protection of wildlife outside protected … they are spread unequally in northern, southern,...
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PROTECTION OF WILDLIFE OUTSIDE PROTECTED AREAS
WITH REFERENCE TO DESERT DISTRICTS OF RAJASTHAN
UDAY SHANKAR ( IFS) 96
CONSERVATOR OF FOREST, RAJASTHAN EMAIL : [email protected]
Abstract : One of the issues that has been raised is the importance of conserving endangered species other than large mammals like the tiger. The government initiated a new Centrally Sponsored Scheme’ Assistance for the Development of National Parks and Sanctuaries' entitled Integrated Development of Wildlife Habitats to focus, among other things, on the need to ensure better protection of wildlife outside the protected areas and initiate recovery programmes for saving critically endangered species
To ensure better protection of the wildlife, and critically-endangered species and habitats in and outside protected areas, the centrally-sponsored scheme, 'Assistance for the Development of National Parks and Sanctuaries' has been modified during the 11th five-year plan period to address the new generation issues facing wildlife conservation.
The scheme has now been named as the 'Integrated Development of Wildlife Habitats,' and has been made operational by adding more components and activities and widening the scope of conservation interventions.
KEY WORDS : Outside protected areas, National wildlife action plan, integrated
development of wildlife habitats, man animal conflict.
INTRODUCTION
Inspite of numerous protected areas in India, the wildlife is facing many problems in
terms of survival by way of habitat loss, human invasion of inviolate spaces and
developmental related activities obstructing the natural corridors of migrating animals. In
India, there is no particular definition for a protected area; any area that is considered by the
central government or state government to be important for conservation is designated a
status under the Wild Life (Protection) Act, 1972 and is then legally considered a protected
area. Until 2002, the WLPA only had two main types of protected areas, National parks and
wildlife sanctuaries. An amendment to the Act in 2002 included two more categories -
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conservation reserves and community reserves. A further amendment in 2006 added another
category called the tiger reserve.
Wildlife is well protected within these Protected Areas (PAs) by the umbrella Wild
Life (Protection) Act, 1972 and the respective wildlife laws of the State governments. The
scheduled Species of wild fauna and flora also enjoy the protection even if they are outside
the PAs. The Environment (Protection) Act, 1986 and the Biodiversity Act, 2002 aid in
overall protection of the environment and conservation of biodiversity respectively. With all
these laws in hand, wildlife management is difficult even in PAs because of pressures of
grazing of livestock, encroachments, poaching, extraction of Non Timber Forest Produce
(NTFP), and religious gatherings by local people. Outside the PAs the situation is alarming,
since most of the wild populations like spotted deer, Chinkara, black buck, Indian hare, wild
boar venture out of forests are falling prey to local people or poachers. Leopard, tiger, sloth
bear, wolf, jackal, hyena etc. are also persecuted because people feel they have to kill them to
protect themselves. To protect the wildlife outside PAs, the Governments should undertake
measures which would be beneficial to wildlife and people.
MATERIALS AND METHODOLOGY USED
The issue of management of wildlife outside PAs is studied by understanding the
legal provisions related to wildlife in WPA, 1972 and the information gathering through
visiting the websites of Ministry of Environment and Forests, Rajasthan forest department,
referring to Scholarly articles relating to management of wildlife outside PAs. The
information received from the office of Chief Wildlife Warden, Rajasthan state is also
incorporated in the study. Besides, some case studies from various states regarding
community conservation with examples are also discussed in the paper. The views and
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opinions of various forest officers debating this issue in various forums have been also
incorporated.
PROTECTED AREA NETWORK: A NATIONAL PERSPECTIVE AND
BACKGROUNDER
As per present pattern in the country protected area can be categorized in following five types
according to the intensity and differential focus of management :
1. National park: Chapter IV Section 35 (1) of the WLPA
2. Wildlife sanctuary: Chapter IV Section 18 (1) of the WLPA
3. Conservation reserve: Section 36A (I) of the WLPA
4. Community reserve: Section 36C of the WLPA
5. Tiger reserve: Section 38V (4) of the WLPA
Apart from the protected areas mentioned in the WLPA, the Scheduled Tribes and Other
Forest-Dwellers (Recognition of Rights) Act, 2006 (FRA) provides for the creation of a
stricter category within existing protected areas, called critical wildlife habitat (CWH).
