1.3 Objectives and the Methodology of this Review

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Review of the Implementation of the
Master Plan for the Forestry Sector of Nepal
April, 2014
Prepared for
The Ministry of Forests and Soil Conservation
Singh Durbar, Kathmandu
1
Foreword
The Master Plan for the Forestry Sector (MPFS), implemented in 1988 and concluding in 2011, has
provided the policy framework for forest conservation and management in Nepal for the last 25 years. The
country experienced significant political, economic, and environmental changes during the over two
decades of MFPS. The forestry sector itself faced challenges and opportunities, resulting from changes
internal and external. In short, much has changed in Nepal and across the world since 1988. With the end of
the MFPS in 2011, the Ministry of Forests and Social Conservation (MFSC) must now prepare a new,
relevant, and innovative forestry strategy for the future. A comprehensive review of the MPFS and the
contexts in which it operated must serve as a basis for the new Forestry Sector Strategy (FSS).
This review of the MPFS has been possible due to the support of several government and non-government
organizations as well as individuals. The MFSC highly values and appreciates their support. The MFSC
would also like to extend its sincere thanks to the Multi-Stakeholder Forestry Program (MSFP) and the
Hariyo Ban Program for supporting the review process. The MFSC would like to thank the team involved
in reviewing MPFS and preparing the FSS for their sincere effort in producing this report. MFSC
acknowledges the extensive support of Joint Secretary Mr. Ram Prasad Lamsal in coordinating the effort.
MFSC would also like to extend its appreciation to Dr. Keshav Raj Kanel, Dr. Dhruba Prasad Acharya, Dr.
Binod Bhatta, Dr. Bharat Kumar Pokhrel, Ms. Madhu Ghimire, Mr. Nav Raj Baral, and Mr. Peter Branny
for their contribution in shaping this report.
For their support and assistance throughout the process, MFSC would also like to recognize Mr. Krishna
Prasad Acharya, Joint Secretary, MFSC; Dr. Bishwa Nath Oli, Director General, Department of Forests;
Resham Bahadur Dangi, Deputy Director General, Department of Forests; Mr. Pem Kandel, Director
General, Department of Soil Conservation and Watershed Management; Dr. Maheshwar Dhakal,
Department of National Parks and Wildlife Conservation; Mr. Hasta Bahadur Thapa, Department of Forest
Research and Survey; Mr. Ram Nandan Sah, Mr. Tirtha Raj Joshi, Dr. Anuj Sharma and Mr. Bishal
Ghimire from the Department of Forests.
MFSC also acknowledges the following individuals for their work in collecting data and preparing an initial
draft of various sectoral program reports: Mr. Yajna Nath Dahal, Mr. Kumud Shrestha, Dr. Jaggannath
Joshi, Mr. Pashupati Nath Koirala, Mr. Krishna Prasad Osti, Mr. Dil Raj Khanal, Dr. Bikram Tamang, Ms.
Sangita Bista, Mr. Nagendra Regmi, and Mr. Injun Acharya. MFSC also thanks Ms. Dibya Gurung for her
input to the GESI section of this review report and Ms. Surabhi Pudasaini for editing this report.
For providing relevant data and information, MFSC would like to extend its sincere appreciation to the
Office of the Auditor General, Ministry of Finance, Financial Comptroller General Office, all departments
of MFSC, Timber Corporation of Nepal (TCN), Forest Products Development Board (FPDB), Herbs
Production and Processing Company Limited (HPPCL), Trade and Export Promotion Center (TEPC),
Singhadurbar Vaidyakhana, Gorkha Ayurved Company, Agro Enterprise Center of the Federation of
Nepalese Chamber of Commerce and Industry (AEC-FNCCI).
MFSC would also like to thank the following associations for their input: Nepal Forester’s Association
(NFA), Federation of Community Forest Users in Nepal (FECOFUN), Association of Collaborative Forest
Users of Nepal (ACOFUN), Nepalese Federation of Forest Resource User Group (NEFUG), Himalayan
Grassroots Women’s Natural Resources Management Association Nepal (HIMAWANTI-Nepal),
Federation of Forest Based Industry and Trade, Nepal (FenFIT), Nepal Federation of Indigenous
Nationalities (NEFIN), Federation of Private Forest Stakeholder Nepal (FEPFOS-Nepal), Forest
Environment Workers' Union Nepal (FEWUN), Green Growth Nepal (GGN), Dalit Alliance for Natural
Resources (DANAR), Nepal Herbs and Herbal Products Association (NEHHPA)and the National Forum
for Advocacy Nepal (NAFAN).
Lastly, MFSC would like to extend its sincere appreciation to all individuals and organizations who
contributed directly or indirectly to preparing this report.
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Acronyms
ACAP
AFU
APP
BISEP-ST
BZMC
CBD
CDM
CDO
CEGR
CF
CFM
Cft
CIAA
CIFOR
CITES
CNP
CTEVT
DDC
DFCC
DFID
DFO
DFRS
DNA
DNPWC
DoF
DPR
DSCO
DSCWM
FAO
FDF
FECOFUN
FINNIDA
FMUD
FORESC
FPDP
FRDP
Annapurna Conservation Area Project
Agriculture and Forestry University
Agriculture Perspective Plan
Bio-diversity Sector Programme for Siwaliks and Tarai
Buffer Zone Management Committee
Convention on Biodiversity
Clean Development Mechanism
Chief District Officer
Conservation of Ecosystem and Genetic Resources
Community Forests
Collaborative Forest Management
Cubic Feet
Commission for the Investigation of Abuse of Authority
Center for International Forestry Research
Convention on International Trade in Endangered Species of Wild Fauna and
Flora
Chitwan National Park
Council for Technical Education and Vocational Training
District Development Committee
District Forestry Coordination Committees
Department for International Development
District Forest Office
Department of Forest Research and Survey
Deoxyribonucleic acid
Department of National Parks and Wildlife Conservation
Department of Forests
Department of Plant Resources
District Soil Conservation Offices
Department of Soil Conservation and Watershed Management
Food and Agriculture Organization
Forest Development Fund
Federation of Community Forestry User Groups of Nepal
Finnish International Development Agency
Forest Management and Utilization Development Project
Forest Research and Survey Centre
Forest Product Development Board
Forest Research Development Plan
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FSRO
GDP
GESI
GFP
GAD
GO
GoN
GRB
Ha
HRD
HRM
IAS
IFAD
IGA
IOF
ITTO
IUCN
KAFCOL
LAPA
LFLP
LFP
LFUG
LRMP
M&E
MAP
MDG
MEA
MoAD
MoE
MoF
MPFS
MRV
MFSC
M3
NAPA
NCCNR
NEPAP
NFAP
NFI
Forest Survey and Research Organization
Gross Domestic Products
Gender, Equality and Social Inclusion
Gender Focal Person
Gender and Development
Government Organization
Government of Nepal
Gender Responsive Budget
Hectare
Human Resource Development
Human Resource Management
Invasive Alien Species
International Fund for Agricultural Development
Income Generating Activities
Institute of Forestry
International Tropical Timber Organization
International Union for Conservation of Nature
The Kathmandu Forestry College
Local Adaptation Plans for Action
Leasehold Forestry and Livestock Program
Livelihoods and Forestry Program
Leasehold Forest User Group
Land Resource Mapping Project
Monitoring and Evaluation
Medicinal and Aromatic Plants
Millennium Development Goal
Multilateral Environmental Agreement
Ministry of Agriculture Development
Ministry of Education
Ministry of Finance
Master Plan for Forestry Sector
Measurement, Reporting and Verifications
Ministry of Forests and Soil Conservation
Cubic Meter
National Adaptation Programme of Action
National Commission for Conservation of Natural Resource
Nepal Environmental Policies and Action Plan
National Forestry Action Programs
National Forest Inventory
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NFRP
NGO
NP
NPC
NSCFP
NTFP
OFMP
PA
PAF
PES
R-PIN
RBME
REDD
RPP
RRI
SCWM
SDC
SESA
SHL
SNNP
SNP
SNV
SPCR
SPS
TAL
TCN
TFAP
TISC
UNFCCC
UNFF
VAT
VDC
WID
WR
WUPAP
WUPAP
WWF
This
National Forest Research Plan
Non-governmental Organization
National Park
National Planning Commission
Nepal Swiss Community Forestry Project
Non-Timber Forest Product
Operational Forest Management Plan
Protected Area
Poverty Alleviation Fund
Payment for Environmental Service
Readiness Program Idea Not
Result Based Monitoring and Evaluation
Reducing Emissions from Deforestation and Forest Degradation
Readiness Preparation Proposal
Rights and Resources Initiative
Soil Conservation and Watershed Management
Swiss Development Cooperation
Strategic Environment and Social Assessment
Sacred Himalayan Landscape
Shivapuri-Nagarjun National Park
Sagarmatha National Park
SNV Netherlands Development Organization
Strategic Program for Climate Resilience
Sanitary and Phytosanitary Standards
Tarai Arc Landscape
Timber Corporation of Nepal
Tropical Forest Action Plan
Tree Improvement and Silviculture Component
United Nation’s Framework Convention on Climate Change
United Nations Forum on Forestry
Value Added Tax
Village Development Committee
Women in Development
Wildlife Reserve
Western Upland Poverty Alleviation Project
Western Uplands Poverty Alleviation Project
World Wide Fund for Nature
5
Executive Summary
MPFS started in 1986 but was finalized in 1988 with a planning horizon of 25 years. The goal of
the plan was to meet the Nepali people’s basic needs for forest products, protect the land, conserve
the ecosystem and genetic resources, and contribute to economic growth. A logical analysis of the
goal, objectives, and strategies led to the formulation of six primary and six supportive forestry
development programs. These had to be coherently and consistently implemented to restore the
declining forests and expand the opportunities in productive employment and economic growth
through forest-based industries.
About 92 percent of the total projected cost (USD 1.74 million constant to 1988 exchange rates) of
the MPFS was allocated for the implementation of six primary programs. The remaining eight
percent of the cost was allocated to the six supportive programs. Over the last decade, two other
themes – Gender, Equity and Social Inclusion (GESI) and Climate Change – emerged as important
programs of the forestry sector.
This summary presents the achievements, lessons, and the future direction of forestry based on the
findings emerging from the review of these twelve plus two programs. In broad strokes, this
review finds that the success of the forestry programs depends significantly on inclusive and
credible policy, accountable governance, and bottom-up planning.
Community and Private Forestry
This is the first priority program of the MPFS. The program aimed to develop and manage forest
resources through the active participation of individuals and communities to meet their basic
needs. The MPFS envisioned three major outcomes under the community and private forestry
program: increased area of sustainably managed natural forests, restoration of open and degraded
forests both in public and private land, and reduction in the consumption of fuelwood through the
promotion of improved cook stoves and the adoption of biogas. This has been the most successful
forestry program. There are now about 1.7 million ha of community forests in Nepal (representing
about 29 percent of the total forests) and about 2.25 million households as members of community
forestry user groups (CFUGs).
The program has contributed to halting forest loss and degradation (especially in the mid-hills) and
has increased the access of the rural people to forests and forest products. Lessons from the
community forestry program have influenced other development programs in Nepal. The program
has also influenced community forestry approaches in other countries; community forestry is now
globally recognized as a successful development initiative that has achieved impacts both inside
and outside the forestry sector. Other associated components of this program such as seedling
distribution, enhanced use of fuel-saving devices, and biogas installations have also been
successful. The greening of the landscape and increased biomass mainly in the mid-hills is
attributed to the success of community forestry as supported by the forestry legislation of 1993 and
the autonomy granted to CFUGs. Though designed to fulfill household needs for forest products,
more than half the supply of commercial logs are today sourced from community forests. Recent
information from Community Forestry Division suggests that CFs generate three times more
revenue than the national forests under the jurisdiction of the Department of Forests (DoF).
Though community and private forestry are classified as one program, the situation between the
two is somewhat different. There is rather less policy-levels support for the latter. For example,
while some seedlings were distributed to local households for private tree plantations, no further
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commitments have been made by the government. Nonetheless, farmers seem enthusiastic about
planting and nurturing trees on their private land. This can be seen in the increasing supply of soft
wood to veneer and plywood industries from private tree plantations.
A number of issues remain in both the community and private forestry sectors. First, better income
and employment generating programs for community forest users are required. Second, CFUGs
need support in harvesting and marketing forest products. Third, the imposition of VAT on private
forest products requires further consideration. Finally, excessive regulations on harvesting,
transporting, and trade of forest products increases the cost of doing business across the board.
National and Leasehold Forestry
This is the second priority program of the MPFS, targeting the Tarai and the mountain districts.
The plan proposed to have either the government or the corporate sector manage large blocks of
forests located at a distance from villages. The main aim of these forests was to produce wood
needed for urban use and forest-based industries. The plan also proposed large scale plantations or
enrichment plantations by the government (national forests) or by the private sector (leasehold
forests).
Limited progress in managing national forests was made during the MPFS period. Several efforts
were, however, made to better manage Tarai forests. Key among these was the Forest
Management and Utilization Development Project (FMUDP). FMUDP developed a model of
technical forestry for the Tarai forests, though this was never implemented. At a later stage,
several efforts were made to develop and manage forest resources in the Tarai through the
establishment of District Forestry Coordination Committees (DFCC), creation of forests in public
land, private sector participation in the forest development fund, and through the production and
distribution of seedlings. More recently, some progress has been made in managing blocks of
Tarai forests through the CFM model in partnership between the DFO and local/distance users. To
date, 54,100 ha of forest have been managed as CFM. Similarly, 133,000 ha of forest land has
been declared protected forests for biodiversity and environmental conservation. A new initiative
has attempted to involve all actors within the forestry sector in preparing a District Forestry Sector
Plan.
Significant progress has been made in implementing pro-poor leasehold forestry. Under this
program, which was not conceived in the MPFS, about 41,300 ha of forest land has been leased to
poor households. A total of 6,957 leasehold forest (LF) groups have been formed, with a
membership of 65,402 households. Of these groups, about 88 percent are reported to be functional
and about 68 percent fall in the good to moderately good category.
The national forest program has been constrained by a number of issues. Among them, the lack of
decentralized institutional mechanisms to foster local people’s participation is a key issue. Other
issues include: lack of forest land use classification; mounting pressure on the forests of the Tarai
and Chure due to changes in demography; frequent policy changes in the allocation of forests as
well as in the harvest and sale of forest products; wild fires, uncontrolled grazing, and the illegal
removal of forest products; increased work burden of the DFO staff; lack of skills to ensure
practice of sustainable forest management; haphazard conversion of national forests into protected
forests reducing the potential of multiple use; and forest encroachment and degradation.
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Wood-based Industries
This program aimed to facilitate the conversion of wood into commodities needed by the people,
and to contribute to economic development through industrialization. Significant gaps remained in
the demand and supply of timber during the entire period of MPFS. This adversely impacted the
efficiency, growth, and sustainability of forest-based industries. Forest-based industries also
suffered in the absence of various supportive policies. Furthermore, the proposed low-cost
financing to forest-based industries for renovation, expansion, and pollution-control facilities
were also not realized in practice. The production of veneer and plywood has significantly
increased over the years due to the availability of soft wood mostly from private forests, and to a
lesser degree from community forests.
The insecurity of investment in timber production/processing has de-motivated investors. The
situation has been further exacerbated by the absence of planned forest management, unsustainable
supply of raw materials, and inconsistencies in policies. The issues that need to be tackled include:
enhanced supply of wood from government-managed and community forests, encouraging private
entities to undertake leasehold forestry, arranging financing at low interest rates through private
sector actors, and simplification of procedures for transporting forest products. Furthermore, there
is pressing need to carry out research on fast-growing short rotation timber species.
NTFP/MAP Development
This program aimed to increase the supply of NTFPs/MAPS, provide employment opportunities,
and contribute to the growth of the local and national economies. The MPFS intended to promote
MAPs, and five other NTFP groups of products (lokta, sal-seed, katha and cutch, pine resin, and
sabai grass). Among these, sal-seed and sabai grass are not currently being used as projected by
the MPFS. For the promotion of MAPs, the government prioritized 30 species of MAPs/NTFPs,
but only 19 species have been traded widely. The supply of lokta has been low for the last five
years while that of Khair has been fluctuating over the course of the last two decades. In contrast,
the pine resin processing industries have grown significantly, increasing the area and quantity of
resin tapping.
Despite the significant gap in the projected demand and supply of various NTFPs/MAPs, they still
make up about 8 percent of total exports. This is very low considering the full potential. Part of the
problem is the decreasing supply of NTFP resources from the wild. Meanwhile, there is little
cultivation on private land either through intercropping in agroforestry or as a single crop. The
subsector is also adversely affected by practices such as arbitrary granting of transport permits,
levying of informal fees during transport, and taxation on NTFPs/MAPs produced in private
forests and agricultural land.
Soil Conservation and Watershed Management
The MPFS acknowledged the very high rate of soil erosion as well as the rapid deterioration of
watersheds. As a result, it aimed to protect and conserve watersheds through the mobilization of
national and local resources. During the plan period, on-farm conservation activities took places in
5,746 ha of agricultural land. Rehabilitation activities were also undertaken over 10,000 ha of
degraded land, on 1,600 gullies, and on 1,000 landslides of various scales. Furthermore, protection
activities were undertaken on 1,489 drinking water sources with construction done on 847
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conservation and run-off harvesting ponds. A total of 413 watershed management plans, 304 subwatershed management plans, and 1,167 community development plans were prepared and
implemented at different scales. Soil conservation and watershed management services were
expanded from 25 project districts to 56 regular districts. Despite all these improvements, the
physical targets set by MPFS were not fully achieved. Furthermore, the progress made cannot be
directly compared to the plans laid out in the MPFS as many of the targeted activities were either
renamed or merged.
Insignificant progress was made in meeting people’s demand and fulfilling conservation needs.
Though the Soil and Watershed Conservation Act was enacted in 1982, its provisions were not
adequately implemented. Furthermore, the act did not strengthen institutional and organizational
arrangements for the proper use of land resources and coordination among agencies. As a result,
protection and regulatory measures were not enforced in critical watersheds. In recent years, the
challenges of soil erosion have become further intensified due to improper land use, road track
opening by using bulldozers, and due to large-scale and improper excavation of stones, pebbles,
and sand. The DSCWM, however, does not have adequate capacity to address such challenges.
Conservation of Ecosystem and Genetic Resources
This program aimed to protect special areas for their eco-system and genetic resource values as
well as to promote in-situ and ex-situ conservation of plant and animal genetic resources. To this
end, operational strategies were proposed in five program components including protected area
management, genetic resources conservation, visitor use and tourism, preservation of natural and
cultural values, and institutional strengthening.
The expansion of protected areas for in-situ conservation was quite significant after the
implementation of MPFS. The area of PAs has increased from 7.4 to 23.23 percent during the plan
period. The policy shift from 'people exclusionary' and 'species focused' to 'people-centered
community based' and 'ecosystem/landscape approach' is also a significant achievement. The
population of several protected animals such as tiger, rhino, and wild buffaloes are also increasing.
In addition, other major efforts made for ex-situ conservation during the MPFS period included:
reform of the central zoo; establishment of breeding and conservation centers for elephants,
vultures, and gharial; translocation of rhino and blackbuck; and establishment and maintenance of
botanical gardens and a national herbarium.
Despite such progress, a number of issues and challenges exist for the conservation of ecosystem
and genetic resources. Wildlife poaching and the illegal trade in wildlife parts and NTFPs has
remained a serious conservation challenge. Human-wildlife conflict in and around PAs has
become a major obstacles for conserving wild animals, particularly threatened species. Poaching
of and illegal trade in plant/animal species and their parts is also a serious threat. Furthermore, the
concentration of visitors in just a few protected areas has accelerated negative environmental
impacts. The expansion of invasive alien species (IAS) is also a serious threat to forest ecosystem
and biodiversity conservation. Meanwhile, within forestry organizations, there are staff problems
both in terms of number and capacity of existing employees. There are similar problems in budget
allocation, infrastructure, and logistics.
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Policy and Legal Reform
The reform agenda for forestry policy was explicitly aimed at increasing the supply of forest
products for both household consumption and for urban/industrial needs; reducing the demand of
fuelwood through improved stoves and biogas; conserving the biodiversity and genetic resources;
focusing on integrated farming and improved watershed through decentralized land use planning;
and increasing the role of private sector in forest industries and enterprises.
Based on these points of the reform agenda, five strategies were proposed. One of the strategies
was solely devoted to policy implementation. This strategy called for reforms in forest law to
promote community forests based on decentralized users’ groups. The strategy also called for
improving the livelihood of the poor dependent on forests; reforming the roles and responsibilities
of forest agency staff; providing extensive and intensive retraining to forestry staff so that they
become advisers to users’ groups; expanding the capacity of the communities and the government
in planning, research, and extension; and fostering the involvement of NGOs in forestry programs.
Some of these reform strategies were taken on board by the Forest Act 1993 and the Forest Rules
1995. Indeed, some of these reforms are more empowering than those recommended by the MPFS.
These legal regimes allow the communities to manage forests anywhere, and also sell the surplus
products in the market. They could use the money thus generated for livelihood and community
development. The autonomy granted to CFUGs has helped in the development of democratic
platforms at the grass-roots level for social and political mobilization. The decentralization
continued even in the management of buffer zones around National Parks and Reserves, and
watershed management at the sub-watershed level. Legal provisions on pro-poor forestry, though
not articulated in the MPFS, have expanded further opportunity to reduce poverty and increase
greenery in the degraded forest land. Community-based management has been extended to climate
change adaptations such as LAPA. Forestry planning has been based on a bottom-up and multistakeholder approach even though the budget is provided by the NPC. A Forest Development
Fund has been established to carry out forest regeneration and management. Though the fund has
yet to be operationalized, the idea is to have half the total budget collected by raising funds from
private timber traders.
Policy provisions have, however, been weak in nurturing commercial leasehold forestry,
promoting wood-based industries, and managing government forests. While TCN is still operating,
its market share has significantly reduced. The Nepal Fuelwood Corporation has been merged with
TCN. The HPPCL though still in operation gets its raw material through competitive bidding. The
size and scope of the Forest Products Development Board has also been significantly reduced,
with its area of operations shrinking to less than 20,000 ha in the central and eastern Tarai. A
forest land use policy has not been formulated although potential areas of community and
leasehold forestry have been estimated.
The challenges in policy/legislation relate to the frequent, abrupt, and unilateral ‘policy’
declarations which go against the spirit and letter of the forest act and regulations. Institutional
leasehold forestry rules are not compatible with the incentives for commercial actors. In short,
policies on forest enterprise development are conflicting and lead to underinvestment in forestry
operation and industries.
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Institutional Development Plan
The Institutional Development Plan (IDP) of the MPFS was prepared to facilitate systematic
organizational development of forestry sector institutions. The plan proposed to reorganize the
MFSC and its various departments. The short term goal was to immediately eliminate the most
oblivious short comings. The long-term goal was to continuously strengthen the MFSC to ensure
effective implementation of MPFS plans and programs.
As proposed by the IDP, the MFSC, its departments, and some parastatals were restructured,
dismantled, or privatized. After the implementation of MPFS, a drastic change in structure and
staffing was made in 1993 and 2000. However, both these reforms undermined the spirit and
strategies set by the MPFS. These reforms were reported to be much influenced by the values of
the High Level Administrative Improvement Commission and the Structural Adjustment Program.
But they failed to address the issues of forestry organizations, creation of social image,
professionalism, retention of proactive forestry professionals, and fostering of change agents in the
government service. The issues around inadequate structure, limited human, physical and financial
resources, and cooperative political leaders still exist. The most pressing need of the day, when
looking at the forestry sector from a holistic point of view, is to make organizations context
specific and decentralized.
Human Resources Development
This program is related to the state of human resources within the MFSC, the parastatals, and
educational institutes providing training. The demand and supply projections were made, gaps
were identified, and a financial plan presented. The objective of the plan was to provide human
resources necessary to implement the MPFS programs. This, however, was a very narrow focus.
Many important aspects of human resource development such as transfer and promotion system,
career planning and development, workforce diversity, and succession planning were left out.
The restructuring of 1993 and 2000 missed both the provisions and the spirit of the MPFS.
Nevertheless, significant progress has been made in some aspects of human resource development.
Major achievements were made in forestry education and training. Forestry education at the
bachelors, MSc, MPhil, and PhD levels are offered at various institutes. Within the forestry sector,
reorientation and re-training of forestry staff was emphasized by all institutions and projects. The
HRD and training division at the center and five regional centres have also been institutionalized.
All these changes, together with new opportunities for workshops, seminars, and study tours have
significantly contributed to changing the role of forestry field staff from ‘policing’ to ‘facilitating’.
The HRD and HRM, however, face a number of issues and challenges. The human resource
system – appointment, transfers, appraisal, promotion, training – is still very ad hoc. The MFSC
also does not have a HR policy or an information system. In a grave oversight, there is no
appropriate grievance handling mechanism. This is further exacerbated by a leadership style that is
either feudal or laissez-faire. The attitudinal aspects of staff including intentions, commitments,
enthusiasm, and inspiration are often ignored. As a result, the sector has failed to attract and retain
competent human resources as well as failed to address GESI issues.
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Forestry Research and Extension
This program aimed to strengthen the research capacity as well as expand extension service to
utilize research results for the benefit of the forestry sector. The achievements of the program have
been mixed. The overall research capacity of the ministry and department to carry out the research
effort from conceptualization to reporting has been weak across the board. Indeed, the research
agenda has rarely been crafted based on the needs of the users. For example, the forestry sector has
not adequately researched its contribution to environmental protection, social inclusion, and
especially its impact on economic development aimed at poverty alleviation. Similarly, minimal
research has been done on the impact of tourism, industry, and other factors on watersheds and
national parks.
Forest Resource Information and Planning
The main aim of this program is to develop national capacity to conduct forest surveys and gather
information on forest resources that can be fed into both long-term and operational planning.
While information generation was not satisfactory in the MPFS period, good progress has been
made in institutionalizing participatory bottom-up planning in some sub-sectors. Nonetheless, the
forest resources information generated is not adequately disaggregated by either physiographic and
political boundaries or forest management regimes. There is a pressing need for such
disaggregated information. Indeed, a user friendly forest resources inventory map should be
prepared by both physiographic region and forest management regimes.
Monitoring and Evaluation
This program aimed to institutionalize a system for monitoring forestry operations and their
impacts as well as use the gathered information to guide the development process. The MFSC
practiced a M&E system guided by the NPC, and thus designed to cover all sectors of the GoN. As
a result, it did not capture the requirements set by the MPFS for its programs. In fact, it hardly
reflected the status of implementation of MPFS. To date, there has been little achievements in
implementing four sets of activities (Designing a M&E system, capacity building, collaborating,
and using advanced techniques) proposed by the MPFS’s M&E plan. Though a computer-based
M&E system was designed, it was never used except in the case of the community forestry
database. The individuals working in the M&E division are treated as inferior to those in other
sectors, and thus lack motivation in carrying out their tasks.
Donor funded projects and programs regularly monitor and evaluate their activities, outcomes and
impacts, but their institutionalization and sustainability are weak as they are not followed through
once funding from donors is terminated.
Climate Change and Forestry
Climate change has become a global issue since the Rio conference of 1992 though it was not a
concern when the MPFS was drafted. With two main components - carbon mitigation and
adaptation - the overall policy on climate change is guided by climate adaptation, mitigation and
carbon sequestration as well as mobilization of financial resources for technology
development/transfer and for capacity-building. From Nepal’s perspective, climate change
adaptation at the community level is an important approach as articulated in the climate change
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policy, NAPA, and LAPA. On the mitigation front, MFSC is now preparing a REDD+ strategy to
reduce deforestation and degradation and enhance forest management through financial assistance
from the World Bank.
Lessons from community forestry have been expanded to climate adaptation in the LAPA process.
Climate adaptation plans can be designed and implemented by the groups formed under the
forestry sector at the local level. As monitoring, review and verification (MRV) and social
safeguards are important components of REDD+, they can be very useful tools to conserve,
manage and use the forests. The issue of who owns the carbon has been hotly debated in different
forums. The debate is focusing on whether the payment under REDD+ should go to government
first and then be channeled to other community-based organizations. The question of whether a
market mechanism, development grants, or a hybrid (mixed) payment mechanism is best is also
unresolved.
Gender, Equity and Social Inclusion
The GESI strategy adopted by the MFSC in 2008 commits to ensure gender and social inclusion in
the forestry sector. The Ministry has identified four change areas including: GESI sensitive policy
and strategy, good governance and institutional development, GESI sensitive
budgeting/programming and monitoring, and equitable access to resources and benefits.
The objectives of the GESI strategy within the forestry sectors are twofold. First, it aims to assist
government, non-government, donor and private sector bodies working in the forestry sector to
institutionalize social inclusion in their organization and programs. Second, it aims to guide all
organizations working in the forestry sector to be responsive and inclusive. The strategy has
shown some results in a few areas. The representation of women in various regimes of
community-based forestry has significantly increased. However, women’s participation in the state
structure of MFSC is only 3.3 percent. The government has, however, committed to increasing
inclusion through both the Interim Constitution of 2007 and the revised Civil Service Act. It also
initiated a gender responsive budgeting practice in 2007/08. Yet, only 3.55 percent of the
ministry’s total budget is directly earmarked for gender. The culture of male dominance is still
prevalent in the society although the laws and rules are becoming more inclusive. The government
is struggling to translate the emerging progressive policies into practice.
Evolution of Political Economy and forestry
The political economy of Nepal has changed significantly over the last 30 years. The country has
undergone three constitutional and regime changes in that short timeframe. The MPFS was
designed during the time when the monarchy had absolute power. The subsequent political change
of 1990 which ushered in multiparty democracy led to a decentralization of forestry programs and
the expansion of civil society. Empowering people to participate in development and conservation
works was a mantra of this new regime. However, the armed internal insurgency beginning in
1996, led to the virtual immobilization of state authority. The state machinery, including the
forestry sector, was virtually confined to urban areas. In 2006, a ceasefire was called and
ultimately resulted in a peace treaty among the warring factions.
13
As part of the peace agreement, an interim constitution based on principles of republicanism,
federalism, and proportional representation was drafted in 2007. Elections to a constituent
assembly were held in 2008 and again in 2013, though this body has yet to produce the muchanticipated new constitution. Meanwhile, elections at the local level have not been held since
1997. In the long absence of legitimate and elected local officials, civil society bodies such as
CFUGs have become major players in rural Nepal. Financial assistance, mostly donor funding, for
forestry among other rural development activities, were channeled through these grass root
organizations which were also more democratically formed and operated.
These political transitions, which took place over the MPFS time period, had significantly affected
forestry development in Nepal. The key political economic factors are listed below:

