Abstract of poster presented at the
International Tropical Ecology Congress, 2007 at Dehradun (2-5
December)
Tribals and large mammals: Survey of mammalian fauna and local
attitudes towards wildlife in non protected areas in the vicinity
of Balpakram National Park, Meghalaya
- Anirban Datta
Roy, Nimesh Ved (Samrakshan Trust)
Keywords
: mammal survey, Meghalaya, conflict,
Theme
- Biodiversity: amount, patterns, uses, conservation, and
participatory research.
This poster
presents the findings of a nine month questionnaire survey
conducted in the Garo hills region of Meghalaya state in north
east India. The survey collected information on large mammal
presence in the landscape, threats to them and sources
of human-animal conflict by tapping the knowledge base of
the local Garo tribe.
The north-east
Indian state of Meghalaya, situated in the Indo Malayan
biodiversity hotspot is home to an enormous diversity of flora
and fauna. Within Meghalaya, the Garo hills region is especially
biodiverse, but has been poorly documented over the years.
Samrakshan Trust has identified the Baghmara Balpakram Community
Conservation Landscape (~300 sq.km.) as an area of high priority
and initiated a long term community conservation intervention. The
landscape is bounded by Bangladesh to its south, the Balpakram NP
to its north and east and the Simsang river to its west. Any
community conservation initiative needs to understand local
attitudes and their relationship with wildlife to form an
effective strategy to deal with the challenges.
We thus conducted
a survey of mammalian fauna and local people’s attitudes towards
wildlife. This was done with two major objectives:
-
the establishment of a comprehensive information
base for future conservation efforts as well as recognition of the
current wildlife values in the region
-
to understand the attitudes of local people towards
presence of large mammals in terms of hunting and the nature and
magnitude of human-animal conflict in the landscape.
Questionnaire
surveys were conducted in all 33 akings (clan kingdom) of the
landscape with a total of 334 respondents over a period of nine
months from May 2005 to January 2006. The respondents comprised of
farmers, hunters, government servants and others. The
questionnaires attempted to document local knowledge on 56 species
of large mammal (> 1 kg) presence, fluctuations in relative
densities and degree and nature of conflict between local people
and large mammals. The initial list of mammals was prepared
through discussions with elders and hunters in the Garo hills.
Of the 56 species,
55 species were reported to be have been sighted, the Malayan Sun
Bear being the only animal which was never sighted. Rhesus
macaque, Wild pig and Indian porcupine were the most common
mammals sighted. They were also mentioned as species whose numbers
had increased the most within the last five years. Within the
respondents, professional hunters mentioned the names of the
Capped langur and Barking deer as the most common large mammals in
addition to the above three. Sambar, Water buffalo and the
Himalayan black bear numbers were perceived to have decreased in
the last five years. The biggest reason for this decline was
attributed by respondents to increase in hunting activities.
34% of the
respondents named the wild pig as mammal causing most damage to
crops, followed by the Asian elephant (31%) and the Indian
porcupine (9%). Jungle cat (26%) and Leopard cat (25%) caused the
most damage to livestock (including poultry).
Hunting and
trapping were mainly for domestic consumption (29 akings) while
commercial hunting was reported in a few cases (4 akings).
Elephant, Sambar, Water buffalo, Barking deer and Wild pig were
the animals that were hunted for meat.
The impact of
hunting and trapping activities in tropical ecosystems has largely
been overshadowed by the stress on habitat loss and fragmentation.
This study provides an indication of the dangers of overlooking
the long term effects of large mammal removal. Local knowledge
itself recognizes hunting as the primary factor in the decrease of
certain species. The increase in commensal species such as rhesus
macaques also indicates the gradual habitat degradation and
land-use change. Although commercial hunting is still restricted
to only a few akings, it is disturbing to note its presence in a
landscape where hunting for domestic consumption has already made
considerable impact. Additional pressure in the form of commercial
hunting, especially of large mammals like Asian elephants is a
serious threat.
Abstract of paper
presented at the International Tropical Ecology Congress, 2007 at
Dehradun (2-5 December)
Participatory elephant monitoring in south Garo hills : efficacy
and utility in a human-animal conflict scenario
-
Anirban Datta Roy,
Nimesh Ved, A Christy Williams
Keywords
: elephant, Meghalaya, Human-elephant conflict, participatory
wildlife monitoring
Theme - Biodiversity: amount, patterns, uses,
conservation, and participatory research.
We attempted to
evaluate the efficacy of community based elephant monitoring to
understand the ranging and habitat utilization patterns of free
ranging Asian elephants within a mosaic of forests of variable
legal status (ranging from National Parks to community forests)
and paddy as well as slash-and-burn shifting cultivation.
The northeast
Indian state of Meghalaya is situated in the Indo Malayan
biodiversity hotspot and is home to one of the largest extant
populations of Asian elephants. The south Garo hills region in
Meghalaya supports the majority of that population and forms an
important part of the Garo Hills Elephant Reserve. In recent
decades, this population has come into frequent conflict with the
local inhabitants, raiding crops and resulting in mortalities on
both sides. The promotion of monocultures, decreasing jhum cycles
and declining forest area has only exacerbated the conflict.
Samrakshan Trust
has identified the Baghmara Balpakram landscape (~300 sq. km.)
lying between the Balpakram NP and Simsang river as an area of
high conservation priority and has been involved in a long term
community conservation intervention to maintain habitat integrity,
with the Asian elephant as a flagship species. To develop a
greater understanding of the role of elephants in a landscape, it
is essential to have reliable information on their movement
patterns and utilization of the various available habitats,
including crop fields. Such information on free ranging elephant
herds are difficult to obtain in the absence of radio collared
individuals. We modified an existing model of participatory
elephant monitoring by trained informants in villages for African
elephants (Hoare, 1999) to monitor elephant presence in villages
and adjoining crop fields.
Reliable local
informants were trained in collecting and recording data on
elephant presence in their respective akings (clan villages). This
information was periodically collected by our personnel and
locations identified with the help of the informant with a Global
Positioning System. This information was then fed into the
computer and mapped. Information collected by the informants
included the following :
-
Location
-
Date and time of
elephant visit
-
Approximate
group size (herd or solitary)
-
Damage caused
(if any)
The initial phase
of the work included information from six akings. This formed a
small portion of the 33 akings in the landscape, but local
knowledge indicated that these were the most affected by
human-elephant conflict.
A total of 201
visits were recorded in six akings for the duration between June
2005 and July 2006. Solitary elephants accounted for 100 visits.
The visits were found to peak during the two main harvesting
periods in the Garo hills indicating a definite seasonality
pattern in the visits. This coincided with the two major crop
availability periods of November-December (wet paddy) and
August-September (jhum rice, maize, millets). Information from
individual akings also seemed to indicate that some akings were
particularly prone to visits by solitary animals indicating the
complexity in the dynamics of elephant ranging patterns within the
landscape.
We found
participatory elephant monitoring to be useful in providing basic
information on elephant presence in villages and crop fields. It
can also provide crude estimates of changes in group size across
time. It however, has many limitations and cannot be utilized for
understanding movement patterns of elephants across the landscape
as most observations are restricted to villages and crop fields.
Identification of individual elephants or their herds is usually
not possible as most elephant visits are at night. Variations in
interest levels of individual informants may also influence the
quality and utility of the data. Nevertheless, it can be a useful
tool to collect basic data on elephant presence in tropical
ecosystems where traditional line transect methods are restricted
by considerations of terrain, manpower and resources.