According to Section 2(b), Section 4 (2) (a-f) of the FRA, Critical wildlife habitats are such
areas of national parks and sanctuaries that are required to be kept inviolate for the purposes
of wildlife conservation.
The various activities allowed in these protected areas is given in the table no. 1
Table no. 1: Categories of PAs in India and their differences
PAs
Issues
National
parks
Wildlife
sanctuaries
Conservation
reserves
Community
reserves
Tiger
reserves
Critical
wildlife
habitats Protection
category
Very strict
protection from all
human
Strict, but
allowing some human activity
Strict for activities
negatively impacting conservation
objectives, but do not
Strict for activities
negatively impacting conservation
objectives, but do
Very strict
protection from all human
activity
Very strict
protection from all human
activity
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activity impact human use not impact human
use
Management
and governance
Chief Wildlife
Warden,
forest department
Chief Wildlife Warden, forest
department
Conservation Management
Committee
(representatives from the forest department,
one representative
from each panchayat, one representative
each from
Department of Agriculture and
Animal Husbandry
Community Reserve
Management
Committee (five representatives from
the village
panchayat, one representative from
the forest
department)
Forest department
Forest department
Human
settlements
Not allowed
Allowed Allowed Allowed Interpreted by the forest
department as
not allowed in
the core
interpreted by the forest
department as
not allowed
Rights to forest
resources
Not
allowed
If cannot be
settled and/or
alternatives cannot be
provided, then
allowed
Allowed Allowed interpreted by
the forest
department as not allowed
interpreted by
the forest
department as not allowed
The various categories of protected areas in India is given in the Table no 2
Table No 2: Protected area network in India
Protected Areas Number Area % of geographical area
National Parks 102 40074.78 km2 1.22 %
Sanctuaries 520 1,22867.34 km2 3.74%
Conservation Reserves 57 2017.94km2 0.06 %
Community Reserves 4 20.69 km2 0.0 %
683 164980.75 km2 5.02 %
Source: ENVIS Center on Wildlife and Protected areas
Inspite of many numbers of legally protected areas, the area is just 5.02%. On the
other hand the agricultural land (% of land area) in India was 60.53 in 2009, according to a
World Bank report, published in 2010. The population of India stood at 121 crores according
to 2011 census which means there is a tremendous pressure on the land for resources.
Protected areas scenario in Rajasthan
Rajasthan is the largest state of India having 32 districts. The forests of Rajasthan
cover an area of 32,638.74 sq. km which is 9.54% of the total geographical area of the state.
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They are spread unequally in northern, southern, eastern and south-eastern parts. There are 3
national parks, 25 sanctuaries and 4 conservation reserves.
The wildlife populations in the state of Rajasthan are presented in the table below.
Rajasthan state having many PAs is teeming with wildlife which is not only confined
to the National Parks and Sanctuaries but more of them are confined to the areas outside PAs
barring the tiger populations. Table No. 3 obtained from the website of Rajasthan Forest
Department, wildlife wing gives the data of the wild animal populations in and outside PAs.
Table No. 3
PRESENT PROBLEM SCENARIO
The above table tells that the state of Rajasthan is rich in wildlife and the considerable
numbers of wild life outside the protected areas are always in conflict with the humans and
livestock. This is one of the biggest problems the forest department is facing in Rajasthan.
Wild animals especially tiger, leopard, sloth bear, striped hyena, jackal, wolf are in direct
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conflict with people. Animals like wild boar, sambar, nilgai, chital etc. raid the crops
surrounding the forests and face the ire of farmers.
Considerable number of animals and bird species always inhabit human dominated land
scapes due to which they are under constant threat from the people and the stray dogs. The
various problems of the animals living outside the protected areas are
1. Killing/ injury of humans and livestock by carnivores like tiger, leopard, sloth bear,
wolf, jackal etc.