The structure of the economy has changed. When the MPFS was drafted, agriculture and
forestry accounted for more than 66 percent of the total GDP of Nepal. Today, the share of
agriculture and forestry has gone down to about 33 percent.

The MPFS allocated USD 1.7 billion for the implementation of the twelve programs
described above. Excluding USD 1.1 billion of total allocation to be provided by the
private sector, which is not recorded in the government’s accounting, the analysis shows
that only about 35 percent of the total allocated amount was actually spend in the forestry
sector.

Similarly, the total share of government spending on the forestry sector has declined from
3.5 percent in 1992 to about 2.0 percent in 2011. The proportion of revenue from the
forestry sector to the government has also decreased from 2.5 percent in 1993 to 0.25
percent in 2011. On the positive side, the income of the CFUGs has increased from zero in
1990 to about NPR 2 billion in 2011, which is about four times the government revenue
from the forestry sector.

There has been a demographic shift among the three ecological regions. About 60 percent
of the total population used to live in the hills in late nineties. Now, more than 50 percent
of the total population lives in the Tarai. Similarly, the urban population has increased from
about 5 percent to 17 percent during the MPFS implementation period. This has
significantly reduced the pressure on forests in the hills but increased pressure on the Tarai
and Chure regions.

The number of youth going overseas as labor migrants has soared to about five million,
bringing in about USD 4 billion in remittances annually. This amounts to about 25 percent
of Nepal’s total GDP. Most of this income is, however, spent on consumption with very
little invested.

Today, about 17 percent of household energy is met by LPG imported from India. In 1988,
the share of LPG in household energy was negligible.

Shortage of male labor (and consequently its high price) due to overseas employment and
urban migration as well as the infusion of cash into the rural economy (due to remittance)
has led to decreased pressure on forests. Alongside, there has also been an abandonment of
marginal farming areas and its conversion into forests as well as the nurturing of trees on
14
farms in the mid-hills and mountains. This has led to increases in area and condition of
mid-hills forests even as road networks have cut into forest areas to a degree.

Increased demographic pressures, expansion of public infrastructure, and marketization of
the economy has negatively impacted forest area and condition in the Tarai and the Chure
hills.

International experiences and discourses have shown that our understanding of forestry is
continuously evolving. One major shift is that from centralized to decentralized forestry,
with managing authority slowly being transferred to local communities and indigenous
peoples. International experiences have shown that decentralized forest management
systems under different forest regimes are better performing that centralized management
systems. Moreover, international criteria of forest management now also covers tenure
rights of the local people alongside their role in decision-making and gaining profits. While
the GoN has carried out large-scale decentralization efforts, security of tenure rights of the
local/indigenous users have been diluted over time.
Learning and way forward
Key lessons learnt from 25 years of MPFS implementation are grouped below into the following
five categories:
Management and Utilization of Forest Resources and Conserving Biodiversity





Participatory approaches are highly effective for ensuring local commitment, local benefits
and local awareness of plans and processes. They have been applied to forestry programs
and in climate change policies. There is improved growing stock in many forests
(particularly community forests) that have been effectively protected and managed over the
past 25 years. However, they are not being used for value addition, employment generation
and income growth.
A critical factor for the success of CF is that CFUGs and other forest user groups can
operate as autonomous, independent, and self-governing entities. The legislation that
provides this mechanism needs to be ensured in future.
Improved coordination between the primary programs of MPFS is needed. This would lead
to better achievement across all programs. For example, community and private forestry
can supply raw materials for wood and non-wood based industries and they can also
contribute to the conservation of ecosystems and watersheds.
A large part of the government-managed forests lack effective forest management and
stakeholder participation. In fact, they are effectively open-access. Due to political
instability and the lack of rule of law, large parts of the national forests are being converted
to other land uses or are subject to illicit timber harvesting and forest degradation.
DSCWM cannot fulfil the entire demand for soil conservation and watershed management
services. Leveraging services from other agencies also concerned with watershed
management such as forestry, agriculture, irrigation, roads, local development,
environment, and hydropower can synergize soil and water conservation. The DSCWM
needs to re-invent itself from implementer to facilitator.
15

Poaching and illegal trade in wildlife and forest products continues to be a critical issue.
These have been exacerbated by civil unrest and poor rule of law during and after the
conflict. The solution lies in effective management of resources, reducing poverty and
enhancing good governance including enforcement.
 Successes in biodiversity conservation can have adverse impacts on forestry. The
concentration of visitors in certain parts of the PAs and the need to develop associated
visitor facilities is necessary to avoid environmental damage. Improved numbers of certain
species - elephants and tigers - has the downside of increasing human wildlife conflict.
Given this reality, the compensation processes for loss of life or property needs to become
meaningful and more responsive.
 Forest resource information systems and planning need to be improved. Current levels of
forest resource information and data management systems are insufficient for effective and
transparent planning in the forest sector. Data should be disaggregated based on political
and physiographic regions as well as based on forest management regimes. MFSC has too
few qualified staff responsible for updating and analysing such MIS systems. Outsourcing
to private agencies for data generation, analysis, and synthesis can mitigate this shortfall.
 There is a need to balance natural resource conservation with the needs of development.
Roads, hydro-schemes, power-lines, and urban expansion are all necessary for Nepal’s
development. But they also adversely affect forests and protected areas resulting in habitat
fragmentation, higher levels of illicit use, and pressure for over-use of resources and land.
Conservation cannot be tackled in an isolated way through a process of exclusion. Instead,
the only way forward is by involving and informing decision-makers, planners and civil
society in decisions.
Policy and Legal Framework





The policy framework must be backed up by supportive legislation in all interventions and
programs. A deliberative and open policy development process will ensure its
implementation.
Various government orders, directives and regulations are inconsistent with forest policy
and laws. This has particularly affected the wood-based industry, community forestry, and
the national and leasehold forestry program where government restrictions on collection,
transportation and marketing of forest products, and price controls exist.
For investment and effective implementation, a transparent and predictable regulatory
framework and operational environment is essential.
Implications of the Local Self Governance Act (1999) need to be considered. There is a
critical need to engage with local government at all levels to enhance accountability and to
follow the spirit of decentralisation legislation. Inconsistencies between the LSGA and the
Forest Act (1993) need to be removed or clarified.
The application of Environmental Regulations for the forest sector needs to be reviewed as
IEE/EIAs are legally binding for a range of forest management operations. They make
program implementation expensive, time consuming, and the process seems to be
redundant for sustainable forest management.
16
Forest Sector Institutions

A constraint for most programs is a lack of speciality staff. Forestry staffs need to be
trained in technical, managerial, and communication aspects of forestry. As the actual
forest management is gradually decentralized to entities outside the government, the staff
should be more skilful in regulation, monitoring, and facilitation.
 Nowadays many skill areas in forestry are also available outside government institutions.
The sector must promote using them through contractual, service providers, or other
arrangements. This approach can be extended to cover other areas of activity.
 The strongly protection-orientation and command and control attitude of MFSC
administration has not shifted significantly over the MPFS period. These attitudes are
inconsistent with policies, with the increased capacities of individuals, and with the needs
of a modern democratic society. Policy shifts need to be matched by institutional reforms
in the changing context and changes in attitude amongst individuals.
 MFSC staff is overburdened with administrative tasks. The focus for most field-level forest
sector activity lies at the DFO. DFOs have largely become administrators rather than sector
specialists and they are expected to undertake a very broad range of administrative tasks –
often beyond their management capability. This is not sustainable and some functions of
DFOs need to be altered or assigned to other parties to address this issue.
 The sector lacks insufficient political engagement and support. Forest legislation does not
give enough space for local level government leaders and political parties in the decisionmaking process. New institutional mechanisms taking into account the concept of
federalism and power-sharing in natural resource management need to be developed during
formulation of new forest sector strategy.
Forest Sector’s Contribution to Economic Development




Over-regulation is a constraint. Eexcessive regulation on the harvest, transport, process and
sale of forest products is increasing the cost of business. This has increased the transaction
cost and also demotivated communities and private tree owners in managing forests and
trees on farms,
Fiscal policy is a constraint. Revisions of royalties have taken place on a rather ad-hoc
basis is necessary. The present royalty rates for wood are too high, with 13 percent VAT
imposed on timber sales and some NTFPs produced in private land. Meanwhile, there is no
VAT on the production and sales of agricultural commodities thus stifling private
landowner involvement in commercialisation of forest products.
Only comparatively small quantities of forest products are legitimately supplied to industry
from government-managed forests. The overall supply of forest products is far less than
could be potentially produced. Not only does this reduce government revenue, it also limits
the expansion of the wood-using industry and the commercialisation of the forest sector.
TCN has a distorting impact. Although the role and functions of FPDB have been
drastically reduced, the government still gives preferential treatment to TCN for the supply
of timber (logs) at reduced rates. Despite this, TCN is unable to operate on a fully
commercial basis and its role in distorting markets and creating a dis-incentive for private
sector investment is increasingly being questioned.
17

