encroachment and over exploitation of
NTFP are causing serious crisis for the elephants in the area. During the period 2012 till 2015
there were more than 175 crop raiding cases, 56 household and other property damage cases
and 10 human death cases were reported. (Table 3). If the current pace of disturbance persists it
could cause serious crisis for elephants and humans in the near future. Some of The cases of
crop raiding, household and property damage of the previous years (2001 – 2006) were
collected from the forest department of Lakhimpur district. There may be some sort of biasness
in data maintenance regarding the Ex. Gratia claims. The cases of human deaths due to
elephants were well authenticated for use for better understanding of the status of human
elephant conflict situation in Lakhimpur district.
Patterns of Elephant Depredation:
1. Crop Annihilation
1. a. Distribution of crop raiding incidents:
Distribution of crop raiding incidents was not uniform, as few villages suffering
significantly more damage than the others. However, distance from the forest to the crop field
have some effect on crop raiding, as the fringe villages suffered more crop raiding incidents
than the rest. As the distance increases the conflict gradually decreases. Similar results were
obtained from the studies by Marak et.al[6], in Africa and Sukumar [1]in Assam. During their
study they observed the relationship of distance factor with crop raiding. The maximum
straying distance recorded in the study was 23 km. by a herd of 56 from Ranga RF to Bodati
Jamuguri in the year 2006.The general cases recorded is about 5 to 6 km. by the bull elephant.
Usually the herd restricts its area of raiding crops within 3 km. from the reserve forest. During
analysis 10 villages were identified that have crop raiding during 2212-2015. During this
period 4 villages near longer Ranga reserve forest suffered the highest occurrence of crop
damage. It was followed by Dirgha Naharani gaon near Kakoi reserve forest. The villages near
Dulung reserve forest are less affected in comparison to the others.
1.b. Raiding seasons & crop preferences
There are around 175 cases of crop raiding in the study period, which include raiding of
both field crops as well as backyard garden crops. The crop depredation mainly in case of
paddy, which is generally preferred by the elephants in this region, starts right from the
vegetative stage and continues till the crop gets maturity and reaches the harvesting stage.
However, the intensity of crop raiding attains the highest level as the crops get full maturity.
Generally the peak raiding moment arrives twice a year as the paddy harvesting time
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approaches, once in June-August (for Ahu paddy) and another in October-to December (for
Sali paddy). During the months from February to April, intensity of crop raiding remains very
low. Because, February is the post-harvesting month, so it remains no longer attractive to the
elephants as most of the crop fields are cleared up and they remain unplanted till April. In
April, sowing of Ahu paddy starts and till the month of May the paddy remains in the
vegetative stage, which is although raided but preferred comparatively less by the elephants.
Among the garden crops, damages to Banana, Coconut and Beetle nut trees which are normally
more destructed by elephants rather than being eaten cause more economic loss to the farmers
due to their high market value (Table-2).