2. Poaching of black buck, Chinkara, peacock, jungle fowl, grey francolin, Indian hares
etc. for pot / bush meat
3. Retaliatory killing of animals mainly tigers , leopards, sloth bears, wolves, jackals by
people outside PAs
4. Stray dogs injuring and killing black buck, Chinkara, peacock all-round the year
5. Loss of corridors in case of tiger reserves like Sariska and Ranthambhore where the
animals stray out and are in direct conflict with the livestock and people
The protected areas in Rajasthan are porous and the boundaries often are breached by local
people who enter the forests for grazing, fuel wood collection, and others minor forest
produce collection. Many villages inside the PAs are the reasons for human wildlife conflict
and the religious tourism in the parks is aggravating the situation day by day. The various
reasons stated for the man animal conflict are
1. Villages inside and surrounding the protected areas
2. Wild animal depredation into human habitats
3. Mob and unruly behavior of people
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4. Lack of preparedness in the forest department to tackle the man animal conflict
situations
5. Small size of the protected areas
6. Negative attitude of people towards forest department
As per government records of forest department of Rajasthan , following table no. 4
and 5 depicts the extent of recorded conflicts and damage to livestock.
Table 4: Human wild life conflict
S.no year Loss of human life Permanent
incapacitation
Temporary
incapacitation
Total ex-
gratia paid
No. of
cases
Ex-gratia
paid
No. of
cases
Ex-gratia
paid
No. of
cases
Ex-gratia
paid
(in lacs)
1 2 3 4 5 6 7 8 9
1 2009-10 5 05.00 3 1.50 48 2.45 08.95
2 2010-11 2 02.00 3 1.50 37 3.17 06.67
3 2011-12 7 14.00 0 0 19 2.04 16.04
4 2012-13 4 08.00 0 0 27 5.50 13.50
18 29.00 6 03.00 131 13.16 45.16
Table 5: wildlife damage to Livestock
S.no year Buffalo
and Ox
killed
Cows
killed
Calves of buffalo
and cow killed
Goats and sheep
killed
Ex- gratia paid
(in lacs)
No. of
cases
No. of
cases
No. of cases No. of cases
1 2 3 4 5 6 7
1 2009-10 22 82 8 86 3.08
2 2010-11 22 72 10 81 2.87
3 2011-12 14 59 8 76 5.21
4 2012-13 11 45 16 49 4.16
69 258 42 292 15.32
PRESENT APPROACH : SPECIES RECOVERY BASED AND AREA SPECIPIC
Great Indian Bustard conservation at landscape level (Species Recovery base)
The endemic great Indian bustard (GIB) is under threat of extinction and the largest
population of 100–125 birds exists in Jaisalmer, Barmer, Ajmer and Bikaner districts of
Rajasthan. A landscape conservation strategy using conservation/community re-serve concept
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that includes controlled traditional land uses with GIB-friendly infrastructural development is
needed.GIB requires a landscape level conservation policy. Its habitat occurs in areas where
human-induced changes in the landscape are most rapid due to intensive agriculture and
industrialization, making it difficult to create protected areas that encompass GIB landscapes.
Moreover, some form of traditional land uses like dry farming and controlled grazing are
beneficial to GIB. Thus, its conservation is not entirely incompatible with some forms of
human use of the landscape which requires minimal infrastructural development.
GIB-friendly grassland management regime will benefit local communities in the long
run as it will enhance productivity for livestock and prevent overgrazing. A major threat
today to bustard habitat is not so much from pastoral use of GIB landscape but rather its
conversion to other land uses such as intensive agriculture and industry, along with their
associated infrastructural developments. Such land use changes rarely benefit local
communities, and therefore it will be relatively easy to bring in reforms which are both
economically beneficial for local people, as well as being GIB friendly. Appropriate
incentive-driven legislation and policy reforms have to be implemented in collaboration with
local NGOs to achieve this dual goal. Publicity and awareness campaigns should be taken up
to generate support among the local people A profitable and equitable mechanism to share
revenues generated from eco-tourism with local communities (Narain et al. 2005) may go a
long way in harnessing support for GIB conservation. Along with designing appropriate
conservation action plans, the restoring and managing of the grasslands or grazing lands by
promoting community institutions is seen as an effective step towards enhancing fodder
availability and quality in these areas, which in turn would create habitats for the Great Indian
Bustard.