There is a need for a stable regulatory environment to attract investment. The more than
5,000 wood-based industries registered and operating in Nepal face the following
problems: impractical environmental standards, dual taxation, inconsistency in the auction
system, lack of private sector participation in policy-making process, and lack of
transparency in decision-making processes. These problems result in erratic and confusing
regulations, ultimately creating uncertainty and challenges to the growth of wood-based
industries.
 Sources of finance for small-scale forest-based industries are inadequate. Taxation, loan
regulations, and land-related laws are also not favourable for the establishment of smallscale private and community-based enterprises.
 Commercial leasehold forestry is virtually not implemented. The Forest Regulations
(1995), which only focused on improving degraded forest, is to blame for this oversight.
Even where provisions do exist for lease of degraded forest for commercial purposes, for
example eco-tourism, factors such as high annual rental fee act as a disincentive to uptake.
Addressing Poverty and Social Exclusion


The sector provides good opportunities for addressing poverty and social exclusion. A high
percentage of people in Nepal still live in poverty and still depend on forests for their
livelihoods. Experience has shown that there are good opportunities for the forest sector to
contribute to their livelihoods.
Governance is the key to addressing issues around poverty and social exclusion. Local
forestry groups are now becoming more inclusive and pro-poor in the country. The MFSC
GESI strategy attempts to do this amongst MFSC institutions – however many elements
have not yet been implemented.
Nepal’s Climate Change Agenda




The forest sector is critical to Nepal’s climate change agenda. The progress of developing
Nepal’s response to climate change has enhanced public awareness of the important role
that forests play. This is strongly conveyed in Nepal’s NAPA as well as in the strategic
processes being followed for REDD+.
REDD+ is fully compatible with forestry sector goals. REDD+ aims for a healthy and
vibrant forestry sector. Expansion of forest, carbon, soil and watershed conservation
measures using systems for Payment for Ecological Services (PES) to leverage funds is a
potentially viable approach for Nepal. It, however, requires much more action-oriented
piloting and testing.
Local forest groups provide a strong institutional base for community-based adaptation,
planning, and implementation. As inclusive and well-governed local institutions,
community forest groups of various kinds can be effective for implementing actions to
enhance the climate resilience of the most vulnerable households.
Climate change is already affecting Nepal’s forests. These effects include invasive species,
forest fires, changes in forest regeneration and growth, soil and water conservation, floods,
and water source depletion. Although quantitative data is lacking, there is sufficient local
experience to demonstrate these effects at present.
18
Contents
Foreword ................................................................................................................................................................................ 2
Acronyms ............................................................................................................................................................................... 3
Executive Summary ............................................................................................................................................................ 6
Chapter 1: Introduction ......................................................................................................................... 23
1.1 Background..................................................................................................................................................... 23
1.2 Rational and Imperatives of MPFS .......................................................................................................... 24
1.3 Objectives and the Methodology of this Review .................................................................................... 25
1.4 Strengths and Limitations of this Study .................................................................................................. 25
1.5 Structure of this Paper ................................................................................................................................. 26
Chapter 2: The Context of the MPFS ................................................................................................. 27
2.1 International Context ................................................................................................................................... 27
2.2. National Political and Planning Context ................................................................................................ 27
2.3. Prevailing Environmental Discourse ....................................................................................................... 28
2.4. Organizational Culture and Knowledge System .................................................................................. 29
2.5. The State of Forests, Projected Depletion Trend, and Program Design......................................... 29
Chapter 3: Forestry Programs and their Relationships ................................................................. 31
3.1 Objectives and Programs ............................................................................................................................ 31
3.2 Program Relationships and Implementing Mechanism ...................................................................... 33
Chapter 4: Key Achievements and Outcomes of the Primary Programs ................................... 35
4.1 Community and Private Forestry Program............................................................................................ 35
4.1.1 Key Achievements .................................................................................................................................................36
4.1.2 Key Issues and Challenges ..................................................................................................................................39
4.1.3 Lessons Learnt and Way Forward .....................................................................................................................40
4.2 National and Leashold Forestry Program .............................................................................................. 41
4.2.1. Components and Targets .....................................................................................................................................42
4.2.2 MPFS Program versus Implementation Modalities .....................................................................................42
4.2.3 Key Achievements of National Forestry Program .......................................................................................43
4.2.4 Key Issues and Challenges of National Forestry Program ........................................................................46
4.2.5. Key Achievements of Leasehold Forestry Program ...................................................................................48
4.2.6. Key Issues and Challenges of Leasehold Forestry Program ....................................................................51
4.2.7 Lessons Learnt and Way Forward .....................................................................................................................52
19
4.3. Wood-based Industries Development Program .................................................................................... 53
4.3.1. Key Achievements ................................................................................................................................................53
4.3.2. Key Issues and Challenges ................................................................................................................................56
4.3.3. Lessons Learnt and Way Forward....................................................................................................................56
4.4 Medicinal and Aromatic Plants and Minor Forest Products ............................................................. 57
4.4.1 Key Achievements .................................................................................................................................................57
4.4.2 Key Issues and Challenges ..................................................................................................................................59
4.4.3 Lessons Learnt and Way Forward .....................................................................................................................59
4.5 Conservation of Ecosystem and Genetic Resources .............................................................................. 60
4.5.1 Key Achievements .................................................................................................................................................61
4.5.2. Key Issues and Challenges .................................................................................................................................62
4.5.3 Lessons Learnt and Way Forward .....................................................................................................................66
4.6 Soil Conservation and Watershed Management ................................................................................... 67
4.6.1 Key Achievements .................................................................................................................................................67
4.6.2 Key Issues and Challenges ..................................................................................................................................68
4.6.4 Lessons Learnt and Way Forward .....................................................................................................................71
Chapter 5: Review of Supportive and Additional Programs ........................................................ 73
5.1 Policy and Legal Reform ............................................................................................................................. 73
5.1.1 Key Achievements .................................................................................................................................................75
5.1.2 Key Issues and Challenges ..................................................................................................................................85
5.1.3. Lessons Learnt and Way Forward....................................................................................................................85
5.2 Institutional Development Plan ................................................................................................................. 87
5.2.1 Key Achievements .................................................................................................................................................88
5.2.2 Key Issues and Challenges ..................................................................................................................................89
5.2.3. Lessons Learnt and Way Forward....................................................................................................................90
5.3. Human Resources Development ............................................................................................................... 91
5.3.1 Key Achievements .................................................................................................................................................91
5.3.2. Key Issues and Challenges .................................................................................................................................92
5.3.4 Lessons Learnt and Way forward ......................................................................................................................94
5.4 Forestry Research and Extension.............................................................................................................. 95
5.4.1 Key Achievements .................................................................................................................................................96
5.4.2 Key Issues and Challenges ..................................................................................................................................97
5.4.3 Lessons Learnt and Way Forward .....................................................................................................................97
5.5 Planning and Information ........................................................................................................................... 98
20
5.5.1 Key Achievements .................................................................................................................................................98
5.5.2. Key Issues and Challenges .............................................................................................................................. 100
5.5.3 Lessons Learnt and Way Forward .................................................................................................................. 100
5.6 Monitoring and Evaluation...................................................................................................................... 100
5.6.1 Key Achievements .............................................................................................................................................. 101
5.6.2 Key Issues and Challenges ............................................................................................................................... 101
5.6.3 Lessons Learnt and Way Forward .................................................................................................................. 102
5.7. Gender and Social Inclusion ................................................................................................................... 102
5.7.1. Key Achievements ............................................................................................................................................. 102
5.7.2 Key Issues and Challenges ............................................................................................................................... 104
5.7.3 Lessons Learnt and Way Forward .................................................................................................................. 105
5.8 Climate Change and Forestry ................................................................................................................. 107
5.8.1 Key Achievements .............................................................................................................................................. 108
5.8.2 Key Issues and Challenges of REDD+ ......................................................................................................... 109
5.8.3 Lessons Learnt and Way Forward .................................................................................................................. 109
5.9 Financial Allocation in Forestry over Time ......................................................................................... 110
5.9.2 Key Issues and Challenges ............................................................................................................................... 112
5.9.3 Lessons Learnt and Way Forward .................................................................................................................. 113
Chapter 6: Other Factors and Actors Driving MPFS Performance ......................................... 114
6.1 Political Changes ........................................................................................................................................ 114
6.2 Economic Changes ..................................................................................................................................... 115
6.3 Demographic Changes .............................................................................................................................. 116
6.4 International Experiences ........................................................................................................................ 116
Chapter 7: Conclusions ........................................................................................................................ 118
7.1 Lessons Learnt ............................................................................................................................................ 118
7.1.1 Management and utilization of forest resources and conserving biodiversity ................................. 118
7.1.2 Policy and legal framework .............................................................................................................................. 119
7.1.3 Forest sector institutions .................................................................................................................................... 120
7.1.4 Forest sector’s contribution to economic development ........................................................................... 121
7.1.5 Addressing poverty and social exclusion ..................................................................................................... 123
7.1.5 Nepal’s climate change agenda ....................................................................................................................... 124
7.2 Way Forward .............................................................................................................................................. 124
7.2.1 The nature of Nepal’s forestry sector strategy (FSS) ............................................................................... 125
7.2.2 Forestry sector governance and administration .......................................................................................... 125
21
7.2.3 Management of forest resources ..................................................................................................................... 127
7.2.4 Forest sector contribution to economic development............................................................................... 127
7.2.5 Forestry sector contribution to social inclusion and poverty reduction .............................................. 128
7.2.6 Forest biodiversity and environmental conservation ................................................................................ 128
7.2.7 Forestry sector response to climate change ................................................................................................. 129
References ........................................................................................................................................................... 130
Annex 1: Reports Prepared by the Master Plan for the Forestry Sector (MPFS) ............................ 133
Annex 2: Gazette notification on NTFPs..................................................................................................... 134
Annex 3: Ratified/accessed/signature by Nepal in MEAs ....................................................................... 135
Annex 4: Bottom up planning process in the forestry sector ................................................................. 136
List of Tables:
Table 2.1: Forest and shrubland in Nepal ........................................................................................ 30
Table 4.1: The targets and achievements of MPFS on MAPS and other minor forest products ..... 57
Table 5.1: Policy and legal reform strategy of MPFS under six primary programs ........................ 74
Table 5.2: Legal instrument on all forms of national forests ........................................................... 76
Table 5.3: Policy instruments on all forms of national forests ........................................................ 78
Table 5.4: Policy and legal instruments on wood-based industries ................................................. 79
Table 5.5: Legal and policy instruments on NTFPs/MAPs ............................................................. 80
Table 5.6: Legal and policy instruments on watershed conservation .............................................. 81
Table 6.0: Budgetary allocation in different programs of MPFS ................................................... 112
List of Figures:
Figure 3-1: Logical relationship among plan objectives, strategies, and programs ......................... 33
Figure 4.1: Community Forests from 1987 to 2013 (Area, CFUGs, and households) .................... 37
Figure 4.2: Forest use for non-forest and commercial lease purposes ............................................ 36
Figure 4.3: Leasehold forest groups and their area of management over 20 years .......................... 49
Figure 4.4: Timber supplied from various forest regimes and agencies .......................................... 54
Figure 5.1: Comparative study of estimated vs actual MPFS expenditure .................................... 110
Figure 5.2: Share of revenue and expenses from MFSC to GoN ................................................... 111
Figure 6.1: Contribution of industry, service, and agriculture to national economy ..................... 115
22
Chapter 1: Introduction
1.1 Background
The forestry sector contributes significantly to the betterment of the environment, enhances the
livelihood and health of people, is a repository of biodiversity, and furthers the growth of the economy.
The sector has intimate linkages with other sectors such as agriculture, watershed protection, tourism,
and energy including hydropower. Realizing its multifaceted importance, the Ministry of Forests and
Soil Conservation (MFSC) of the Government of Nepal (then His Majesty’s Government of Nepal)
carried out a comprehensive study of the sector starting from early 1986. The study, supported by
FINNIDA and the Asian Development Bank, aimed to revert the accelerated deforestation and
degradation of land with all its associated impacts. It took three years to prepare the Master Plan for the
Forestry Sector (MPFS). The government approved the MPFS in 1988. The plan, which had an
implementation period of 25 years including three years for preparation, came to an end in 2011.
The MPFS became a vehicle in the paradigmatic shift of the forestry sector in Nepal. It recommended
the mobilization of communities and the private sector in the conservation, management, and utilization
of forest resources in a larger scale than stipulated in previous plans and policies. Though the plan was
designed during the phase of ‘guided democracy’, the restoration of multi-party democracy in 1990
expanded the role of local communities in combating the process of forest depletion. The growing
international concerns over rapid deforestation and degradation in tropical countries were also a driving
factor in the management of Nepal’s forestry sector. Consequently, the strategic framework of the
Tropical Forest Action Plan helped in mobilizing resources to prepare the MPFS.
The MPFS was centered around five strategies: production and utilization, conservation of ecosystem
and genetic resources, forest decentralization to communities and livelihood promotion, private sector
involvement, and policy implementation. These strategies were intended to balance the demand and
supply of forest products as well as to conserve ecosystems and watersheds. The major thrust of the
MPFS was to transfer forest management authority from the forest administration to the local
communities. The role of forest officials was to be advisers to forest management groups. The total
proposed outlay of the MPFS was USD 1,742 million. Of this total, 46.6 percent was allocated to the
Community and Private Forestry program and 20.2 percent to the National and Leasehold Forestry
program. The remaining outlay was distributed between ten other programs, for example in conserving
the ecosystem and genetic resources. While community forestry was the priority program, the leasehold
forestry program was designed to solicit private sector investment. Meanwhile, the government was to
invest in managing the remaining national forests.
There were two objectives, related to each other, in preparing the MPFS. :

Identify priority programs, implementable proposals, and estimates of investment needs for 25
years. All these details were to be included in the ongoing and subsequent periodic plans to be
formulated by the National Planning Commission (NPC).

Develop planning, project formulation, monitoring and evaluation, and donor coordination
functions for the MFSC in order to enable the ministry to implement the master plan proposals
included in its framework of annual plans.
23
1.2 Rational and Imperatives of MPFS
The National Forestry Plan of 1976 had realized the need to reverse the process of forest degradation
and deforestation in Nepal through various interventions including people’s participation in forest
management and utilization. However, the then government was reluctant to decentralize forest
management to the forest users. Instead, it only gave superficial management rights to the local political
bodies. As a result, forest depletion and soil erosion continued at an accelerated scale. It was in this
context that the need for a long-term MPFS, based on detailed analysis of the situation, was felt. The
three year planning exercise of the MPFS was focused on analyzing the situation, synthesizing
prevailing and projected trends, and formulating new policies and programs to meet the ongoing and
future needs of the country.
The MPFS prepared 13 reports (see annex 1), including six primary and six supportive programs for
intervention. It also produced one report projecting land use changes as well as the accompanying
demand and supply scenarios of the main forest products (timber, fuelwood, and fodder) over time. The
projected forestry scenario under different trends (current, moderate, and optimistic) provided the
rational for setting the objectives and designing the 12 forestry programs under the MPFS. The plan also
highlighted the importance of continuity in planning as a process rather than preparing a planning
document. The necessity of building the capacity of agencies involved in the MFSC to plan and
implement activities was also highlighted.
The MPFS identified four imperatives to develop the forestry sector:

Satisfaction of basic needs: Forests resources are required to fulfill basic survival needs. This
includes fuelwood/charcoal as a source of energy for households and industries, timber for
building construction, fodder for animal husbandry, herbs for human health, protected areas for
tourism promotion, and watershed management for maintaining agricultural productivity as well
as to prevent natural hazards.

Sustainable utilization of forest resources: To ensure the sustainable use of the essential forest
resources noted above, the MPFS states that these products should be used within their carrying
capacity. This limitation is also necessary to protect watersheds, prevent soil erosion, conserve
biodiversity, and ensure a sustained supply of forest products.

Participation in decision-making and sharing of benefits: Local community participation in
forestry management is required to reduce the concentration of government power, to expand
opportunities for local residents, and to generate enthusiasm for forest protection among the local
communities. This also entails bringing decision-making power to the forest users’ level so that
they themselves benefit from their improved management, harvesting, and plantation efforts.

Socio-economic growth: Multiple contributions from the forestry sector should be streamlined
to provide maximum benefits to local and national economies. Special provisions should be
made for the poorest segments of society.
These strategies and imperatives have been the basis of the 12 forestry development programs
implemented in Nepal. These programs are designed to interact with each other so as to bring synergetic
impacts in the field.
24
1.3 Objectives and the Methodology of this Review
The team guiding this MFSC review began by carrying out a thorough review of past forestry sector
policies, programs, and the previous MPFS. This was necessary to understand changes in political and
social priorities as well as the current context of environment protection and climate change. Based on
this review, and with the expiry of the previous MPFS in July 2011, the MFSC review team has realized
the need for a new forestry sector strategy. It is in this context that this study is being carried out. The
specific objectives of this study are:

To document the achievements, challenges, and lessons learned from the previous MPFS.

To identify what worked, what did not work, what could be improved, what was missed, and
factors affecting successes and failures from 25 years of the implementation of MPFS.

To make a critical analysis of the relevance of the themes and approaches outlined by the earlier
MPFS in the changed socio-political, economic, and environmental context.