Table-1 Crop damage
Area/R.F. Village Crop type Area of damage
Harmutty Kachajuli Paddy 2 bigha
Harmutty Dhunaguri Paddy 2.5bigha
North Lakhimpur Tariyoni Paddy 1 bigha
Harmutty Dhunaguri Paddy 3.10bigha
Harmutty Chensa rajgarh Cerals 0.54bigha
Harmutty Kachajuli Paddy 1.2bigha
Harmutty Bhuyanpara Vegetables .3bigha
North Lakhimpur Dirgha rajgarh Paddy 2.2bigha
Harmutty Bhuyanpara Banana .2bigha
Harmutty Bhuyanpara Banana .57bigha
Harmutty Kachajuli Paddy 4.2bigha
North Lakhimpur Padumani Ceral 1bigha
Harmutty Kachajuli Paddy 2.3bigha
North Lakhimpur Lalpani Paddy 1.6bigha
North Lakhimpur Lalpani Vegetable .9bigha
North Lakhimpur Tarioni Paddy 4 bigha
North Lakhimpur Lalpani Paddy 2 bigha
Harmutty Bhuyanpara Banana 1bigha
Harmutty Chesa Rajgarh Paddy 7bigha
Harmutty Dhunaguri Banana 1 bigha
North Lakhimpur Kakoi Rajgarh vegetables .7bigha
Source: Field Survey
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Table-2
List of different plants consumed/trampled/damaged by elephants in the villages around the reserve forests
of Lakhimpur district
Sl. No. Plants Parts consumed/
Trampled/Damaged
Season
1 Banana Whole plant Round the year
2 Jackfruit Fruit April-August
3 Pineapple Fruit, leaves June-July
4 Coconut Pulp Round the year
5 Sugarcane Entire plant Feb-March
6 Tapioca Leaves, root March-December
7 Pumpkin Fruits November- January
8 Summer squash Fruits August-September
9 Cabbage Entire plant October-February
10 Cauliflower Entire plant October-February
11 Tomato Entire plant/Trampled October-February
12 Squash Damaged April - October
13 Brinjal Damaged October-November
14 Potato Damaged November-December
15 Bamboo New shoots, leaves Round the year
16 Beetle nut Damaged Round the year
17 Jute (bitter variety) Entire plant/Trampled March-August
18 Gram (Kechari, Mug,
Green pea)
Trampled/Damaged November-February
19 Mustard Trampled/Damaged December-February
20 Chilli Trampled/Damaged October-November
21 Basmati (Paddy) Entire plant April-September
22 Ranjit (Paddy) Entire plant June-November
23 Moinaguri (Paddy) Entire plant June-November
24 Ahu (Paddy) Entire plant February-August
25 Sali (Paddy) Entire plant June-December
26 Chinese (Paddy) Entire plant March-June
27 Chinese boro (Paddy) Entire plant March-August
28 Bangla eri (Paddy) Entire plant March-November
29 Parimal (Paddy) Entire plant August-October
Source: Field Survey
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1. c. Raiding group size :
From the present study and the data available with Forest Department records we find out
the number of raiding group sizes in few instances. It has been found that the single animals
tend to raid crops significantly more number of times than the female led family herds. Singles
generally visit the villages and raid the crops on round the year basis, whereas the herds on
seasonal basis. The average herd size recorded was 56 with raiding group sizes ranging up to 9.
The single crop raiders are Makhnas (bull elephants).
2. Human injury and man slaughter by elephant:
Human injury and death by the raiding (rogue or disturbed) elephants is one of the very
crucial aspects of the human-elephant conflict. Although the annual number of human injury
and death cases at the hands of raiding elephants in Manas is comparatively less, there are
many incidents of frequent encounters between humans and elephants.
During 2012-2015 only ten death cases and 21other cases of human injury were reported
(table 3).Only the Makhnas were responsible for the cases of death and injury. The maximum
number of human death was reported during the year 2004 and the village under Harmutty
Range of Ranga Reserve Forest topped the list. Of the injury cases, 34% were major (fracture
of bone, head injury etc) and 66% minor (scratch, sprain etc.) . In a majority of the human
death/ injury cases the elephants responsible were either in the state of musth or injured..
However, there were some accidental encounters where humans and elephants were unaware
of each others presence due to obscurity at night.
Table-3
Human death due to man-elephant conflict.
Area/R.F. No of death M/F date time Name of the victim
Harmutty Range 1 M 16-04-2012 Arupjyoti borah
Harmutty Range 1 M 20-07-2012 Nagen Hazarika
Harmutty Range 1 M 06-11-2012 Jakaria Chandigiri
Harmutty Range 1 M 24-01-2013 Kolimai Das
Harmutty Range 1 M 25-04-2014 Indeswar Borah
Harmutty Range 1 M 26-04-2014 Tileswar Borah
Harmutty Range 1 M 09-05-2014 Magina Nag
North Lakhimpur Range 1 M 25-01-2014 Dilip Patir
North Lakhimpur Range 1 M 12-11-2015 Matiram kalamadi
Harmutty Range 1 F 23-11-2015 Shabitri Tamang
Source: Field Survey
3 . Household and property damage:
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Household and property damage by wild elephants is another aspect of human-elephant
conflict. The main cause behind majority of the house raiding cases was for stored paddy and
salt in the houses. However, there were some accidental cases also, where the elephants caused
damage to the household after being provoked by the villagers while trying to chase it off.