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Protection of wild life habitat in Desert areas of rajasthan ( Area Specific base)
Under the Centrally sponsored scheme,“National Wildlife Action Plan(2002-2016)”,
the state of Rajasthan has taken up a project named " Protection of wildlife habitats in desert
districts of Rajasthan funded by MoEF as a 100% central assistance. The name of the
component under the scheme is " protection of wildlife habitats outside protected areas" and
the data available for the year 2008-09 gives a description of the project. It covers the high
value biodiversity areas of ten desert districts of Rajasthan namely Jodhpur , Barmer ,
Jaisalmer, Jalore,Pali, Nagaur,Bikaner, Ganganagar, Hanumangarh and Churu and in
total 11890 villages. The biodiversity recovery programme envisaged supports six globally
threatened species namely, the great Indian bustard, lesser florican, houbara bustard, grey
wolf, chinkara and spiny tailed lizard. The funds provided for the same under state plan
from2004-05 to 2007-08 is to the tune of 21.97 lakhs.
There is an urgent need to provide necessaryinfrastructure facilities and deploy
adequate staff at strategic placesto protect the free roaming wild fauna. The plan for the year
2008-09 contained capital expenditure for preperation of biodiversity plan, development of
rescue and veterinary care center for wild fauna purchase of multiutility vehicles along with
ambulance and communication equipments. Construction and commissioning of guzzlers is
included in it.The recurring expenditure was on management and upkeep of wild faunain
drought prone areas and on awareness generation. Transportation of water, feed and fodder
during drought periods is included in the recurring expenditure. The multiutility vehicles ,
wireless and GPS sets will be used for patrolling the entire areas for protection of With
reference to the proposal from Chief Wild Life Warden Rajasthan, on integrated development
of wildlife habitats (component-Protection of wildlife outside Protected Areas)- Rajasthan,
the Government of India gave administrative/ financial approval for Rs 92.10 lakhs for the
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above scheme for the year 2008-09. Various works have been proposed and have been
carried out in Bharatpur high value biodiversity area and Thar Desert high value biodiversity
area to facilitate conservation of biodiversity out of protected areas wildlife.
STRATEGY: INVOLVING PARTICIPATION OF STAKEHOLDERS IN
MANAGEMENT
As per the above table depicting increasing trend of man animal conflict due to habitat
shrinkage and various other social demographic factors , the present management needs to
rethink for protection of wild life beyond the contours of protected area. Since the above
conflict involves attitude of human being versus wild life along with economies of illegal
trade of wild life the management strategy need to have a societal approach with the
participation of wild life lovers of the society. There are umpteen examples where the Indian
/State government have taken steps towards the conservation of wild life and finally
concluded "Conservation cannot be imposed from above. Any conservation effort must
involve the local people, based on their interests, skills, self-reliance and traditions and
it must initiate programs that offer them spiritual and economic benefits." (Schaller,
1993).With the same spirit, in India there are communities where either they are carrying on
an age-old practice of regulated use, management of resources and protection of species and
habitats or have evolved such systems in recent times for a variety of reasons. Such areas
have become known as community conserved areas (CCAs). CCAs have been defined as
“natural and/or modified ecosystems containing significant biodiversity values, ecological
benefits and cultural values, voluntarily conserved by indigenous peoples and local
communities, both sedentary and mobile, through customary laws or other effective means”.
These include the protection of trees on which migratory and local birds roost and nest,
village irrigation tanks being used by wild birds and animals, coastal areas where youth
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groups are involved in the protection of turtles and their nesting sites, forest areas being used
and protected by local people, parts of rivers where no fishing is allowed, and many more.