To gather lessons learnt with the aim of using the knowledge in preparing a new forestry sector
development strategy for the coming 10 years.
This review of the MPFS comprised of at least three components. The first component consisted of
consultations with a variety of stakeholders – frontline staff, civil society and academic institutions,
forest entrepreneurs, mid-level forest professions, and policy makers – in the capital and the regions.
There were also a series of consultations by the Federation of Community Forest Users of Nepal
(FECOFUN) team and the Gender, Equity, and Social Inclusion (GESI) team from the grassroots level
in the field to the center in Kathmandu. Their feedback on the performance of the forestry sector over
the past 21 years was illuminating and invaluable for this review. The second component comprised of
desktop reviews of all 12 MPFS programs as well as of two other programs, namely forestry and climate
change as well as gender equity and social inclusion. The latter two have emerged over the last decade.
The reviews were also enriched by the international experiences that have evolved over the last two
decades. These desktop review documents were further improved through peer review by Nepali
experts. The third component comprised of informal discussions and dialogues with representatives of
professional groups, NGO staff, and government officials.
Two major deliverables will emerge from this study. First, an analysis and synthesis of emerging
forestry and related issues will be prepared. Second, and most importantly, this study is the foundation
for the preparation of a new forestry sector strategy.
1.4 Strengths and Limitations of this Study
The MPFS document had suggested the need to periodically review the master plan so as to take
corrective measures to streamline forestry programs and activities in the changing context. However, no
review of the past performance of MPFS has been undertaken. The only exceptions are the assessments
of the forestry sector undertaken by the National Planning Commission (NPC) during the formulation of
new periodic plans. Thus, this review is the first comprehensive assessment of the achievements and
challenges of the MPFS programs, institutions, and policies. The review is partly based on information,
documents, and data gathered from a range of government sources as well as the institutional memory of
25
various individuals including the team members of this review. A wealth of information was also
generated through consultations with multiple stakeholders active in the management and promotion of
the forestry sector in Nepal.
Despite the cooperation of government and non-government actors, the review team faced some
difficulties in gathering information, outcomes, and relevant literatures. The single greatest barrier to
information was the long time period of over 25 years; soliciting views from stakeholders spanning over
two decades was a daunting task. The team took four months – rather than the initially planned two
months – to complete this review because of difficulties in gathering reliable and credible data. The
challenges in data collection were threefold: the large scale and complexity of the programs, the fact that
the programs were implemented in silos but impacts had to be considered in an integrated manner, and
the difficulty in measuring program effectiveness and impacts.
1.5 Structure of this Paper
This study is divided into seven chapters. After the introduction, the second chapter deals with the
national and global scenario in which the plan was prepared. The third chapter presents the MPFS
programs, their relationships to each other, and the institutional modalities used to implement them. The
fourth and fifth chapters form the core of the study. These two chapters analyze and synthesize the key
achievements and outcomes along with the underlying incentives/factors driving the programs. The sixth
chapter highlights the political, economic, and demographic trends of Nepal over the past decades,
which have a significant bearing on the implementation of forestry programs. Chapter six also presents
the international trend in forestry, which partially influenced forestry in Nepal. The final chapter
concludes with major learning from the review and implications or future directions useful for preparing
a new Forestry Sector Strategy (2014-2024) for Nepal.
26
Chapter 2: The Context of the MPFS
The MPFS design was a coming together of different contexts prevailing within the country and outside,
also keeping room for future scenarios generated through simulation models. These prevailing contexts
were formed through the confluence of several factors – international initiatives, the political context,
national goals of the Seventh Periodic Plan, environmental discourse, and organizational culture.
2.1 International Context
The destruction of tropical forests drew international attention beginning in the 1980. The ongoing
depletion was considered a threat to the very existence of global commons such as biodiversity and
climate. The Tropical Forest Action Plan (TFAP), later renamed Tropical Forestry Program, was agreed
upon in 1985 as an international framework for forest-related action after its adoption by the World
Forestry Congress in Mexico. It was also agreed that TFAP needed to be translated into national
programs based on national priorities and development plans. Thus, the MPFS was prepared in the
context of TFAP but based on Nepal’s priorities and development challenges. The TFAP was launched
with the following objectives:

To increase awareness of the problems of deforestation and to mobilize all relevant stakeholders
in order to address them.

To introduce inter-sectoral planning approaches involving all relevant partners to stimulate
generation of more effective policies and programs.

To mobilize national and international resources to assist in the preparation and implementation
of National Forestry Action Programs (NFAP) in a coordinated manner
The TFAP identified five areas of inter-sectoral priorities: forestry in land use, forestry based industrial
development; fuelwood and energy, conservation of forest ecosystems, and institutional development.
The process was to enable wider participation of major stakeholders and also to build national capacity
to implement programs. The TFAP provided a rational to formulate the MPFS in Nepal.
2.2. National Political and Planning Context
The Panchayat polity, with constitutional and political power vested in the king, did not allow political
parties to function. The ‘control and command’ nature of forest administration was not able to stop or
reverse the process of forest depletion. There were, however, pressures on the polity to decentralize and
liberalize the economy to improve forest management. The state was in a dilemma – should it
decentralize forest management or should it retain central control. The easy solution, to appease both
pressure groups, was for the state to decentralize forest management to the local political units (village
Panchayats), which were controlled by the center. Thus, the concept of Panchayat and Panchayat
Protected Forests were incorporated in the National Forest Plan of 1976, and ultimately included in the
Forest Act.
Lessons learnt from the pilot forestry project funded by the Australian government showed that forests
could be more effectively, equitably, and efficiently managed by the local communities than the local
Panchayats. Furthermore, the Decentralization Act of 1982 and its regulations were used to involve the
27
local users’ groups in the management of forest resources. The Panchayat system was under intense
pressure to democratize the political process towards the end of the master planning process. As a result,
the then government agreed to operationalize the concept of users’ group in the management of forests
as well. Once the Panchayat system was overthrown in 1990, it became easier to legalize community
forestry; forest users groups were formed in 1993 and regulation began from 1995.
The Seventh Five-year Plan (1986-1990) of Nepal pledged to meet the basic needs – food, housing,
clothing – of the Nepali people by the year 2000. This was the mandate given by the king to the
government. Accordingly, every sector was compelled to design programs and strategies to meet basic
needs within this timeline. The MPFS, thus, was geared to meet the needs of fuelwood (for cooking
food), timber (house construction), fodder (for livestock), and medicinal and aromatic plant products
(for health). Soil and water conservation was also linked to maintain or enhance the productivity of both
upstream and downstream land as well as to help in food production. Ecosystem and genetic resource
conservation was linked to promote ecotourism and maintain a healthy environment. Similarly, woodbased industries were designed to produce panel and furniture products for household and commercial
purposes. Alongside, they were also intended to provide productive employment and to generate
revenue for the government. As the overwhelming majority of people lived in the rural areas where the
economy was subsistence based, the community forestry program was designed to meet the subsistence
needs of the rural people through forest products. Meanwhile, the national and leasehold forestry
program was designed to produce timber, fuelwood, and non-timber forest products (NTFPs) for
commercial purposes.
2.3. Prevailing Environmental Discourse
Starting in the 1970s, there was an intense national and international environmental discourse on
accelerated deforestation in the hills of Nepal. These discussions focused particularly on the adverse
impact of soil erosion in Nepal, and neighboring Bangladesh. The World Bank postulated that if the
same trend of deforestation continued in Nepal, the mid-hill forests would be depleted within 25 years
and the Tarai forests within 15 years. This logic was based on the declining supply of fuelwood due to
continuous forest degradation and deforestation as well as increasing harvesting of forest products to
meet the needs of the increasing population. The suggested ‘gap analysis’ between the demand and
supply of wood products became the guiding mantra for expanded tree plantation programs in barren
mid-hill land. The ‘gap analysis’ later became the “Theory of Himalayan Degradation”. Under both
these theories, the poor rural households of the mid-hills were characterized as the culprits responsible
for land degradation and soil erosion in Nepal. The suggested remedy was a technocratic one; carrying
out massive afforestation and reforestation through the Department of Forests.
The experiences and lessons of the pilot forestry project implemented in Sindhu and Kavre districts had,
however, already disproved the efficacy of these technocratic strategies. Carried out in the 1980s, these
pilot projects had demonstrated that forest rejuvenation occurred most quickly and effectively if the
local people were empowered to protect and utilize the forests through rules designed by the community
itself. Thus, the key strategy to increased forest greenery was to trust the local people, authorizing them
to protect, manage, and utilize the local forests they accessed. In addition to being effective, this
institutional innovation for expanding greenery could be widely replicated in the mid-hills of Nepal.
This model of forest rejuvenation and expansion sharply countered the “Theory of Himalayan
Degradation”. This decentralized model gradually came to be adopted as the new paradigm of forest
28
management though community mobilization and empowerment. This approach was adopted by the
MPFS as the priority program of forest management in the mid-hills of Nepal.
2.4. Organizational Culture and Knowledge System
The organizational and administrative culture of Nepal’s forestry sector was influenced by the systems
existing in India. Indeed, India’s practices were often simply superimposed onto Nepali society. This
system was based on control and command as well as revenue and rent collection. Forest management
entailed state ownership of forests and its management by foresters employed by the state. A system of
permits and licenses issued as well as regulated by the forest officials was legally enforced. However,
because the rules were so rigid and divorced from reality, they were essentially disregarded by the local
users. People were afraid of forest officials. And the hierarchical nature of the forest administration
system prevented forest officials from trusting the local people.
Reforming the organization culture to close the trust deficit between foresters and users was a key
requirement to ensure better forest management. A reduction in the trust deficit would allow both the
indigenous knowledge of the local people and the scientific knowledge of the foresters to guide
management strategies. A new culture of relationships and responsibilities had to be reinvented between
the forest staff and the people. Thus, the reforms could not only include transferring forests management
to local forest users. Rather, a true reform process required a radically different understanding of what
constituted appropriate knowledge of the forest. This required changing the role of forest officials to
forest advisers rather than forest managers. To reconfigure these new roles, the forestry staff had to be
retrained. Alongside, the forest user groups’ capacity to undertake these new rules had to be
strengthened. The reinvention of forest administration and CFUGs had to be synchronized to have a
synergetic impact on forests and local people. These imperatives were considered vital even by the
forest officials. They were, thus, included in the MPFS.
2.5. The State of Forests, Projected Depletion Trend, and Program Design
The forest area of Nepal has declined over the last six decades as shown in table 2.1. In 1964, the Forest
Survey and Research Office (FSRO) estimated the forest- and shrubland area to be 45.5 percent of the
total national land. Based on the forest area reported by the Land Resource Mapping Project (LRMP) of
1978/79, the MPFS estimated the forest and shrubland area of Nepal to be about 42 percent. As per the
National Forest Inventory carried out through the Department of Forest Research and Survey (DFRS),
the annual deforestation rate of Nepal was estimated to be 1.7 percent during the period from 19781991. Similarly, the rate of deforestation in the Tarai was estimated to be about 1.3 percent within the
same period. However, a study conducted by DoF in 2005 shows that the forest cover in Tarai districts
as a whole has decreased by an annual rate of 0.06 percent from the period 1990/91 to 2000/2001 (DoF
2005). The recent forest inventory carried out by the Department of Forest Research and Survey shows
that the forest area in plain Tarai of 18 districts has decreased by 32,000 ha with an annual rate of 0.4
percent in the last 19 years from 1991 to 2010. Similarly, the forest area in the same region has
decreased by 16,500 ha with annual rate of 0.44 percent in the last nine years from 2001 to 2010.
(FRA/DFRS, 2014)
The table 2.1 shows that forests cover in Nepal has declined over the last six decades. Importantly, it
also shows that there has been an increase in the degradation of forests over time – the rate at which
29
forests are converted into shrub land has increased. Based on the past trend of deforestation and
degradation across Nepal, it was reasonable to assume that deforestation rates would rise with the steady
growth in population. To meet the growing needs of forest products, MPFS projected three scenarios to
develop forestry programs in Nepal: the current trend or the business as usual scenario (BAU), the
medium term scenario, and the optimistic scenario. As per this analysis of Nepal, under the BAU
scenario, for example, the biomass fuelwood deficit would peak at about 3 million Tons (T) in 1995/96.
This would, however, gradually reduce to a deficit of 1.4 million T in 2010/11. As a result, the forest
land use would reduce from 6.67 million ha in 1985/86 to 5.59 million ha in 2010/11.
Table 2.1: Forest and shrubland in Nepal
Report produced by
Year
Forest
Shrub
Total
000 ha
%
000 ha
%
000 ha
%
FSRO
1964
6402
45.5
-
-
6402
45.5
LRMP
1978/79
5616
38.1
689
4.7
6285
42.8
HMG/N (MPFS)
1985/86
5424
37.4
706
4.8
6210
42.2
DFRS (NFI)
1999
4268
29
1560
10.6
5828
39.6
Sources: FSRO 1967; LRMP 1986; HMG/N 1989; DFRS/FRISP 1999
Under the moderate trend scenario, the fuelwood deficit would peak at 2.7 million T in 1990/91. There
would, however, be an overall surplus of 3.2 million T in 2010/11, with a caveat that there would be a
fuelwood deficit of about 370,000 T in the Tarai. This scenario would lead to a change of land use in
Nepal, leading to about 5.8 million ha under forest cover in 2010/11. The forest area would further
increase to about 5.9 million ha by 2010/11 under the optimistic scenario. The scenario analysis was
carried out to ensure that distinct forestry programs reinforced each other rather than worked in
isolation.
At present, there are no up-to-date macro-level forest/land use change data available in Nepal. However,
recent micro-level data based on watersheds or on individual districts suggest that forest area is
increasing in the mid-hills and in some cases in the mountains. This change is attributed to the
community forestry program, demographic shifts, cash infusion from remittances, and changes in energy
use pattern (Profor 2013, Niraula et al. 2012, Kanel et al. 2012, Gautam et al. 2003).
The composition of the forest management regime has changed significantly over the decades. Less than
30,000 ha of forests were managed under community forestry principles in 1985. By the end of 2013,
the area under community forestry has expanded to 1.7 million ha. Similarly, about seven percent of the
total forest was under the protected area system during the time the MPFS was prepared. Now, the area
is about 23 percent of the total area of Nepal, about 12 percent of the total forest area of Nepal.
Similarly, other forest management regimes (such as CFM, pro-poor leasehold forests, protected forests,
and religious forests) have also expanded over time.
30
Chapter 3: Forestry Programs and their Relationships
The MPFS developed four long-term and three medium-term objectives in order to conserve,
manage, and utilize forests as well as watershed areas. It was hoped that these forests along with
wood-based and Medicinal and Aromatic Plant products (MAP)/NTFP-based enterprises would
broaden inclusive development in Nepal. Six primary and six supportive programs were designed
to meet these objectives, listed below.
3.1 Objectives and Programs
The four long-term objectives included:

To meet the people’s basic need for fuelwood, timber, fodder, and other forest products on
a sustained basis while also contributing to food production through an effective interaction
between forestry and farming practices.

To protect the land against degradation through soil erosion, floods, landslides,
desertification, and other effects of ecological disturbance.

To conserve the ecosystems and genetic resources.

To contribute to the growth of local and national economies by managing forest resources
and developing forest-based industries, thus creating opportunities for income generation
and employment.
The three medium-term objectives included:

To promote people’s participation in forestry resource development, management, and
conservation.

To develop the legal framework needed to enhance the contribution of individuals,
communities, and institutions to forest resource development, management, and
conservation.

To strengthen the organizational framework and develop institutions of the forestry sector
to enable them to carry out their missions.
The six primary programs included:

Community and Private Forestry: This program is aimed at developing and managing
forests through the active participation of household members and communities.
Supporting the communities in meeting their basic needs is a key concern of the program.

National and Leasehold Forestry: This program is aimed at developing and managing
national forests through government agencies or by leasing forests to the private sector.
This program is intended to complement community and private forestry as well as to
supply raw materials for forest-based industries.
31

Wood-based industries: This program is aimed at processing and adding value to wood
needed by people. In turn, the value-added is intended to contribute to income generation,
employment opportunities, and increases in the national revenue through industrialization.

MAPs and other minor forestry products: This program is aimed at increasing the
supply of MAPs and other minor forest products. Once harvested, these resources are
converted into products for distribution to domestic and foreign markets.

Soil conservation and watershed management: This program is aimed at protecting the
land against degradation through preventive, rehabilitative, and conservation measures.

Conservation of ecosystems and genetic resources: This program is aimed at protecting
and managing special areas for their ecosystem and genetic resource values. These special
areas are also intended for the provision of amenities as well as for promoting in-situ and
ex-situ conservation of genetic resources of plant and animals.
The six supportive programs included:

Policy and legal reforms: This program is aimed at developing and implementing policy
and legal frameworks to facilitate and enhance the contribution of individuals,
communities, and institutions to forest resource development, management, and use.

Institutional reform: This program is aimed at strengthening the organizational
framework in the forestry sector for more efficient implementation and service delivery in
the priority areas.

Human resources: This program is aimed at developing and managing the capability of
human resources in the forestry sector.

Research and extension: This program is aimed at strengthening research, bolstering
extension and public information capabilities, and promoting the utilization of research
results.

Resource information and planning assistance: This program is aimed at developing a
forest resources information system within the line ministry. Alongside, this program aims
to build the capability of the line ministry to conduct surveys, take inventories, and
undertake other information-generating activities. In the long term, these activities will
lead to better use of information as well as more efficient operational planning by the
government, users, and other stakeholders.

Monitoring and evaluation: This program is aimed at institutionalizing a system for
monitoring operations and their impacts as well as for processing monitoring data into
information to guide the development process.
The supportive programs were designed to complement the main programs. Each of the supporting
programs had to assist the effective implementation of the main programs. Supporting programs
also had to complement one another. For example, the national and leasehold forestry program had
to produce and supply forest products needed for the expansion of wood-based industries. Forests
32
under the community and private forestry program as well as under the national and leasehold
forestry program had to contribute to the conservation of the ecosystem and genetic resources.
3.2 Program Relationships and Implementing Mechanism
The programs were designed in a logical framework. Their interdependencies and relationships are
shown below in a schematic diagram (Figure 3.1).
Figure 3-1: Logical relationship among plan objectives, strategies, and programs
33
The implementation of the programs was also considered from the perspectives of the forestry
organizations designed to implement them. For example the community and private forestry program
and the national and leasehold forestry program were implemented through the Department of Forests.
The Department of National Parks and Wildlife Conservation had the primary responsibility for
implementing the conservation of ecosystem and genetic resources program. The Department of Soil
Conservation and Watershed Management (DSCWM) was responsible for the implementation of the soil
conservation and watershed management program. Meanwhile, the wood-based industries development
program was led by the private sector, while the government was tasked with creating a conducive
policy and operational environment. Similarly, MAPs and the NTFP program were implemented partly
by the DoF, partly by the Department of Plant Resources (DPR), and partly by the private sector and
parastatal organizations. The first three supportive programs were led by the MFSC. Separate entities
were created to implement the other three supportive programs in a coordinated manner.
In designing these 12 programs, the MPFS intended to create a complementary relationship among the
programs. The MPFS intended for these relationships to occur both conceptually and in implementation,
with the respective lines agencies taking a coordinated approach. In reality, the different departments
and divisions implemented the program in ‘silos’ without much synchronization. Moreover, the
restructuring of the ministry in 1995 weakened the implementation capacity of the forest organizations.
The donor community played a constructive role in the design of the MPFS as well as in the
implementation of certain programs, including community forestry. Overtime, however, donor support
changed to a project modality. As a result, parallel donor structures with direct funding of activities
became the norm. Donors argued that these parallel structures allowed funds to flow more quickly and
expedited the field implementation process. Yet, donor funded projects/programs had to encounter two
different sets of bureaucracies – Nepali and foreign. In essence, donors were unable to evade the Nepali
bureaucracy but were able to disburse funding through project modality without channeling it through
the national treasury.
Donors also had their own priorities and interests, at times diverging from the national priorities, in
funding the implementation of the programs. For example, donors were attracted to successful programs
such as community forestry. Other programs, for instance the national forestry program, were excluded
by donors. Imbalance in donor support to both programs and geographical areas such as the Tarai, the
Chure range, and the high mountains also led to low levels of implementation.
The MPFS was also poor in terms of geographical balance; while it was visionary in its focus on
community forestry in the mid-hills, it excluded the Tarai almost completely. Indeed, the MPFS does not
even touch upon how the government would manage the national forests of the Tarai when it had
previously faced so many hurdles in this area. The management of national forests leased by the private
was also not clearly articulated in the plan. This was a major weakness considering that the leased
forests enhanced supply of forest products for forest-based industries. The provision of pro-poor
leasehold forestry was not mentioned in the MPFS, and this program was crafted subsequently. Overall,
the implicit assumption of the MPFS appears to have been that the situation in the Tarai was too
complicated (such as regulations and competition for land use) for more creative management systems.
Forests had to be managed by the government or the private sector. For example, complications
appeared in the piloting of the Bara forestry project – an experiment in leasehold forestry where the
program was to be implemented as a joint venture between three Nepali firms and one Finnish company.
The problems were largely caused due to the exclusion of the local community during the
implementation phase. Eventually, the project could not take off.
34
Chapter 4: Key Achievements and Outcomes of the Primary Programs
This chapter presents key achievments and challenges as well as the way forward based on the lessons
learnt from each of the six primary forestry programs and the additional programs on gender/inclusion
and climate change.
The MPFS intended to achieve the seven following goals:

Increase forest handover for local management, mainly in the mid-hills.

Forest restoration to reverse the rate of degradation.

Improve forest management and utilisation.

Conserve biodiversity and ecosystems both in-situ and ex-situ.