Damage to households and property occurred more or less through out the year with a
peak in winter season. This was found to coincide with the harvesting period of paddy. The
village Kachajuli and Bhuyanpara under Harmutty range of Ranga reserve forest reported the
highest number of house damage cases. It was followed by Tarioni and Lalpani, Dirgha
naharbari and Bokanallah of Dulung and Kakoi reserve forest. Maximum household and
property damage (70%) was caused by the makhnas, followed by herds (30%).
Table-4
Livestock damage
Area/R.F. Village/ G.P. Livestock Number Date Causes
Harmutty Bhuyanpara Cattle 1 10-05-2012 Breaking of cattle
yard by elephant
Harmutty Chensa Poultry 10 dead 16-11-2012 Complete destroy
of poultry house
Harmutty Kachajuli Piggery 2 21-11-2012 Kicking pig while
escaping from
human attack
North
Lakhimpur
Dirgha rajgarh Sericulture 1 bigha
completely
damaged
26-12-2014 Complete destroy
of one culture
room as well as
trees by elephant. Harmutty Kachajuli Cattle 2dead, 3
injured
10-06-2014 Destruction of
cattle yard.
Harmutty Kachajuli Poultry 15 10-06-2014 Complete destroy
of poultry house
North
Lakhimpur
Lalpani Cattle 2 10-11-2015 Knocking cattles
at paddy field
Harmutty Bhuyanpara Piggery 1 injured 15-12-2015 Kicking pig while
escaping from
human attack
Harmutty Chesa Rajgarh Cattle 1 21-12-2015 Knocking cattles
at paddy field
Source: Field Survey
Mitigation Measures:
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The methods used to ward off elephants in the fringes of the reserve forests include the
age old, traditional drive away techniques which include noise making activities like shouting,
drum beating, bursting fire crackers, firing gunshots into the air , using torch light, pelting
stones, and throwing burning fuel woods. Depending on the severity, Kunki (captive trained
elephants to drive away the raiders) operations are also provided by the forest department.
During the harvesting period, the farmers guard their crops every night from “tongis/machans
(temporary shelters built by the farmers during cropping seasons on the high trees) build near
the crop fields. Discussion with the villagers revealed that none of the active drive away
method is fully effective if used singly. Because, each single mitigation method may help a
little but would not, on its own, be sufficient to make much difference to the human elephant
conflict problem.[7] On the other hand, acting together, the whole “package of methods”
(synergism) may be more effective than the sum of its individual constituent parts. It probably
works because although problem elephants are very resourceful, if their intensions are hindered
or blocked in several different ways, most of them may give up trying. While family herds
could be deflected easily, the solitary bulls were always more difficult to ward off and required
lots of effort, time and man power as stated by the local farmers during the interview.
Views and Opinions of the local people
India has its own cultural heritage. The traditional, cultural and religious attitudes
towards wild animals make local people tolerant towards wild life, despite the damage to
crops, household and property damage .The general reverence towards plants and animals in
some Indian religions has often been reported to be the main reason for a positive attitude
towards wild life and nature reserves[8][9]. Though positive attitudes towards elephants still
persists among the fringe villagers [10], the majority, almost all (98%) of them expect more
intensive crop, human life and property saving initiatives from the forest department of Assam.
The families affected by human elephant conflict expressed their dis-satisfaction with the
current compensation process due to its lengthy and complicated procedure. It is also reported
that they are paid much less than the actual amount they claim and sometimes they do not even
get any response despite repeated follow-ups. During the survey when the villagers were asked
to recommend some possible effective measures against elephant depredation, the majority of
them suggested electric fencing (48%) along the park boundary, followed by concrete wall
(25%), Next to it, the majority of the respondents recommend regular patrolling (15%) by the
forest department officials along the park boundary areas and special joint patrolling with
JFMC during peak raiding period. A minor portion of the villagers also suggest simply drive
away (8%) and lighting the reserve boundary during night hours (7%) along with the other
recommendations.
