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and helps to suppress invasive species. Technical and financial assist-
ance has been received from the Governments of Australia, Denmark,
Switzerland, Netherlands, Finland, USA and UK, as well as from
multilateral agencies like UNDP, FAO and The World Bank in imple-
menting the CF programme.
Improvements in carbon sequestration potentiality
Improved forest management initiatives have also contributed to
enhancing the carbon sink and sequestration potential of forests.
REDD+ pilot projects, supported by Norwegian Assistance for
Development (NORAD), indicate that the annual average forest
carbon increment in CF from the project area was estimated at
2.6 tC.
7
This demonstrates the potential of community forests to
support climate change mitigation by reducing carbon emissions and
enhancing carbon removal capacity. Local involvement in carbon
stock estimation shows the scope of capacity-building for knowl-
edge sharing and technology adoption from the REDD+ mechanism.
GoN received support from the Governments of UK, Switzerland
and Norway and the World Bank/Forest Carbon Partnership Facility
in the national REDD+ readiness process.
Restoration of functional corridors in critical landscapes
Conservation initiatives of local CF networks have been instrumen-
tal in protecting focal species like tiger, one-horned rhinoceros, wild
elephant, red panda and snow leopard at landscape level. The estab-
lishment of functional corridors and bottlenecks to facilitate free
movement of wildlife between Protected Areas are unique examples
of success in biodiversity conservation of a transboundary nature.
One such corridor was successfully restored within five years and
the forest has been functioning as an important corridor for wildlife
in Terai Arc Landscape (TAL) with technical and financial support
from UNDP and WWF Nepal
Improvement in environmental restoration and food security
Since the contribution of CF to household income has not been
properly valued and quantified at national level, to what extent the
regrowth of biomass has contributed to uplifting the livelihoods of
the rural ultra-poor is not clearly understood. However, pro-poor
leasehold forests implemented by the Government with financial
and technical support from International Fund for Agricultural
Development and the Food and Agriculture Organization (FAO)
demonstrates that after implementation of this programme, vegeta-
tive cover had increased up to 90 per cent after seven years.
An effectiveness study commissioned by the Department of
Forests/FAO in 2009 shows that livestock units have increased due
to improved forage production that has directly contributed to food
security. It has also been observed that about 11 per cent of target
households now have year-round food security and average house-
hold income has increased by 70 per cent.
Issues and challenges ahead
Product-focused CBFM now has new windows of opportunity from
the emerging market of environmental services, including biodiver-
sity, carbon sequestration and hydrological services. In the absence
of clear tenure rights on these services, local communities are
finding it difficult to participate in the Payments for Environmental
Services (PES) market. If tenure rights are well defined, then there
is potential for sustainable financing of CBFM from PES so that
local people can be made more responsible for forest conservation
in future. There is still a need for a robust technical
MRV system and a lucrative carbon market may lead to
recentralization of forest governance.
8
Due to limited access to information and technol-
ogy, there is a potential risk of elite domination in the
entire PES value chain to capture prospective benefits.
Therefore, it is important to secure the rights of poor,
marginalized and women’s groups in the decision-
making process. In many places communities have been
protecting their forests at the cost of adjoining state
forests; in sub-national REDD+ projects it is difficult to
take account of such leakages in net emission reduction.
Key challenges for CBFM in capturing the benefits of
environmental services include:
• Developing an appropriate structure to satisfy local
as well as market expectation
• Developing local capacity to amalgamate the local
fragmented production supply chain to global
market networks
• Satisfying market expectations for a robust MRV
system and other national and international criteria
• Providing technical support to local communities from
the existing institutional capacity of the State agency
• Developing a PES mechanism responsive to poor
and marginalized people.
Potential futures
A one-size-fits-all approach does not work and different
modalities of CBFM are attainable, provided that local
communities have clear tenure rights on the forest products.
Prevailing policies and institutions need to be reformed to
cater to emerging public demand for PES. To capture this
opportunity, small fragmented production units need to
bundle all environmental services to reduce transaction
costs and increase bargaining power in price negotiations.
There is agreement that large sections of the popula-
tion have benefited fromCF, either in terms of consumer
goods or ecosystem services. However, benefit-sharing
mechanisms must be further improved to assure equity
and social justice for poor and marginalized households
through appropriate institutional arrangements and
capacity-building schemes.
Institutional reform may be necessary to improve
transparency and accountability in the value chain
process for CF-produced goods and services. The
current practice of mandatory representation of poor
and marginalized groups on executive committees and
allocation of CF funds for pro-poor activities are good
initiatives from Government which need strong moni-
toring and regulation to achieve the desired change.
It is also crystal clear from three decades of experience
with the CF development process in Nepal and elsewhere
that if stewardship is given to local communities, forests
can be better managed for sustainable biomass produc-
tion, biodiversity conservation, livelihood improvement
and sustainable supply of ecosystem services.
With thanks to Anuj Sharma, Narendra Chand and Nirmala
Bhandary for their generous support in preparing this paper