Increase employment opportunities.

Increase income and revenue generation.

Improve people’s living conditions as well contribute to fulfilling their basic needs.
The MPFS estimated that 60 percent of national forests, approximately 1.8 million hectares of land,
mainly in the mid-hills would be brought under local management. It was expected that this process
would restore forest cover including on private land. Alongside, better soil conservation measures in the
watersheds were planned. As a result, there would be minimum negative effects on agricultural land and
ownership structure. The MPFS predicted that there would be at least a 34 percent increase in
sustainable fuelwood production, 57 percent in timber production, and 39 percent in fodder production.
Increased employment, a jump of at least 47 percent, from the baseline number of 1989 was also
envisioned. The estimated figure was 2.5 million persons with full time jobs each year. The MPFs stated
that approximately NPR 23,900 million of additional income at current prices (1988) would be
generated with increased forest-based industries and enterprises. This would lead to a better quality of
life for the rural people, especially lower income groups, through the increased availability of forest
products and better amenities from the protected areas. Meanwhile, networks of national parks and wild
life reserves would contribute to conserving plant and animal genetic resources.
4.1 Community and Private Forestry Program
The MPFS, which was approved by the then HMG in April 1989, had the following main components:

Enrichment and management of natural forests.

Establishment and management of community forests in open and degraded areas.

Encouragement to people to reduce the consumption of fuelwood by using improved cook-stoves
and adoption of biogas.
35

Distribution of seedlings to expand the establishment of private tree farms.
The MPFS projected the management of 1.28 million ha of community forests and the establishment of
about 325,000 ha of tree farms in private land. These programs would lead to the production of 11.25
million tons of fuelwood, 2.34 million cubic meter of timber, and 5.5 million tons of fodder for
livestock. Moreover, about 753,000 improved stoves would be adopted to reduce fuelwood consumption
by 5.8 percent. Similarly, instalment and use of 154,000 biogas plants would reduce the consumption of
fuelwood by 0.6 percent. Of the twelve programs formulated in the master plan, the community and
private forestry programme was identified as the priority program. The largest share (46.6 percent) of
financial resources was allocated to this program, out of which about 59.4 percent would be borne by the
communities and private sector.
4.1.1 Key Achievements
“If the present trends continues, 0.6 million hectares of Nepal’s natural forests will be lost during the
next 25 years, plunging the nation deeper into the vicious cycle characterized by a widening gap
between demand and supply, and by the destruction of the supply base in trying to meet the inmediate
needs”.
This is a quote extracted from a paper presented by the late Rabi B. Bista, then Chief Planning Officer of
the MPFS, during the donors’ meeting held on 30 August 1989 in Kathmandu to announce the launching
of the MPFS. Nepal’s forests did not, however, follow the trend mentioned above. Rather, forests in the
mid-hills grew, deforestation was reversed, and degradation stopped. Community forests covered an
area of about 57,000 ha during 1988. By the end of 2013, a total of 1.7 million ha of national forests has
been handed over to 18,133 CFUGs with a membership of about 2.24 million households (figure 4.1).
Of the total, 65.5 percent of the forests in the mid-hills had been handed over to local groups, covering
64.7 percent of the mid-hills households. A study by LFP shows an additional 2 M3 of wood production
per ha per annum from the community forests of the mid-hills as calculated over a period of 14 years
from 1994 to 2008. An estimate of the supply of wood products shows that about 6 million tons of
fuelwood, and about 2.2 million M3 of timber was effectively supplied from community and private
forests in 2011 (Kanel et al. 2012).
The living standard survey carried out in 2011 shows that the percentage of household fuelwood
collectors from community forests has increased from 12 percent in 1995/96 to 44 percent in 2010/11.
Similarly, the percentage of fuelwood collectors from private forests has increased from 19 percent to 24
percent during the same period. By the end of 2013, 700,000 improved stoves and about 228,000 biogas
plants had been installed and were operational. Both of these programs helped in reducing the
consumption of fuelwood in the rural areas of Nepal. Households have also moved collecting fodder
from government forests to community forests. For example, about 10 percent of fodder collectors used
to collect from the community forests in 2003/4. The number increased to 17 percent in 2010/11. (CBS
2011).
Forestry in Nepal is today in a healthy state. This claim is backed by people’s perceptions, office records
of groups’ operational plans, and a range of government reports. Indeed, government progress and
projects’ evaluation reports indicate increases in forest density, regeneration, species diversity with more
wild plants and animals, increased volume of water springs with more volume, and better soil nutrition
and moisture during dry season to name just a few positive signs. Alongside, there has been a decrease
36
in the number of forest fires, reduced grazing pressure, a drop in encroachment of forest land, and
reductions in the illegal felling of trees. Significantly, the number of complaints and forests offences
reported to the DFO office has decreased noticably. Significant achievements have been made in
increased representation of women and marginalized groups in user group committees. There has also
been an increase in the number of trained human resources and service providers at the village level.
There has been phenomenal increase in the awareness and sensitivity of forestry officials, nongovernment service providers, and local community members on the need for positive discrimination.
There is an increased trend of pro-poor provisions in group decisions regarding funding and forest land
allocation.
Figure 4.1: Community forests from 1987 to 2013 (area, CFUGs, and households)
The pro-poor policies can be attributed to the practice of carrying out social mobilization through
community forestry, which led to the proliferation of grassroot CFUGs. These groups not only protected
and utilised the forests, but also provided a platform for developing leadership and resolving conflicts.
The CFUGs continued to be active even when the country faced a 10-year long armed insurgency. In
1995, FECOFUN, an umbrella group established to lobby for the rights of CFUGs members, was
formed. Today, FECOFUN also plays a crucial role in networking between CFUGs, NGOs, forest
offices, and political parties.
37
Despite its many successes, the community forestry program has had a poor record in employment
generation. Though a huge potential exists, a CFUG has generated only 2 person years of employment
on average, which is only 36,000 person years in total (MFSC, 2012)1. This is much lower than the
numbers envisioned in the MPFS: 2.5 million person years of full time jobs in total by the sector with
community and private forestry expected to generate half these jobs. That would, however, amount to 34
times more than the current rate at which community forestry creates jobs. Most of the contributions of
community and private forests are, however, found to be in terms of non-monitised value. These
contributions take the form of undervalued or non-priced goods and services as well as in the formation
of social capital and democratic practices at the grassroots level. Indeed, community forestry has
become a catalysts for gender equality, social inclusion, and pro-poor practices in the forestry sector.
The inability of community forestry to kickstart employment and industries may be a function of
structural changes in the Nepali economy. In 1988, 60 percent of Nepal’s total GDP came from
agriculture, forestry, and fisharies. In 2013, these sources contributed to 33 percent of the total GDP. In
the intervening decades, the economy became market- and cash-driven. Similarly, people’s dependency
on forests for fuelwood and fodder has significantly changed over time. For example, the percent of
people using LPG as household energy has increased from virtually none in 1988 to about 18 percent in
2011 (CBS, 2011).
Based in the economic structure of the 1980s, the MPFS did not foresee the commercial sale of forest
products outside the CFUGs. However, timber sale outside the groups for commercial purpose has been
one of the main sources of wood for forest-based industries in Nepal. An analysis of the timber supply
from community forests to the market (outside CFUGs) in the fiscal year 2009/10 shows that a
maximum of about 164,000 M3 of round wood timber was supplied from 2,324 CFUGs. This constituted
about 58 percent of the total timber supply. Private tree owners contributed to about 27 percent of the
total market supply. The remaining 15 percent was supplied from the government-managed forests.
The trade in timber is a significant source of government revenue. CFUGs, for example, have to
contribute 13 percent VAT to the government on the external sale of timber. In 2009/10, the government
earned NPR 68 million simply in VAT paid for timber sales. This suggests that the CFUGs generated
total revenue of NRs 523 million from surplus timber sales. In the same fiscal year, the government also
collected an additional NPR 56 million charging 15 percent tax on the sale value of Sal timber and Khair
wood as per a revenue-sharing arrangement with the CFUGs. Thus, the government in total collected
about NPR 124 million from the CFUGs. The CFUG generated NPR 515 million from the commercial
sale of timber from community forests to the market in the fiscal year 2009/2010. The total government
revenue in the same fiscal year was about NPR 411 million from the sale of forest products obtained
from the national (government-managed) forests. There is no reliable data on income from the sale of
forest products within the group. However, it can be estimated that at least the double of the value CF
timber sales (valued at market price) in the market is distributed among the CFUG members for their
own consumption. Therefore, the total value of timber extracted from CF in 2009/2010 comes to about
NPR 1.5 billion, which is at least three times higher than the government revenue from the sale of forest
products from government managed forests.
1
http://www.msfp.org.np/uploads/publications/file/ebook_interactiv_20130517095926.pdf
38
There is also a massive trade in timber from private plantations. The latest survey shows that about
about 55,000 ha was under compact private treee plantations in 2011 (CBS 2013). It was only 27,000 ha
in 2001. In addition, trees on farmland have significantly increased and forests in abandoned agricultural
land have also expanded over the years. This expansion may not necessarily be due to the community
and private forestry program. It may be because of youth migration for labor, cash flow into the village,
increased opportunities to sell tree products due to the expansion of road networks, scarcity of domestic
labor, and low incentives for farmers to continue in subsistence agriculture
Many of the achievements mentioned above reach far beyond the expectations and imagination of the
MPFS. For example, despite limited support from the government and donors, the supply of wood and
commercial timber from private land has increased tremendously in recent years. The management and
use of community and private forests have gone beyond basic needs. Geographically speaking, the
community forestry program has been expanded into the Tarai and mountain regions; about 19 percent
of national forests in the Tarai are now under community forests and 22.1 percent of households are
CFUG members. Similarly, 16 percent of national forests in the mountains have been handed over to 13
percent of the region’s population. The mountains and other remote parts of the country do still,
however, have areas that could be transformed to community forests.
4.1.2 Key Issues and Challenges
It can be said that the community and private forestry programme has achieved its institutional and
environmental objectives. It has failed, however, in achieving the economic objectives of job creation
and income generation to the extent envisioned in the MPFS. Therefore, the review team has identified
some gaps in the economic practices of community forestry. For example, the cost of labour invested by
member households and the time spent by individuals in community forestry activities is unknown.
Similary, the CFUGs do not keep track of the growing forest stock or of the volume of harvestable
timber, firewood, and fodder. There are also no records of the income generated from internal and
external sale. As a result, it is difficult to estimate the gross and net income generated, and the amounts
distributed to users, to the central treasury, and to local government bodies.
Another issue flagged by FECOFUN has been the categorization of certain forests, especially in the
Tarai. According to the Forest Act of 1993, community forestry is the prefered form of management,
valued over leasehold, religious, or collaborative forestry as well as over the protected area system.
Whereas in practice, the system of collaborative forestry and the protected area system has been prefered
over community forests in the Tarai and inner Tarai.
Forest Act/Rules have granted CFUGs status as autonomous, independent, and self-governing
organizations involved in forest conservation, management, and community development. They have
rights to access, use, manage, and sell forest products as per the operational plan. However, these rights
have often been diluted through administrative orders, circulars, and decisions. These orders, circulars,
and decisions have heavily increased the transaction cost of forest production and utilization. Indeed,
they have hampered the growth of forest-based industries in Nepal. On other other hand, illegal
harvesting of timber in some community forests has compelled the CIAA to take action against forest
officials and executive members of the CFUGs. The issue of how best to motivate CFUG members to
promote sustainable forest management and increase the productivity of community forests is a key
issue in Nepal.
39
Several forestry projects including community forests in the mid-hills and the Tarai, the Livelihood and
Forestry Program, the Biodiversity Sector Program in the Tarai and Siwaliks, and the Tarai Arc
Landscpate Program promoted tree plantation on farms and distributed tree seedlings to households. The
MPFS had identified expanding commercial tree seedling production and distribution as well as relaxing
the cumbursome permit proceduresfor private tree products as a key goal. This has not been a success.
Indeed, over the years the trend has been of a limited number of seedlings produced by the line agencies
in the district. Meanwhile, restricted budgets and administrative hurdles have been imposed on farmers
wishing to harvest and transport products from private trees to the market. There is significant interest,
especially in the Tarai, in commerical tree plantation as cash crops. The permit system has, however,
been a major disincentive for private tree growers.
4.1.3 Lessons Learnt and Way Forward
Building on the institutional and environmental achievements of community forestry, the new forestry
development strategy should focus on income generation and job creation. To succeed in these areas,
reforms are needed in the following areas:

Intensification of forest management and the application of tools and techniques for sustainable
management of forests.

Enterprise development and value addition of forest products.

Simplifying marketing inside and outside the village, district, region, and country.

Simplifying the regulatory and adminstrative procedures of extraction, harvesting, sale, permit,
and transport of forest prodcuts, especially timber.
With reference to the last point, several surveys (CBS 2013) show that trees on private land have
significantly increased overtime. Farmers are also abandoning their marginal land to be converted into
forest land as youth are migrating in search of alternative (to agriculture) income earning employment
opportunities. As the labor shortage increases, forests and trees on private land will tend to increase.
Tree planting on private land can further be enhanced if quality and desired seedlings are provided to the
farmers. Further, the contribution of VAT from private forests is insignificant (about NPR 60 million)
compared to the transaction cost of permits and hassles farmers have to encounter in the sale of their
products. Since there is no VAT in the trade of agriculture products, it is necessary that VAT on private
forest products are also eliminated as soon as possible. The government can capture more than this sum
through value addition in the supply chain. The farmers will intensify tree plantation and forest
management in their private land if the permit regime is simplified.
Though the areas of reform have been noted above, the question of why the focus of community forestry
should shift towards intensive management perhaps has not been made. The following eight points
highlight the reasons we need to shift to an economic focus in forestry:

Forest growing stock, biomass, market, human resources, and local institutions exist. There is
immense potential to increase the sustainable harvesting of timber and wood to several times
more than the current production rate.

Local communities are willing to shift to a market focus to create more jobs locally.
40

The environmental, political, and demographic context is changing fast; the youth are
increasingly less interested in subsistence farming, preferring income earning jobs. Such jobs
could be provided through commercial forestry.

Sustainable harvesting generates excess production meeting more than the local consumption.
Commercialisation will add value to the supply chain and provide employment to the local
people.

The current level of employment through community forestry in thining, prunning and harvesting
is estimated to be just two persons per CFUG round the year. This can and should be increased
significantly.

Sustainable management of community forests can generate both intermittent and final products.
Forests can produce income earning products through thinning, prunning, singling, harvesting,
and cleaning of weeds. The intermittent harvesting of forest crops is necessary for both
maintaining forest health and extracting products for domestic and commercial needs. These
intermittent and final wood products can be used as timber or composite wood.

Community forestry has been more or less successful in achieving institutional and ecological
sustainability. It is now time to move towards financial gain and economic sustaniability.
Rigourous studies on the financial, economic, and ecological contribution of community forests are
needed if the shift towards income and employment generation is to take place. Solid research must
form the foundation of any subsequent interventions.
4.2 National and Leashold Forestry Program
National and leasehold forestry is the second priority program of the MPFS. The program aims to
complement community and private forests by developing and managing national forests through
government agencies or private sector leases. While the community forestry program aims to fulfill the
household needs of rural people, the national and leasehold forestry program aims to produce forest
products for commercial use, expansion of forest-based industries, revenue generation, and employment
to the people at large. The MPFS categorizes national forest as forests managed by the government or
the Department of Forests (DoF). This is equivalent to the government-managed forest category created
by the Forest Act 1993 and Forest Regulations 1995.
Leasehold forests, as identified by the MPFS, are similar to the corporate-based or institutional leasehold
forest provided for by the Forest Act. The pro-poor oriented leasehold forestry program implemented by
the DoF was not conceived during the MPFS. However, the prevailing Forest Act and Forest
Regulations have specific provisions for pro-poor leasehold forestry. The fundamental differences
between these two types of leasehold forestry lie in (a) the annual rental fee for the use of the forest
land, (b) the organizational characteristics of the leaseholder, and (c) the decision to lease the forests.
There is an annual rental fee for using the land leased to the corporate sector. However, it is free for the
poor households. Further, while corporate bodies or firms can rent leasehold forests, poor households
have to first organize themselves into groups before they can apply for the leasehold forests.
Additionally, a group of poor households can get the leasehold forest by the decision of the District
Forest Office (DFO). However, corporates can have the leasehold forest by the decision of the MFSC.
The initial duration of the lease is 40 years but renewable for another 40 years in both corporate and propoor leasehold forestry.
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Theoretically, MPFS envisaged national forests as being on an equal footing with community and
leasehold forests. The Forest Act 1993 and Forest Regulations 1995, however, signal governmentmanaged forests as residual national forests, which have not been converted to the community and
leasehold categories. In this paper, we use the term “national” forest as equivalent to “governmentmanaged” forest, unless specifically described differently.
4.2.1. Components and Targets
The program seeks to demonstrate enhanced management techniques for natural and plantation forests
in the Tarai as well as inaccessible areas in the mid-hills and mountains. Once the forest agencies
demonstrated the enhanced management techniques, these forests would be gradually handed over to
local people as community forests. Until then, the remaining inaccessible forests of the mountains and
the Chure range were to be considered protected forests or wilderness areas. The program contained the
following components:

Land use classification of forests. Forests would be classified into National Protection Forests or
Wilderness Areas, National Production Forests, and Community Forests (including the present
and potential community forests).

Establishment and management of production forests in suitable areas to supply wood to urban
and wood-deficit areas.

Leasing of available and suitable forest land to private sector for industrial plantations.

Trial plantings followed by large-scale plantations on degraded land. These replanted areas
would be managed as demonstration sites or national production forests.

Practice silviculture and yield regulation in natural forests. These forests would be managed as
demonstration sites or national production forests.

Loans for private and industrial leasehold forestry would be provided by the Agricultural
Development Bank.
The program aimed at managing about 0.5 million ha of forests though government and leasehold
arrangements over the MPFS period. This was projected to lead to the production of about five million
tons of fuelwood and about 1.1 million M3 of timber by the end of 2011. These targets were not
separately segregated into national and leasehold forests.
About USD 352 million (1988 constant prices) was estimated to be required to implement the program
during the 21 year period (1989/90 to 2009/10). This amounts to about 20.2 percent of the total
projected investment made under the MPFS. The private sector was expected to contribute about 25.5
percent of the total program cost over the years.
4.2.2 MPFS Program versus Implementation Modalities
To date, most accessible forests in the mid-hills and mountains have been handed over as community or
pro-poor leasehold forests. Some accessible forests in the Tarai and Siwaliks have also been handed over
as community forests. But the process of handover has been very slow in these two regions, with some
42
efforts coming to a complete halt. A major problem in the Tarai is that many community members
would be distant users (households living farther away from the forests). Meanwhile, many conservation
issues have been faced in the Siwaliks. Each of Nepal’s 75 districts – except Mustang which is covered
as a protected area under the ACAP – prepares a District Operational Forest Management Plan spanning
five years. These plans are applicable to all the forest management regimes as well as state the amount
of forest products to be harvested from each regime. Since the community forests and pro-poor
leasehold forests conduct detailed inventories of forests types and the silvicultural systems to be
followed in both harvesting and regenerating the forests, green trees harvesting is allowed from the
former and planted trees from the latter. No clear harvesting and regenerating system is followed in the
national forests, except in those Tarai forests which are now being managed as collaborative forests.
This category is discussed in detail below. In much of these residual forests, an “undeclared policy of
removing 4 D trees (Dead, Diseased, Died, and Decayed)” has hampered the management of these
forests (NRB, 2013).
At present, the GoN is managing some blocks of national forests under a collaborative forest
management program in some districts of the Tarai. In this program, the government collaborates with
adjacent and distant forest users and local government bodies such as VDCs and DDCs. This
Collaborative Forest Management (CFM) model is still in a pilot phase at 20 sites, covering a total area
of about 54 thousand hectares, across nine Tarai districts. Since CFM is not specified in the Forest Act
and Forest Regulations, this program is being run through guidelines approved by the GoN in 2002 and
further revised in 2011.
The section below reviews both the national and leasehold forestry programs. In the latter, the main
focus is on the pro-poor leasehold forestry as the corporate-based leasehold forestry is of small scale.
4.2.3 Key Achievements of National Forestry Program
The DoF is responsible for the implementation of the national and leasehold forestry program.
Accordingly, the National Forestry Division, one of the three divisions of the DoF supports the
implementation of the program in the districts. The DFO is responsible for the implementation of the
program along with the handing over, technical support, and monitoring of community forestry and
enhancement of private forestry in the field. The National Forestry Division has three sections namely
(a) Forest Protection Section, (b) Forest Management Section, and (c) Forest Product Utilization section.
The functions of the division are stated as follows:

To promote scientific management and development of national forests.