Use of Elephant deterrent alternative cash crop as Bio-fence.
It is advisable to change the traditional cropping pattern by introducing some elephant
repellent alternative cash crops like lemon and chili. These were introduced in the fringe
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villages of Manas national Park on an experimental basis[4]. In the study area it is seen that
Tea cultivation along the boundaries of the reserve forest also act as barrier to the crop land.
Therefore it is advisable to shift to tea cultivation as an alternative to paddy cultivation. This
alternative cropping pattern is expected to compensate the annual crop loss, and at the same
time due to their deterrent effects also thought to act as a “Bio-fence” to check the elephant
depredation/movement into the villages.
V. Conclusion: The fate of the Asian Elephant is dwindling day by day. To ensure the future of this
giant, it is important to clearly understand the ecological processes that drive HEC, along side
the attitude, expectation and tolerance level of the local people living near by. As a long term
measure, restoration of already degraded habitats is of utmost necessity. Protection and proper
management planning should be immediately made to foster natural regeneration of forest.
Communities living within or near forest can be an essential component of forest conservation,
by actively engaging with forest management activities and defending their territories against
poachers and loggers. Involvement of the local community in minimizing elephant depredation
and managing the critical issues of HEC could be strong initiative in the fringe areas.
Improving the livelihood security, introduction of alternative living options and improved
agricultural practices will reduce the pressure for annual land expansion too, which should in
turn reduce the need for forest clearance. Eco-development initiatives need to be encouraged in
the fringe villages, along with a series of conservation education and awareness programmes.
The alternative elephant deterrent cash crop concept could be a promising move towards
minimizing the conflict. However it may take a couple of years as such activity is new for the
villagers. The enquiry processes that involve more than one government department and the
compensation process should be prompt for loss of life and property. This will help to get back
the lost faith of the local community to the forest department.
References :
[1] Sukumar .R. :Ecology of the Asian Elephant in Southern India. II. Feeding Habits and
Crop Raiding Patterns. Journal of Tropical Ecology, Vol. 6, No. 1 (Feb., 1990), pp. 33-
53
[2] Choudhury, A.U. (1991). Status of wild elephants in Cachar and N.C.Hills, Assam - a
preliminary investigation. J.Bombay Nat. Hist. Soc. 88(2): 215-221.
[3] Choudhury, A. (1999). Status and conservation of the Asian elephant Elephas maximus
in north-eastern India. Mammal Review 29(3): 141-173.
International Journal of Interdisciplinary Research in Science Society and Culture(IJIRSSC) Vol: 2, Issue:1, (June Issue), 2016 ISSN: (P) 2395-4345, (O) 2455-2909 © IJIRSSC
www.ijirssc.in Page 143
[4] Menon, V., Tiwari, S.K., Easa, P.S. and Sukumar, R. (2013) Elephant corridors of India
: An analysis. In : Right of Passage: Elephant Corridors of India. Menon, V., Tiwari,
S.K., Easa, P.S. and Sukumar, R. (eds). Pp 258-65.
[5] Talukdar, B. and Barman, R. (2003). Man - Elephant Conflict in Assam, India: Is There
a Solution? Gajah 22: 50-56
[6] Marak, T. T. C. (2012). Status, distribution and conservation of the Asian elephant
(Elephas maximus) in Meghalaya. Indian Forester 128(2): 155-160
[7] Choudhury, A.U. (1992). Trunk routes. WWF- Quarterly 3(1): 14.
[8] Gurung, S. and Lahiri Choudhury, D.K. (2000). Project Elephant-human conflict in Asia
state report on Meghalaya, India. Part-I. Asian Elephant Research and Conservation
Centre
[9] Gurung, S. and Lahiri Choudhury, D.K. (2001). Project: Elephant-human conflict in
Asia state report on Meghalaya, India,. Community development-block reports. Part-II.
Asian Elephant Research and Conservation Centre
[10] Williams, A. C. and Johnsingh, A. J. T. (2006). Threatened elephant corridors in Garo
Hills, north-east India. Gajah 16 : 61-68.