In most states, the community has come up with rules and regulations, and penalties
for anyone violating these. Usually, also, there is a system to protect the area, such as forest
protection committees, youth groups, wildlife protection groups, women’s committees, even
gram sabhas (village assembly) actively protecting the wildlife. Most importantly, strong
leadership from within the community, and often a supportive role from outside, has been
crucial in successful conservation by communities. At Khichan village (Rajasthan), villagers
provide safety and food to wintering populations of demoiselle cranes which flock there in
huge numbers of up to 10,000 birds (Pathak et al.,). In Goa, Kerala and Orissa, important
nesting sites for sea turtles such as Galjibag and Rushikulya and Devi beaches are being
protected through the action of local fisher folk and volunteers. Of the 2,240 sq. km stretch of
the Gori Ganga river basin in the upper mountains of Kumaon, 1,439 sq. km is under the
management of village van panchayats. This area forms an important corridor between the
Nandadevi Biosphere Reserve and the Askot Wildlife Sanctuary which are critically
important for highland biodiversity.
The Bishnois people living in western Rajasthan on the fringe of the Thar Desert,
have for centuries, been conserving the flora and fauna to the extent of sacrificing their lives
to protect the environment. For these nature-loving people, protection of the environment,
wildlife, and plants is a part and parcel of their sacred traditions. Almost every village in
Rajasthan has a gauchar where the Chinkara, spotted deer and black buck would feed and
people would not harm them. Andhra Pradesh is rich in nesting sites of water birds. In
Veerapuram village, painted storks, pelicans and black-headed ibis have been nesting since
time immemorial, at times exceeding 5,000 in numbers. Pedullupalle village of Cuddapah
district protects painted storks, white ibises, and cormorants, which have been nesting for
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over a century. Nellapattu and Vedurapattu, in Nellore district, have been visited by open
billed storks, white ibis, and cranes since ancient times. Villagers in all these villages have
zealously looked after these birds and protected them from external threats. Due to its
ecological importance, Nellapattu was declared a wildlife sanctuary in 1997.
DISCUSSION OF ISSUES IN PERSPECTIVE OF ALL STAKEHOLDERS
The main challenges are even though the animal habitat within the PAs is being
scientifically managed, the lack of such attention in adjoining areas, is leading to
fragmentation of habitat and loss of animal corridors. While endangered species of wild
animal and birds are accorded full legal protection under national and international law and
conventions against such illegal hunting and from trade or commerce in their derivatives, it is
often a lack of effective organization and coordination between PA management and the
Forest Department machinery outside the PAs, which is responsible for the decline in their
numbers. A significant number of our wildlife populations, including that of many threatened
and endangered species, are found outside our Protected Area network, in areas including
Reserved Forests, Revenue Forests and Lands, Village Forests and commons, Private Forests
and Lands, and Community Areas. Such lands can also act as corridors, connecting wildlife
habitats. It is seen that such areas are extremely vulnerable both from the perspective of high
mortality of wildlife as also very high human-wildlife conflict. Forest Areas harboring
important wildlife species or identified as critical corridors, particularly those immediately in
the vicinity of PAs, should receive support on a priority basis for building capacity, including
appropriate infrastructure for wildlife protection in these areas. Working plans for Forest
Areas, especially those in the vicinity of PAs; usually do not give adequate significance to
wildlife conservation issues in their planning process. The Working Plan code prescribes that
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all Working Plans are to have a section on wildlife conservation, which is to be developed
under the guidance of the Chief Wildlife Warden. This should be given due significance, and
not just as a matter of routine, so that the broader goals of maintaining landscape integrity
and viable populations of wildlife, as well as to reduce human-wildlife conflicts are
adequately addressed.
To address all the issues of protecting the wildlife outside the PAs, the Government of
India has come up with a Centrally Sponsored Scheme known as “National Wildlife Action
Plan(2002-2016)” with the objective to provide adequate protection to wildlife in multiple
use areas, such as farm lands, waste lands, wet lands, coastal habitat etc. that form corridors
linking up the protected areas and providing for genetic continuity between and among them.
Adopting and implementing strategies and needs outlined above will call for action covering
the following parameters:
RESULTS
The priority projects to be taken up to protect wildlife outside PAs would be
a) Evolving and prescribing guidelines for local community involvement in the
different Management zones of PAs and adjacent areas.
b) Initiating orientation programmes for PA staff and developing capacities to
implement developmental activities for the local people in a way compatible to
conservation.
c) Enhancing allocations for and strengthening the schemes in the forestry and wildlife
sector for community support through ecologically sound development.