To promote proper and equitable utilization and distribution of forest products.

To promote leasehold and collaborative forest management through DFOs.

To protect the forests through DFOs.
Not much progress has been made in the management of national forests. Indeed, national forest
management has been a bottleneck in the development of forestry in Nepal. The Forest Act/Regulations
have a provision for allocating some part of national forests as protected forests for restoring its cultural
and conservation value. In the latter phase, protected forests have been declared as an integrated comanagement modality of 133,000 ha forest land for biodiversity and environmental conservation. As the
43
implementation of the national and leasehold forestry program is facing serious challenges, we review
some achievements and processes under this program.
Listed below are some major interventions of the DoF to better manage the national Tarai forests during
the MPFS period.
I. FMUD project and technical forestry
The Forest Management and Utilization Development Project (FMUDP) supported by the Finnish
government provided both financial and technical assistance to focus on national forestry programs in
the Tarai. The project ran from 1991 to 1995. The objectives of the project were to increase the longterm productivity of the national forests of Nepal. The activities would be concentrated primarily in the
Tarai area, the main objectives being the fulfillment of people’s basic needs of forest products and
protecting the environment. The outcome of the project was to be improved protection of actively used
national forests with increased productivity.
Working procedures for the district-level managers of Tarai forests were prepared under the project.
Although forest management plans were also prepared previously, they were not operational. These
earlier plans were prepared by the center, were protection oriented, and did not focus on proper
harvesting and utilization of the forests. The project developed a strategy for operational planning
(working at the sub-district and forest stand level rather than at the district forest as a whole) based on
information related to socio-economic background, forest management aspects, technological factors,
and economic factors. A number of practical studies relating to stocking, yield and growth, species
composition, and regeneration status of the Tarai forests were carried out in order to make the
Operational Forest Management Plans (OFMPs) more practical and easier to implement. These studies
showed that the Tarai forests could yield as much as 12 to 15 cubic meters of wood per hectare per year
in comparison to the previous figure of 5 cubic meters per ha per annum. Similarly, the rotation age of
Sal (Shorea robusta) was reduced to 80 years from 120 years.
The project also prepared the “contents of an operational forest management plan”. The project initially
piloted two plans in Rautahat and Bara districts. Later, similar plans were prepared for another 17
districts based on the concept, guidelines, and modalities of these two plans. FMUDP spent significant
efforts in generating information and knowledge on the potentials of implementing OFMP in Tarai
districts. Several reports and papers were prepared by FMUDP focusing on new information on Tarai
forests and their management.
As a result of the extensive groundwork, certain parts of the OFMPs were implemented. Activities such
as delineation of plots, marking trees, fire line construction, and climber cuttings were carried out as per
the plans. The implementation was, however, not backed by political forces and some forestry
stakeholders. Local communities surrounding the forests and further afield noted that these plans were
prepared without their participation. As a result, these plans were not implemented in totality.
II. Development of a technical forestry model
The initial exploration on technical forestry based on stand level management, which started through
OFMP, showed the technical potential of managing old growth forests of the Tarai with a shelterwood
silvicultural system. The shelterwood system was suggested as the most appropriate silvicultural system
for the management of these matured to over-matured forests. The simulation model developed by
44
Kanel (1994) also showed the high payoff of active forest management in the Tarai. These technical
forestry studies showed that the growth rate of the Tarai’s Sal forests is significantly higher than the
estimates available in the yield tables from India. Similarly, the rotation of Sal forest could be reduced
from 120 years as was the practice then to 80 years. Thus, a technical model of forest management was
developed through the FMUD project. This approach of forest management is now being tested in the
CFM plots in the Tarai.
III. Development of District Forestry Coordination Committees (DFCC)
The forest administration realized that without the cooperation of the local people and district level
political bodies, forest management in the Tarai and adjoining areas could not be implemented. This
realization, and the innovative work done in the Tarai through BISEP-ST, led to the formulation of a
district-level multi-stakeholder forum named the District Forest Coordination Committee (DFCC).
Chaired by the DDC president, the DFCC included all forest stakeholders as members working in a
district. A directive on DFCC was approved initially in 2006 and was again revised in 2011. The DoF
believes that this mechanism can help in allocating different forest management regimes as well as in
resolving other forest-related conflicts on the ground.
IV. Institutional modality of involving distant users and CFM
One of the stated achievements of the CFM is the design of a unique forest tenure regime in the
management of larger natural forests in the Tarai with the cooperation and participation of both
proximate and distant users, local governments, and the central government. The chairperson of the
users’ committee is the representative of the users whereas the member secretary is the local forest
officer. The CFM program is supposedly self-sustaining as fifty percent of the income from the harvest
and sale of matured forests accrues to the committee. This institutional arrangement in terms of tenure
reform, forest governance, the inclusion of distant users, and the application of active technical forestry
are all highlighted as achievements (various publications of Hamro Ban, National Seminar of DFOs2009).
V. Public forest management in the southern Tarai
Public land under the jurisdiction of local government is being used for tree cropping in the southern
parts of the Tarai, where national forests are lacking. These areas are being planted by the poorer
households as part of a group with support from DFOs. In some cases, the households use agro-forestry
as a technique, while in others trees are planted along the fringes of local ponds established in the public
land. The objective of this program is to involve poorer households who do not have access to private
land for tree planting, to increase the income of the poorer households, and also to increase the supply of
forest products.
VI. Establishment of the forest development fund (FDF)
The FDF was established in 2007 to expand forest development and management activities. The Fund
was designed to ensure a sustained flow of resources to the forestry sector. This was a necessary
measure in a context where the annual budget devoted for forests depends on political priorities. The
fund was created with NPR 5 per Cft levied from private timber traders and NPR 5 per Cft provided by
the government for the same wood. To date, about NPR 204 million has been collected in this Fund.
45
However, the operational modality of spending the money on different forest activities has yet to be
approved by the government.
VII. Production and distribution of seedlings
The production and free distribution of seedling for plantation in private land has expanded since 1990.
This has helped to expand the number of trees on farms. As a result, timber production from private
forests has been increasing. Different projects such as Tarai community forestry, BISEP-ST, LFP Tarai,
Tarai Arc Landscape Program, Rastrapati Chure Program, and recently the government itself have
increased budget for free seedling distribution.
4.2.4 Key Issues and Challenges of National Forestry Program
A key constraint in managing national forests is the lack of a decentralized institutional mechanism as
well as of local people’s participation. This institutional vacuum still prevails, particularly in the Tarai,
Chure, and the high mountains. Some major issues, challenges, and threats are as follows:
I. Land use classification of forest land
The land use classification system has not yet been operationalized for real zonation in order to manage
the forests. Categorization of the forest land – into forest and non-forest, accessible and non-accessible
forest, productive and protective forests, and forests and grazing land within the forest boundary – is a
pending task. Similarly, the forests have not been categorized for scientific management, mixed
management, reclamation, and for protection. The Ministry of Land Reform and Management has lately
(2012) prepared a land use policy. This policy has also been approved by the government, but it is too
general and lacks a proper enforcement mechanism to make it implementable.
II. Pressure on Tarai and Chure forests
The demography of Nepal is shifting. More people are either moving to urban areas or to the Tarai and
Chure areas. The latest census report shows that more than 50 percent of the total population of Nepal
now resides in the Tarai and Chure areas. This has caused tremendous pressure on the forests of these
regions. Official data shows that about 90 thousand people are encroaching on the forests in 25 Tarai
districts. The higher density of population also requires more public infrastructure such as roads,
schools, medical facilities, and other open spaces. The forests are gradually converted either into private
residential areas, private farms, or public infrastructure. Even in the mid-hills and mountains, national
forests surrounding urban or bazar areas are prone to illegal use or deforestation. Pressure is also
mounting to provide forest land for hydro-electricity generation, mainly in the mountains and the midhills. Similarly, pressure is also increasing to provide forest land for police and army barracks, hospitals,
and academic institutions. These are all challenges for forest management.
III. Frequent policy changes in the allocation of forests and harvest/sale of forest products
The government had demonstrated a habit of changing forest policies frequently without a consultative
process beforehand. In some cases, the Forest Act is in conflict with other legislation on local
development, mining, and water resource development. The frequent and abrupt changes in forest
policies create risk which discourages investment in forestry and limits people’s participation. The
46
recent attempt to revise the Forest Act and Regulations and the restrictions on the sale of forest products
has adversely affected motivation among communities and created frustration among the forest-based
industrialists. The attempt has unnecessarily increased the transaction cost of doing business in forest
products’ processing and marketing. It has even promoted the import of timber from other countries
such as Myanmar, Malaysia, and elsewhere.
IV. Wild fires, uncontrolled grazing, and illegal removal of forest products
Since there is no practical tenurial regime to regulate the household use and extraction of forest
products, access to national forests is in fact free for all. Although the Forest Act/Regulations prescribe
the mechanism for entering and grazing in the national forests, enforcement is weak. It is reported that
some herders entering the national forests deliberately set fire in the forest to get a flush of green grass
during the dry season. This and other reckless activities, such as throwing burning cigarette stubs in the
forest, promote the spread of fires in the forest. The government, including DFOs, does not have
equipment or training to control the wildfires. Such fires are especially acute during the early summer
season when high temperature coincides with the presence of dry ignitable material – fallen branches,
leaves – on the forest floor.
Uncontrolled grazing compacts the forest floor (soil), adversely affecting regeneration and regenerated
seedlings. Illegal removal of forest products by rural households depletes forest resources and is
anathema to better forest management. Although these are activities against the provisions of the
prevailing Forest Act and Regulations, enforcement of them is very weak or non-existent.
V. Workload of DFO staff
The DFO staff is responsible for the implementation of both community and private forestry as well as
for national and leasehold forestry programs. The tenure and ownership of community, private, and
leasehold forests is more or less defined in the Forest Act/Regulations. The management responsibility
of these forests lies within the community, private holder, and leaseholders respectively. The DFO staff
support these entities in executing the programs. However, in the case of national forests, the
responsibility of protecting and managing, access rights and control of the forests, and the sale of forest
products lies with the DFO staff. Moreover, the DFOs are also involved in the legal adjudication of
forest offences. Regular monitoring and inspection has also to be carried out by the DFO. Forest
technicians face difficulties in carrying out these multiple and conflicting functions. Moreover, the
MPFS also recommends that the forestry staff be involved more in technical aspects of forestry rather
than occupied by administrative tasks.
VI. Skills, knowledge, and capacity in sustainable forest management
The need for foresters to upgrade their skills, knowledge, and practices on SFM has become a common
concern. This issue was highlighted at a DFO seminar in 2010 as well as by numerous Hamro Ban
publications. Although much has been written about community forestry in the social sciences, the
technical aspects of enhancing forest productivity and forest product marketing still need strengthening
in Nepal. Collaborative forest management in some districts of the Tarai is generating some knowledge
on silvicultural systems. However, such practices suitable for Chure, mid-hill, and mountain forest
management have neither been innovated nor adopted in these regions. Developing appropriate skills,
generating new knowledge, and practicing these innovations are serious challenges in the management
of Chure and mountain forests as well as in expanding active forest management in the Tarai.
47
VII. Conversion of national forests into protected forests or protected areas
A large area of national forests has been transformed into protected areas since the adoption of MPFS.
This measure has limited these areas for multiple use. In some cases such as the Banke and Gauri
Shankar area, these policies have antagonized the local communities who had access to these forests
before the transfer. Converting multiple use forestry (national forests, community forests) to protected
areas or protected forests inhibits the supply of forest products to be used by local households and as raw
material for forest-based industries. The trade-off between production forest and protected forests, and
the comparative advantage of these management regimes have to be assessed before forests are allocated
into different management regimes.
VIII. CFM and block forest management
A DFO seminar held in 2010 in Kathmandu presented a case for both the CFM and for block forest
management systems. The CFM model has already been discussed in the context of the Tarai. Block
forest management is, however, discussed in the context of all of Nepal. The seminar proposed the
management of block forests both by the government in national forests and/or as public-private
partnerships in corporate leasehold forests. How these types of forest management regimes would be
differentiated and allocated has not been clarified by the government.
IX. Forest encroachment and degradation
About 80,000 ha of national forests have been encroached on by individuals and institutions, mainly in
the Tarai. The average rate of deforestation in the Tarai was 1.3 percent per year between 1978/79 to
1990/91, but declined to 0.4 percent per year during 1990/91 to 2010/11 (DFRS, 2014). However, forest
degradation (reduction in growing stock, forest species diversity, lack of regeneration, among other
indicators) appears to be higher than deforestation in the Tarai. Empirical databases on this subject are
lacking.
4.2.5. Key Achievements of Leasehold Forestry Program
I. Commercial leasehold forestry program
Figure 4.2: Forest use for non-forest and
commercial lease purposes
The Forest Act of 1993 has a provision to lease
degraded forest plots below 20 percent crown
cover for commercial and scientific purposes.
Meantime, the leasehold forest policy of 2002 has
also enumerated guiding principles to lease out
parts of forests for commercial purposes. The DoF
record shows that about 14 percent (1,600 ha) of
total allocated leasehold forest land (about 13,000
until 2013) has been used for tree-based forestry
purposes. Eco-tourism and herbal farming
constitute about four percent of total commercial
leases. Contrastingly, 82 percent of total forest
land has been leased for non-forestry purposes to the army and police as well as to hydropower
developments.
48
II. Pro-poor leasehold forestry program
The Forest Act of 1993 has made special provisions to lease degraded forest land to groups of
households living below the poverty line. Pro-poor leasehold forestry is one of the priority programs of
the government. This program has been considered an instrumental model for poverty reduction and the
rehabilitation of degraded forests by the government of Nepal. The program is implemented by the DoF,
the Ministry of Federal Affairs and Local Development, and the Department of Livestock Development.
However, the handing over of the forest lease is the responsibility of the concerned DFO.
The program began as a small pilot project in 1989 in two mid-hill districts – Kavre and
Sindhupalchowk. It has since been extended to 40 districts covering areas from the Tarai to the high
mountains. Perceived as an innovative program for poverty alleviation, pro-poor leasehold forestry has
already been mainstreamed in the forestry sector. The NPC has designated it as a priority government
program. The DoF has been regularly implementing this program with financial and technical support
from IFAD and the Food and Agriculture Organization (FAO). Meantime, a number of other donors
(SNV/BISEP-ST, DFID/LFP, SDC/NSCFP, PAF/Nepal) have also supported the implementation of the
program in their respective project areas.
About 41,300 ha of forest land has been leased to poor households. A total of 6,957 leasehold forest
(LF) groups have been formed, with a membership of 65,402 households (Figure 4.2). Of them, 916, 26
and 71 LF groups were established through the Western Upland Poverty Alleviation Project (WUPAP),
Bio-diversity Sector Programme for Siwaliks and Tarai (BISEP-ST), and the Livelihoods and Forestry
Program (LFP) respectively. The average size of LF user groups (composed of poorer households) is 9.4
and average forest area is 5.93 ha per group (0.60 ha/HH), though these numbers vary across the
program (WUPAP and FAO TA Pilot districts having about 1 ha/HH). Among these interventions, the
Leasehold Forestry and Livestock Program (LFLP), a project funded by IFAD has been a major
promoter of leasehold forestry. The project is now running in 26 districts. The ethnic composition of
participants in the LFLP is 58.8 percent Janajati and 12.5 percent Dalit, with Brahmins, Chhetris, and
Newars making up the remainder. Meanwhile, women make up 37.8 percent of participants, a higher
percentage than many similar programs in the forestry sector. In all, about 88 percent of the groups are
reported to be functional.
Figure 4.3: Leasehold forest groups and their area of management over 20 years
49
The majority of LF groups, about 68 percent, have good to moderate institutional and technical
capability. Yet, they are managing 89 percent of the allocated forest area. With reference to financial
management, less than 40 percent are in the good to fair category. Nevertheless, the groups have been
organized into inter-groups and cooperatives. Altogether, 55 cooperatives have been formed by 500 LF
groups. In the latter phase of the program, district federations of the individual user groups were formed
in six LFLP districts. Recently the TA/FAO/LFLP (2012 and 2013) carried out detailed outcome level
studies of LFLP covering the major components of leasehold forestry including institutional
development, forest and livestock development, and rural finance development. Major findings of these
studies in terms of livelihoods capital of LFUGs are:
III. Impact on natural capital
The majority of the degraded land has been converted into multiple use forests with trees, grass, and
herbs. The forests now have more than 90 percent ground cover. Leasehold farmers have increased
fodder and grass production to feed livestock. Some have practiced high value NTFPs for markets.
Forest fires and open grazing have been controlled. The program has also reduced pressure on adjacent
forests as the leasehold farmers have produced their forest product needs from their leased land.
IV. Impact on social capital
Poor households are organized into more than 6000 LFUGs. LFUGs in six districts have been organized
into district federations and about 500 LFUGs have been organized into 54 Cooperatives. Moreover,
they have been able to develop linkages beyond forestry pulling more than NPR 3 million in funds from
other district based offices. About 11 percent of the ultra-poor LFs have been lifted up to the rich
category as compared to a similar upward movement for only 1-2 percent of the control groups over a
period of 10 years. Representation of women in LF management and benefit-sharing has increased from
34 percent in 2005 to 55 percent in 2012. LF is mainstreamed in the forestry sector and it is ranked a
national priority (P1) project by the NPC and MoF.
V. Impact on human capital
School attendance of children has increased. Similarly, LF has significantly contributed to saving
women work hours for the collection of forage/fodder and firewood from 2.5 hours in 2000 to 2 hours in
2012. Part of the time saved was "re-invested" in livestock rearing, agricultural production, and work in
kitchen gardens.
VI. Impact on financial capital
Over 90 percent of LF members are involved in saving and credit schemes with accumulation of NPR
62,035,796. More than two thirds of the funds have been mobilized in various IGAs and the repayment
rate is satisfactory. The number of cooperatives has increased from 17 in 2005 to 54 in 2012. The S&C
groups of LF have initiated developing linkages with other financial institutions.
LF households are involved in more than a dozen micro- or household level IGAs from kitchen garden
to agro-forestry enterprise development. The average annual cash income of the LF households has
increased from NPR 25,589 before the project to NPR 43,768 post-intervention. Livestock products are
the overriding income source, with the total almost doubled as compared to the base year level.
50
LF households linked with good road networks and markets have changed their traditional farming
system with increasingly more farmers joining in the commercial farming of cash crops such as
vegetables, fruits, broom grass, and NTFP such as Chiraito, Argheli, and Kurilo. They have been
promoting the commercialization of forage and fodder seed production across the country.
VII. Impact on physical capital
Households investing on education, health, and clothing has increased. The number of households with
thatch roofs, brush wood, and mud stone are steadily decreasing. The LF project has increased the
access of LFUGs to various basic services such as drinking water, health and sanitation facilities such as
toilet and cooking stoves, electricity and education, and quality of livestock.
4.2.6. Key Issues and Challenges of Leasehold Forestry Program
Private or corporate-based leasehold forestry has virtually been a neglected program except for some
interventions in eco-tourism and NTFPs. This is due to the fact that the existing Forest Act does not
have a provision for leasing existing forests for management and utilization. The lack of legal provisions
has adversely affected the implementation of corporate-based forest management through leasehold
forestry. Secondly, the existing annual rental fee for bare or degraded forest land is very high. This is a
further disincentive for the private sector. Both of these legal provisions need to be simplified so that
private investors can be tempted to sustainably manage part of the national forests for wood and nonwood production.
Despite the positive attributes of the pro-poor LF, more than a dozen articles on LF, the LF Supervision
Mission, and an Interim Evaluation Report (IFAD 2003, 2009 and 2012) have reported a few relevant
institutional, technical, and socio-economic issues about the sustainability and scaling up potential of
pro-poor LF. The commonly stated issues include: the adoption of a blanket approach mostly driven by
donors, competition with community forestry, unsecured tenure rights, conflicts with customary land
tenures, exclusion of poor households and traditional users, lack of post-formation support, poor support
for livelihood diversification and value chain development, weakening group cohesion, poor
coordination and governance (GOs and LFUGs), and poor monitoring and knowledge management
system.
The most pertinent issues and challenges of group leasehold forestry are:
I. Inheritance rights and its risk assessment
A major issue of pro-poor leasehold forestry is the generational continuity and its risk assessment. Many
youths from the mid-hills are not interested in subsistence based farming, and are temporarily migrating
overseas for employment, or moving to the Tarai or urban areas. Similarly, farming a small patch of
degraded forest may not provide enough incentives for the poor. Population dynamics and its
management should therefore be considered for the next generation of leasehold forestry. An option
would be to merge community forestry and leasehold forestry for institutional sustainability.
II. Rise in social conflicts over traditional use rights
Inclusion of the relatively rich and the elites in LF groups while poor households are excluded has been
a problem of the LF program. Similarly, the handing over of LF plots used for grazing and the collection
51
of grass and other biomass by local communities without their prior consensus has resulted in conflict
over rights to use between LFUG and non-LFUGs. There has also been tension between the formal
LFUGs and customary land tenure systems including shifting cultivation.
III. Weakening group cohesion
The trend of managing LF plots on an individual basis has weakened group cohesion, threatening the
sustainability of the program. LF households involved in individual management have informally started
selling their plots to Non-LFUGs or leasing plots to other group members.
IV. Entrepreneurship development and climate change
Although the program has produced much better results than other programs in supporting the poor and
generating livelihood opportunities, the program has not been able to foster direct employment through
enterprise development. The poorest are a climate change vulnerable group, and should be the major
target to address the issue in rural development.
V. Indebtedness
Significant numbers of LF households who have borrowed loans during the HLFFDP period have
experienced repayment problems and many face the risk of being landless.
VI. Cultivation and marketing of NTFPs
Sustainable production of NTFPs in high altitudes is currently not possible. Mainstreaming the technical
services demanded by local users is a challenge. Event-based and seasonal service providers may not
support the users’ regular demand in the long term. High altitude forest land and degraded land
management require more inputs to be provided partly on subsidy. About 50 percent of the land still
needs maximum inputs for optimal and sustainable utilization of the land.
4.2.7 Lessons Learnt and Way Forward
The implementation of the national and corporate leasehold forestry program is very weak. Significant
progress has been made in pro-poor leasehold forestry, which was not conceived in the MPFS. The
major lessons learnt are as follows:

The recent practice of CFM in some national forests in the Tarai has been a success. Significant
volumes of wood can be obtained from the removal of old growth and the natural regeneration of
the forests. This CFM approach can be further expanded in the Tarai where the issue of distant
users is acute. However, the mechanism of benefits sharing and the cost of CFM implementation
need further consideration. Similarly, the institutional structure (representation, decision-making,
and benefit sharing) of the CFM also needs to be reformed.

No existing national forest has been leased to private parties for management and utilization. The
MPFS had envisioned the involvement of corporate (private) sector in the management of
national forests. However, the Forest Act only allows corporate sector involvement in new
plantations and not in the management of existing forests. Even in new plantations, the high
leasing fee has been a disincentive. The existing Forest Act needs to be revised so that private
52
entities can manage the existing forests for the supply of forests products. Similarly, the annual
rental fee of the leasehold forest should be streamlined to make it competitive with other
investment activities.

The protective regime of forest management and the command and control nature of forest
administration have to be changed to increase better performance both in forest management, and
organizational performance. New knowledge and skills in tenure reform, sylvicultural system,
GIS and MIS, entrepreneurship, organizational management, and leadership have to be imparted
to forest professionals so that they produce better results. Similarly, a culture of positive attitude
and team work has to be instilled to promote sustainable forest management. All of these things
have to be strengthened so that the capacity of the staff and the forestry agency is enhanced.
Similarly, some of the functions (such as managing the forests) of the DFO staff could be
changed and they could be assigned to other parties. This has already happened in some of the
other technical ministries of Nepal

The pro-poor leasehold forestry is successful where the adjacent and non-poor have agreed to the
tenure of the leasehold forestry. However, the group-based leasehold forestry and community
forestry program are so compatible and synergetic that they could be merged to optimize the
benefits to the rural poor.

Various studies show that sustainable forest management and REDD readiness and results
complement each other. The market for forest carbon is very low, and Nepal seems to face
several hurdles (incremental production and leakages) in capturing the value of forest carbon.
However, dealing with the drivers of deforestation, governance reforms, and application of MRV
will ultimately help in enhanced management of forests. REDD+ readiness and strategy
formulation should promote forest management. The carbon credit that can be generated from
better forest management should be considered as additional financing rather than as a tradeoff
between wood production (provisioning services), and carbon sequestration (regulating services).
4.3. Wood-based Industries Development Program
This program aimed to facilitate the conversion of wood into commodities needed by the people, and to
contribute to economic development through industrialization. The program identified the possibility of
operating eight industries, namely timber harvesting, sawmilling and wood seasoning, furniture, parquet,
plywood, veneer, matches, and wooden handicrafts. It also identified eight issues and constraints
ranging from supply and pricing of raw materials to research and development. These issues are still
relevant today.
4.3.1. Key Achievements
The eighth to tenth five-year plans and two three-year interim plans were implemented during the MPFS
period. All these plans incorporated the major objectives of the MPFS. However, the designed programs
were not directed towards maintaining an effective balance between the demand and supply of timber
products. The MPFS recognized that coordination is virtually non-existent among forestry, agriculture,
livestock farming, energy policies, and other public sectors. The market-led economic liberalization
policy was not effectively pursued in the case of timber and fuelwood markets. The regular supply of
forest products required to sustain the forest-based industry did not take place as planned by the MPFS.
53
There has been a huge gap in the demand and supply scenario for raw materials, mainly in the urban and
suburban areas as well as in the Tarai region. It has also been difficult to ascertain the actual progress
and status of the forest-based industry in the absence of an appropriate monitoring system as envisioned
by the MPFS. Moreover, there have not been supportive policies (for instance, industrial policy, trade
policy, banking/financial investment policy) to promote forest-based industries. However, supply of raw
materials has been the major constraint in the development of this sub-sector. As per the estimate of the
MPFS, the demand for industrial sawn wood was about 438,000 M3 in 2011. However, about 376,000
M3 of roundwood (or about 188,000 M3 of sawn timber) was officially supplied in the 2009/10 fiscal
year. However, the supply was reduced to about 80,400 M3 of round wood in 2010/11.
The MPFS emphasized the need to generate revenue from the payment of market prices for forest
products from the national forest. This provision was not considered in the past. Recently, government
royalty (floor price) on timber sales have increased significantly. But these increases are not linked with
the cost of production and management. The MPFS forwarded a strategy to free internal trade and the
transport of timber and fuelwood from all restrictions. To support this, a provision was made to seal the
transport vehicle carrying forest products at the district of origin so that there would be no hassles at
transit points/checkposts on the way. However, several hurdles in the form of permit regimes and
informal taxes from various groups/institutions still exist.
Figure 4.4: Timber supplied from various forest regimes and agencies
The MPFS made some provision which required parastatal organizations (e.g. TCN) to compete on
equal terms with private enterprise. These provisions were initially enacted, but subsequently relaxed.
The MPFS also proposed to make low-cost financing available to forest-based industries for renovation,
improvement of productivity, expansion, and pollution-control facilities. It also forwarded strategies for
liberalization of the regime to import raw materials for forest-based industries and support for technical
and vocational training. There was no practical movement on all these provisions.
54
Significant increase has taken place in terms of imports of timber logs (from countries such as
Myanmar, Malaysia, Vietnam, Nigeria) and substitution of timber products (by steel, aluminum, PVC).
This situation has considerably hindered the growth and survival of forest-based industries, further
exacerbated by the poor management of national forests. An estimate by FenFIT indicates that about
NPR 20 billion is invested by private entrepreneurs (about 5,000 industries/establishments) in various
forests-based industries including timber and non-timber. Around 200,000 persons are directly or
indirectly employed in these industries.
Despite the MPFS proposed financing plan – NPR 2.1 billion at 1988 constant price of which 743
million comes from the GoN, 210 million from the private sector, and 1.15 billion from external
assistance – the investment from the GoN and external assistance has been practically nil.
Some noteworthy points of the program are:

Commercial leasehold forestry: Despite provisions in the MPFS, only about 10,000 ha of forest
land has been leased for commercial purposes. Out of this, approximately 14 percent (1,600 ha)
had been used for forestry related activities.

Timber production and harvesting: Timber production in Nepal has been occurring in national
forests, community forests, and private forests. The main actors in harvesting have been from the
private sector, even though some harvesting is carried out by TCN and FPDB. In the case of
community forests, some communities are harvesting themselves.

Timber processing: The TCN was the main harvesting and processing organization in the past.
However, they are now processing to a much lesser extent. At present, the main actors in
processing are from the private sector, though some communities (either individual CF or an
alliance of CFs) have also been involved in processing timber. The private sector institutions are
also the main actors in the marketing of the various intermediary and finished products. At the
district level, some distribution/sale of the forest products is also done by the District Forest
Product Supply committees. Some community organizations such as CFUGs and cooperatives
are also engaged in marketing forest products.

Market chain analysis: This analysis revealed that the policy environment, including rules and
regulations pertaining to the timber trade and industry, has not been very supportive. Despite a
recent easing of guidelines for timber transportation, the problem of taxation at multiple levels
by multiple groups continues. Banks and financing institutions have not been supportive of the
forestry sector, as it is considered a risky area for bank loans. Quality control and branding
support is still a distant thing to institutionalize this sector. The facilities for seasoning and
treatment of wood are limited and even the existing facilities are not operating at full capacity.

Changes in wood technology: Several advancements in wood technology have taken place in
the two decades since the MPFS was drafted. The veneer and plywood industry at that time was
mainly using simal, sissoo, and poplar as raw material. At present, Alnus is the main species
used as raw material. Similarly, national forests were the only sources of timber then. Today,
community and private forests also produce logs for veneer and plywood production. Moreover,
in the past, most of the technology required large-sized wood/timber. With the newer technology,
smaller sized wood/timber can be used as raw material.
55
4.3.2. Key Issues and Challenges
As timber production is a multi-year venture, investors see it as a risky undertaking. Besides, trees are
biological resources, thus susceptible to drought, flood, pest and diseases, fire hazard, and grazing.
Another aspect is that usually the return from the industrial timber plantation only comes at the end of
the rotation period. Since there is no provision of insurance, the following factors make timber a risky
investment:

As there has not been a planned management of forest with consideration of sustainable supply
of raw materials, investors have limited confidence in the sector.

Quick and frequent change in policies and decisions creates an environment of uncertainty,
which in turn negatively affects investments. Predictability of policy is a major issue in forestry
investment.

Interference of various agencies such as the police, the CDO, or the CIAA interfere in the timber
market chain further complicating the process.

There is a shortage of trained technical human resources as formal and informal training facilities
do not exist. The CTEVT has a few training programs, but they are limited to the lower skill
levels.

There is no insurance or other risk avoidance mechanism for risky forestry works such as
harvesting, lumbering, and processing. This is a serious challenge in the forestry sector.
4.3.3. Lessons Learnt and Way Forward
Based on the above review, the lessons learnt are as follows:

Enhanced management and supply of wood from government-managed forests and community
forests is needed.

Implementation of private leasehold forests is needed so firms can manage the existing forests
for sustainable wood supply.

Financing with low interest rates should be made available through banks or other financing
institutions for private nurseries and plantations.

Carry out research and development related to fast growing short rotation timber species.

Further simplify the procedure for trade and transport of forest products.

Make parastatal organizations (such as TCN) compete with private enterprises.

Ensure financing at low interest rates for forest-based industries seeking renovation,
improvement, expansion, and pollution-control facilities.
56
4.4 Medicinal and Aromatic Plants and Minor Forest Products
The MPFS prepared a plan for the development of MAPs and five other NTFPs with the following
objectives:

To increase the supply of NTFPs.

To provide employment opportunities and contribute to the growth of local and national
economies.
4.4.1 Key Achievements
The MAPs/NTFPs have significant potential. But the substantial supporting and promotional work
required to tap this potential was not carried out during the decade-and-a-half of MPFS implementation.
Nonetheless, rural people from across Nepal have been collecting and selling NTFPs to augment their
income. NTFPs have also been an important source of revenue to the GoN; DoF records show that the
government collected about NPR 21 million as revenue from NTFPs during 2008/09. NTFPs were
mostly exported to India in crude or semi-processed form. However, during the last few years, some
semi-processed or processed NTFPs have also been exported to India and elsewhere. Such exports
mainly include essential oils from about 18 plants. The MPFS intended to promote MAPs and five other
NTFP groups of products.
Table 4.1: The targets and achievements of MPFS on MAPS and other minor forest products
Unit
New herbal centers
New processing centers
New cooperatives.
Farmers trained
Herbal farms:
Private farms
Community forests
Other plantations
Herbal collection:
From the wild
From farms
Lokta, increased capacity
Pine resin processed
Sal seed collection
New production areas:*
Khair trees
Sabai grass
Target
Achievement
No.
No.
No.
No.
12
4
46
2,000
10
4
No data available
No data available
ha
ha
ha
2,500
3,000
500
No data available
No data available
No data available
t/total
t/total
T
t/year
t/year
15,683
176,600
1,000
22,000
80,000
2,882
No data available
41
2,421
Stopped
ha
ha
6,000
6,000
No data available
No data available
I. Medicinal and aromatic plants (MAP)
The MPFS sought to promote MAPs/NTFPs for economic development of the country by
sustainable production, value addition, and trading in the global market. Though 30 species of
57
MAPs/NTFPs have been prioritized by the government, only 19 species have been traded widely at
maximum rates.
II. Lokta
The MPFS sought to build the capacity of the industries to produce 1,000 metric tons of lokta per
year. This target was not met. The annual supply of lokta during the last five years has been less
than 100 metric tons per year.
III. Sal seed
Though the MPFS planned to enhance Sal seed collection, the Sal seed industries have been closed
and there has been no supply of the seed for over a decade.
IV. Khair
The supply of Khair has been fluctuating every year during the last two decades. Over the last nine
years, the highest collection of Khair took place in the fiscal year 2004/05 (18,650 M3).
V. Pine resin
During the formulation of MPFS, only three rosin and turpentine industries were supporting resin
tapping and processing. At present, about 17 such industries are involved in resin‐tapping and
making rosin and turpentine in Nepal. They collectively tap about 40,438 metric tons of resin
annually from about 13.5 million trees. Pine resin is processed to produce rosin and turpentine, and
they are mostly exported to India.
VI. Sabai grass
There are four paper mills active in paper production. However, the quantity of Sabai grass used is
not known, as they mostly use paddy and wheat straw as raw material.
There has been a significant gap in the projection of demand and supply scenarios for various NTFP
commodities. It has also been difficult to ascertain the actual progress and status of the NTFP-based
industry in the absence of an appropriate monitoring system as envisioned by the MPFS. The
contribution of NTFPs/MAPs has been around 8 percent of total exports. Achievements regarding some
of the MPFS provisions/strategies are discussed below.

The MPFS proposed to promote agroforestry in the form of fruit trees inter-cropped with
medicinal and aromatic plants. However, very little has been achieved in this regard. There has
been decreasing supply of NTFP resources from the wild. A few NTFP species have been
cultivated in private land, either intercropped in agroforestry or as a single crop.

The MPFS provisioned for fair prices to the rural poor engaged in collecting and selling MAPs.
Unfortunately, no efforts were made to ensure this. Rural people sell to local traders, who often
do not pay them the just amount. However, certain highly priced NTFPs such as yarsha gumba
do signficantly contribute to the rural income. The government collected NPR 5.1 million from
the sale of 511 Kg of yarsha gumba during 2010/11.

The MPFS forwarded a strategy for identification and utilization of herbs and other minor forest
products. An NTFP policy along these lines was formulated only in 2004. This policy also
identified and prioritized MAPs for cultivation and trade.
58

The MPFS also proposed regulations to discourage the export of low value-added products and
encourage export of high value-added products. There was no implementation on this front.
4.4.2 Key Issues and Challenges
Key issues and challenges in the arena of NTFPs including MAPs are as follows:

Barrier of 3 km in mountains/hills and 5km in the Tarai is required from the forest to establish a
forest-based enterprise. This provision has hampered the establishment and promotion of forestbased industries in rural Nepal.

The authorities responsible for issuing certificates of origin are not issuing them for products
manufactured from enterprises registered as cooperatives. This is a major hurdle in NTFP trade.

Transport permits are arbitrarily issued and nullified.

Multiple check points and “informal fees” in the transport, trade, processing, and marketing of
products continue uncontrolled.

Lengthy and costly export formalities and difficulties at Indian customs are the norm.

Absence of modern and well-equipped chemical testing facilities/laboratory to identify the
chemical constitution of MAPs processed in Nepal.

Limited Sanitary and Phytosanitary Standards (SPS), quarantine inspection, and testing
facilities/centers in Nepal.

Non-trade barriers exist in exporting countries.

Arbitrary royalty rates and VAT for NTFPs are barriers for traders.

Royalties and taxation is also applied for NTFPs/MAPs produced in private forests and on
agricultural land.
4.4.3 Lessons Learnt and Way Forward

Nepal has some comparative advantage in niche products, which can be internationally captured
provided the regulatory and fiscal constraints are removed.

Abolish the rule that dictates the distance from forest for establishing forest-based industries.

Enterprises registered as cooperatives should get the same legal recognition as other
organizations.

Introduce simplified mechanisms to regulate the transportation of NTFPs/MAPs.
59

Export formalities required for international marketing of NTFPs/MAPs needs to be simplified to
export the products efficiently and effectively.

Capacity enhancement of existing labs to be compatible with international labs is necessary.

Quarantine facilities and centers should be added at strategic locations.

Revision of royalty and VAT rates based on scientific criteria (phenology, availability, market
price) and with intensive stakeholders/experts consultation is needed. Royalty provision for
cultivated products from private land should be stopped by enforcing a clear mechanism of
identifying the privately cultivated NTFPs/MAPs.

Several strategies need to be developed to promote this sector such as managing NTFPs/MAPs in
the wild, promoting their cultivation and domestication, processing and value addition, branding
certain products for national/international marketing, and research and development.