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d) Holding public hearings in affected areas around the PA once every year. These
should cover damage from wild animals to crops, livestock and human life as well
as adversity to wildlife from forest fires, excessive livestock grazing, encroachments
on forests or PA lands, illegal tree cutting and poaching. Planned prevention and
control measures should be implemented in participation with affected people as
interest groups. Staff, community and NGO based committees should be formed for
transparent and speedy assessment of damage and distribution of compensation.
e) Formulating schemes for conflict management, especially prevention and control of
crop/property damage and injury to or loss of human life, in all ongoing and new
wildlife schemes.
f) Making all relevant information on conservation policies and programmes publicly
accessible in local languages, well in time for a meaningful dialogue with local
people with the objective of conflict resolution.
g) Giving priority to the local communities in employment for various protection and
conservation works such as fire protection, road repair, improvement of habitat and
water and soil conservation measures.
h) Providing a range of incentives to conserve wildlife in different landscapes across
different land and water uses: rewards and public honor for commendable
conservation work and actions, granting of biomass and water resource rights for
personal consumption for communities that have helped protect or restore wildlife
habitats, employment in local conservation works, financial rewards and incentives
to protect sacred groves, share in penalties extracted from poachers, share in tourism
revenues, incentives to move away from ecologically ill-advised activities.
i) Encouraging people to help protect and take measures to manage wildlife habitats
outside PAs (including community conserved forests, wetlands, grasslands and
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coastal areas) as these areas are often critical for wildlife, or as vital corridors that
link the PA Network.
j) Initiating orientation programmes for PA staff to build a positive attitude towards
local people and their rights.
k) Landscape level Planning and Management
Landscape level planning involving the forest department and people is the need of
the hour for effective conservation of wildlife in and outside PAs. A landscape can be
defined as a heterogeneous area comprised of a cluster of interacting ecosystems at
broad scales of space and time. In the conservation areas, landscapes are variously
comprised of four kinds of lands having a gradient of amount of government
management control that would help provide for biological diversity: (1) protected
areas such as national parks and wildlife sanctuaries, having natural conditions and
very strict management; (2) reserved forests having management as per the approved
working plans; (3) protected forests and community forests, having limited
management; and (4) private lands including agricultural fields, having little to no
government management (Marcot et al.,). Landscape planning for conservation of
biodiversity aims at developing and ultimately implementing management for such
lands in a consistent, integrated manner. The Landscape Area Plan is one of the
principle implications of the National Forest Policy of 1988 for achieving goals for
biological diversity. The following steps are described below as a general process for
producing a Landscape Area Plan. These steps are adapted from experience elsewhere
(Miller 1996) with integrated forest planning. Each of these steps should be carried
out in open consultation with local and regional leaders of human communities.
♦ Delineate Landscape Planning Area boundaries
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♦ Collect relevant inventories
♦ Describe the current situation, major trends, resource potentials, and human use
needs.
♦ Establish overall multi-use goals
♦ Devise a reasonable array of alternatives to meet overall goals
CONCLUSION
Conservation of wildlife outside protected areas needs a holistic approach from the
Government, local people and NGOs. The conservation efforts should involve local people
with a sizeable flow of benefits to them coupled with active management initiatives from the
forest departments including management of habitats outside PAs and enabling animal
movement across landscapes by maintaining functional corridors. Timely compensation for
crop damage, loss of human life and livestock killings should be addressed immediately.
Spreading awareness about wildlife values and their role in balancing ecosystems to the
people at large is the responsibility of the forest department. The initiatives taken up under
National Wildlife Action Plan, 2002-16 in the desert districts in Rajasthan are in the right
direction for the protection of the wild animals outside PAs. Trained wildlife experts with
adequate rescue and rehabilitation centers and the goodwill of people towards wildlife would
certainly improve the situation in the ground level and protect the wildlife which have
strayed out of their habitats.
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7. Wildlife Life (Protection) Act, 1972
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