Research and development should be carried out on both biophysical production potential,
processing, and marketing of the products.
4.5 Conservation of Ecosystem and Genetic Resources
The MPFS identified conservation of ecosystems and genetic resources as an important component of
the forestry sector. For the successful conservation of ecosystem and bio-diversity resources, the MPFS
also emphasized forestry’s inter-connection and inter-dependency with other subsectors. The aim was to
ensure in-situ and ex-situ conservation of floral and faunal diversity with reduced human pressure on the
protected areas. Several constraints were identified for the conservation of ecosystem and generic
resources. They included inadequate policy guidelines, shared responsibilities with inadequate
coordination, lack of management capacity, inadequate training and equipment for field management,
lack of skills on human relationship management, community pressure on resources, and adverse impact
of tourism and poaching.
The plan aimed to protect special areas for their ecosystem and genetic resource values, as well as for
the provision of amenities, and promote in-situ and ex-situ conservation of plant and animal genetic
resources with the following objectives:
 To manage diverse ecosystems represented in protected areas for their scientific, scenic and
recreational, economic, and cultural values.
 To conserve flora and fauna diversity and enhance rare and endangered species of plants and
animals.
 To manage visitor use and tourism in protected areas without prejudicing natural or cultural values.
 To help preserve the cultural heritage and religious values of communities living inside protected
areas.
To achieve the above objectives five program components were identified. These included protected
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area management, genetic resources conservation, visitor use and tourism, preservation of natural and
cultural values, and institutional strengthening. Operational strategies were proposed for each
component.
4.5.1 Key Achievements
After the implementation of MPFS, there has been a significant increase in protected areas and in-situ
conservation of ecosystem and biodiversity in the country. The area of PAs has increased from 10,798
sq km (7.4 percent of Nepal’s land area) in 1988 to 34,185.52 sq km at the end of the plan period (which
is 23.23 percent of Nepal’s land area). There is a reasonable increase in the population of several
protected animals. The tiger population has reached 198 in 2013 from 98 in 1995. The rhino population
has also increased to 534 in 2011 from 358 in 1988. Similarly, wild buffaloes (Arna) population has
reached 259 in 2012 from 63 in 1996. The increasing number of these protected animals indicates a
success of Nepal’s conservation efforts. Another area of achievement is a paradigmatic shift in the
conservation policies from 'people exclusionary' and 'species focused' to 'people-centered community
based' and 'ecosystem/landscape approach'. Despite such a paradigmatic shift, the legal framework of
PA is contested on the issues of the process of PA declaration, governance, power sharing between
government authority and local citizens, and equity aspects of sharing benefits.
Efforts are made towards ex-situ conservation and specimen preservation through establishment of
botanical gardens, breeding centers, and national herbariums. Numbers of botanical gardens have
increased to 11 today from merely five during the early MSFP years. These gardens conserve and
demonstrate a variety of tree species, medicinal plants, climbers, orchids, cactus, and many other plant
species. About 161,800 plant specimens are preserved at the National Herbarium. Department of Plant
Resources (DPR) has studied and documented various aspects of the country’s flora and vegetation.
Exploration and collection of plant materials were carried out in every district of the country. Such
explorations and research has facilitated around 300 publications that include books, manuals, quality
standards, catalogue of plant species, and scientific journals.
Several faunal species are conserved at the Central Zoo of Lalitpur and at various small zoos at regional
levels. Similarly, breeding and conservation centers for elephants, vultures, and gharials have been
established in Chitwan and Bardia National Parks. Translocation of rhinos from Chitwan National Park
to Bardia National Park and Shuklaphanta Wildlife Reserve, and translocation of blackbuck from the
Central Zoo to Bardia National Park have been successful.
Wildlife poaching and the illegal trade of wildlife parts and NTFPs has remained a serious conservation
challenge for the last few decades. Curbing these activities has recently become a priority of the GoN,
and significant progress has been made since. A number of Wildlife Crime Control Committees at
different levels were formed and made active. As a result, a large number of poachers and traders were
arrested and wildlife parts confiscated. The GoN made significant progress in controlling rhino poaching
in the last few years. The year 2011 was celebrated as Zero Poaching Year, which is considered a
landmark achievement.
The MPFS had emphasized the need to have harmonious relationships between PA management and
local communities. As a result, the participatory approach of conservation was promoted with the
amendment of the National Parks and Wildlife Conservation Act in 1993. But, the structure and staffing
of the DNPWC was not reformed in line with the shift in conservation policy. The structure of the
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department also did not expand as per the geographical expansions of the PAs. Departments were
reorganized, integrated, and split multiple times. The re-organizations neither followed the institutional
arrangements proposed by the MPFS nor captured the broader aspects of changing management style,
working style, strategies, working culture, and service need of the people.
MPFS was prepared during the time when government was thought to be the sole agency in planning
and implementation of conservation programs and activities. During the implementation of MPFS,
however, the role of the government gradually changed from implementer to facilitator. The DNPWC
recognized the role of communities and introduced several management changes to foster better
relations with people. Today, many national and international conservation partners are active in
supporting DNPWC and community institutions to plan and implement conservation and livelihood
programs/activities.
4.5.2. Key Issues and Challenges
I. Human resources and capacities
As of December 1988, the DNPWC and the protected areas management team had a total staff of 1,126.
Of these, 82 positions were at the professional level or gazetted officers. The MPFS estimated a total
staff of 1,134 by 1995, with the number expected to remain constant at the end of the plan period in
2009. Meanwhile, the DNPWC and protected areas offices had a total staff of 1,041 as per 2013
statistics. The institutions are understaffed, and ill-equipped to manage the current work and extended
areas of the PA system. Moreover, the implementation of buffer zone programs in 200 VDCs and the
introduction of three breeding centers require a substantial number of staff. Similarly, the number of
visitors to 17 protected areas has increased by fourfold in the last ten years and eightfold in the last 20
years. The current staff cannot serve so many visitors, manage different programs particularly buffer
zone activities, and deliver other services. It is important to note that the shortage is not only in terms of
numbers; staff knowledge and skills also need to be enhanced on emerging areas such as climate change,
research, and new modes of conservation management.
The Department of Plant Resources (DPR) faced institutional turmoil in the early period of the MSFP.
The department was integrated with several other forest research/survey divisions and a consolidated
Department of Forestry and Plant Research was established. However, this structure did not last long.
The DPR again got a separate departmental status in the restructuring of 1993. The department currently
has a staff of 349. More recently, the DPR's structure and staffing were further changed in 2013 to adjust
the promoted staff under provision 24d of the civil service act.
To increase the capacity of existing DNPWC and DPR staff, a number of trainings, workshops, study
tours, exchange visits (in-country and international) are organized. However, there is neither training
needs assessment nor any training plan for capacity building. Similarly, there is no capacity building of
frontline staff including senior game scouts and elephant caretakers (DNPWC, 2067/68). Further, there
is inadequate park infrastructure and facilities in PAs; there are inadequacies in security posts,
administrative posts, water and electricity supply, furniture, toilets, and vehicles. The DPR also does not
have any training plan for its staff members. The budget allocation for in-situ and ex-situ conservation is
also very limited as compared to the need. Similarly, the existing infrastructure and laboratory also lacks
appropriate equipment and maintenance. The biotechnology laboratory at DPR also needs strengthening
for quality enhancement and lab accreditation.
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II. High concentration of visitors in few protected areas
Four protected areas of the country (SNP, SNNP, ACAP and CNP) are seen to have the highest
concentration of visitors. About 90 percent of visitors are concentrated in these PAs, putting extensive
pressure on natural resources in these areas. A substantial number of tourist lodges have been
established in SNPBZ during the last forty years due to increased number of visitors. The number of
lodges increased from one small inn in 1971 (Stevens, 2003) to 17 in 1980 to 225 in 1997 (Mattle, 1999
cited in Nepal, 2003) to nearly 500 in 2009 (Sherpa and Bajracharya, 2009). These PAs have neither
assessed visitor carrying capacities nor identified tourism zones. High concentrations of visitors in a few
protected areas, which are biologically fragile and already under stress from local populations, have
accelerated negative environmental impacts (Wells, 1993). In addition, a large amount of garbage has
accumulated along the trekking routes. This suggests an immediate need to determine the carrying
capacity of the protected areas and encouragement of visitors in other less crowded protected areas.
III. Governance and decentralization
The general issues of governance in government bureaucracies, including working style, decision
making, transparency, and accountability are also prevalent in both the DNPWC and the DPR. The poor
decision-making is noticed in PA management, as there is a tendency of asking for departmental
permission even if the full authority lies with the wardens of each entity. The traditional haakim2 style is
evident when forestry officials appear at public functions or negotiations. Such a style of working
together, driven by a “command and control” structure, contradicts the participatory approaches needed
in BZ program implementation. The delayed release of programs and budgets from the center to the
respective local offices is almost a regular phenomenon making it difficult to complete the planned
program implementation within the assigned fiscal year.
Similarly, BZMCs are neither fully empowered nor adequately trained for their governing roles. There
are also limited studies showing the consideration of gender, minorities, the poor, and marginalized
members in the BZUGs.
IV. Gender equity and social inclusion (GESI)
The NBS 2002 had emphasized the role of women in biodiversity and natural resource management,
calling for their participation in decision-making. However, GESI consideration in the DNPWC is weak.
Very few women work within the PA system and there are no visible efforts to increase the number of
women staff. Some initiatives have been taken to mainstream gender balance in conservation and
development. For instance, buffer zone management activities include women empowerment through
non-formal education. Similarly, the participation of women is encouraged in community-based
organizations such as user groups and user committees (Sharma and Yonzon, 2005). Nonetheless, the
fact that the DNPWC does not even have a ladies toilet demonstrated the state of gender inclusion. The
department has neither implemented the MFSCs’s GESI strategy nor appointed a gender focal person.
V. Human-wildlife conflict
2
Haakim is a colloquial term used for a person who is in the government service as a gazetted officer, and has the authority to make decisions (Pokharel,
1997). Haakim style denotes traditions, practices, and behavior resembling feudal style inherited from the 16th & 17th century Moghul regimes and further
solidified and perpetuated by the Rana and Panchayat regimes (Pradhan, 1993).
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The increasing human-wildlife conflict in and around PAs is proving to be one of the greatest challenges
faced in wildlife conservation, especially that of endangered species (Bajimaya, 2012). Humans are most
likely to come in contact with wild elephants, tigers, leopards, rhinos, bears, wild buffalos, wild boars,
deers, and monkeys. Human-wildlife conflicts result in crop damage, livestock depredation, property
damage, as well as injury and death. Similarly, wild animals are affected by retaliatory killings, injuries,
trapping, electrocution, poisoning, and habitat disturbances. Wild elephants are reported to be the most
pervasive human casualty. Yadav (2007) reports the killing of 18 wild elephants and 66 human
casualties by wild elephants in five districts of eastern Nepal from 1986 to 2002. In the past 27 years,
tigers have killed 97 people in Nepal. There has been a significant increase in the number from an
average of 1.5 persons per year from 1979 to 1998 to 8.25 persons per year since 1999 (Gurung et al,
2006 as cited in Karki and Dhakal, 2012). During the last three fiscal years (from 2009/10 to 2011/12),
there have been a total of 85 human casualties and 64 injuries caused by different wild animals in
different parts of the country (Bajimaya, 2012). Similarly, the loss of livestock has also been significant.
In the last eight years, tigers killed at least 2,923 livestock including sheep, goats, pigs, and buffalo
(Thapa, 2011 as cited in Karki and Dhakal, 2012).
The wildlife damage compensation guideline 2011/12 allows compensation for human death and injury
as well as for crops and other property damaged. The compensation process is, however, complicated
and long. Meanwhile, the compensation amount is nominal. These factors combined create significant
local anger against the park. To reduce property loss from human-wildlife conflict, there is a dire need
for education, awareness, and warning. Similarly, knowledge is also needed on species-wise tackling
method. Park staff members are in need of preparedness training as well a supply of appropriate
equipment. Most importantly, the issue needs to be dealt with by creating appropriate human-wildlife
conflict strategies, resources, and technologies.
VI. Poaching of and illegal trade in plant and animal species
Poaching and illegal trade of plant and animal species is a serious issue for the conservation of
biodiversity in Nepal. Nepal is considered a source as well as transit point in the illegal trade of body
parts of wild animals, especially tigers, rhinos, snow leopards, and musk deer. Illegal transit of red wood
from India to China has remained a regular phenomenon for the last few years. Illegal trade of wildlife
parts is well organized at the transnational level. Evidence shows increased poaching activities during
the decade long armed insurgency from 1996 until 2006. From 2000 to 2005, 157 rhinos died across the
country. Of these, 99 deaths were directly linked to the conflict situation (McNeely, etal, 2006).
Specifically, many security posts in the PAs were deserted during the conflict, providing easy
opportunities to poachers and smugglers (Yonzon, 2004).
Recently, the government has formed a National Wildlife Crime Control Coordination Committee and a
Central Level Wildlife Crime Control Bureau. Both these bodies have been effective in strengthening
enforcement. However, the lack of a forensics lab with appropriate scientific equipment and knowledge
makes species identification and determining cause of animal death difficult. Similarly, there are not
enough resources for purchasing equipment, coordinating logistics and human resources, and for
effective intelligence gathering. Even though poaching is increasing, the GoN is yet to adopt and
internalize crime control in its annual planning system by establishing programs and providing a budget.
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VII. Expansion of invasive alien species
Expansion of invasive alien species (IAS) is a serious threat to the forest ecosystem and biodiversity
conservation across parts of the country. A recent study on IAS by the REDD Cell reports that IAS are
more common in tropical and subtropical regions of Nepal. The report further states that IAS are “the
‘passengers’ of deforestation and forest degradation at their early stage of colonization, which later
change into ‘drivers’ by disrupting regeneration process”. Several of these species have become a severe
threat for the maintenance of wildlife habitat in Nepal’s PAs. Among these species, Mikenia micrantha
has already begun covering grassland, wetlands, riverbanks, and other prime rhino habitat areas in the
Chitwan National Park. This has adversely affected the growth of native plant species palatable to rhino
and deer (DNPWC, 2067/68). To address this challenge, Nepal requires both in-depth studies on IAS as
well the adoption of strategies to control these species. To this end, national quarantine and sanitary and
phytosanitary measures need to be strengthened and strictly enforced (Sharma et al, 2006).
VIII. Effects of climate change
The effects of climate change appear to be emerging as a serious challenge for Nepal. The rapid retreat
of glaciers (average retreat of more than 30 m/year), rapid rise in temperature (>0.06 0C), erratic rainfall,
and increase in the frequency of floods and drought have already been observed. The change in global
temperature suggests that many, if not most, wild species will experience climate change as a stressor
that reduces survival and/or reproduction. Climate change has the potential to lead to population
declines, or even extinction (TNC, 2010). The effects of climate change can have a tremendous impact
on all aspects of forest ecosystem services. Mitigating these effects and fostering the adaptation of
biodiversity to climate change is likely to be a grave challenge.
IX. Increase in threatened bird species
Despite increases in conservation areas and conservation efforts, the number of bird species in the
threatened list has increased over time. While 133 bird species in Nepal were on the threatened list in
2004, the number had jumped to 149 species by 2010. Similarly, the number of critically endangered
bird species increased from 40 in 2004 to 61 in 2010. The number of endangered species has also
increased from 38 in 2004 to 50 in 2010 (BCN and DNPWC, 2011). This increase in number of bird
species being threatened every year shows a worsening situation. Birds that rely on habitats and
wetlands are particularly at risk (BCN and DNPWC, 2011; Baral et al, 2012). About 64 percent or 29
species of wetland birds are considered critically threatened or endangered due to habitat loss and
damage, food shortages, fish poisoning, water pollution, invasive weeds, hunting and trapping, and
disturbance and destruction of feeding and nesting sites (Baral, 2009). Similarly, veterinary use of
diclofenac is considered to be an important cause of decline in the vulture population. Protection of
these threatened species, especially wetland birds, is both challenging and necessary.
X. Infrastructure and other development activities in forest areas
Infrastructure such as hydropower dams and plants, transmission lines, highways, and irrigation canals
use large areas of forests causing habitat fragmentation. Today, a number of hydropower projects are
proposed in and around PAs. These types of human-induced interventions have resulted in the
movement of species beyond their areas of origin, fragmentation of wildlife habitats, and ecosystem
disturbances. Bringing a balance between conservation and development needs of people is one of the
biggest challenges.
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4.5.3 Lessons Learnt and Way Forward
The review of MPFS’s CEGR plan suggests the following as key lessons learnt and way forward:

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Policy and legal reform: The legal and policy framework is contested on the process of PA
declaration, governance, and power sharing between government authority and local citizens,
and equity aspects of benefits sharing. A thorough review of the post-conflict political situation
in democratic societies is needed, with a push toward inclusive governance and state
restructuring.
Re-organization and capacity building: The paradigm shift towards community-based
conservation in NPs and WRs requires park staff to shed their traditional role of command and
control. Instead, they need to take up new roles to foster people-centered approaches. To this
end, the DNPWC needs to be re-organized to better manage buffer zone activities. A massive
training program to facilitate the role change of staff is also needed. The DPR needs reorganization, more autonomy, and capacity enhancement to carry out more effective plant
research including bio-prospecting, DNA barcoding, and pest risk assessment.
Representation of protected areas and ex-situ conservation: A large number of threatened
plant species and mid-hills ecosystems are poorly represented by the current PA system. The
network of botanical gardens does not represent the high mountains and the eastern TaraiSiwaliks regions. In order to conserve all ecosystem types represented in the country, there is a
need to develop scientific criteria for the establishment of new PAs and botanical gardens.
Human-wildlife conflict: The human-wildlife conflict needs to be minimized with regular
attention. A holistic approach needs to be taken with favorable government policy, effective
management practices, low-cost technologies, well-equipped emergency response teams, and
rehabilitation of problematic wild animals.
Wildlife-crime control: Institutional and capacity building of central and district level wildlife
crime control bureaus need to be strengthened. Law enforcement agencies need to be
strengthened with appropriate coordination, collaboration, knowledge, database management
system, informant provisions, forensic lab, and logistical support.
Ex-situ conservation: Breeding and plant research centers need further strengthening with
increased budgetary allocation, capacity building, and collaboration with national and
international research organizations.
Research and studies: Studies need to be increased with research on insects, reptiles, and other
animal and plant species in collaboration with national research and educational institutions.
Harmonization with DDCs and VDCs: For the success of conservation efforts, particularly at
buffer zones and conservation areas, the confrontational situation of the local residents with
DDCs and VDCs needs to be resolved. This will benefit both local development and biodiversity
conservation.
Bird conservation: Bird conservation efforts need to be strengthened with habitat conservation,
appropriate protection of endangered species with reference to climate change effects, and
studies of nationally and globally important species in collaboration with communities, civil
society, research organizations, and educational institutions.
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Tourism in protected areas: Sustainable tourism strategies and management plans need to be
developed. Alongside, increases in tourism infrastructure, local capacity, eco-friendly tourism
services are needed. There is a pressing need to diversify tourism pressure from the four popular
national parks.
Climate change adaptation: To deal with the threat of climate change, it is necessary to identify
climate change sensitive species and ecosystems and explore the adaptation strategies.
Gender equity and social inclusion: The GESI vision and strategy of MFSC needs to be rolled
out in the departments with appropriate working strategies developed and implemented.
4.6 Soil Conservation and Watershed Management
The MPFS recognized soil, water, and forests as the principal natural resources for sustainable
development. It acknowledged the very high rate of soil erosion and the rapid deterioration of
watersheds. It aimed to protect and conserve soil, water, and forests through the mobilization of national
and local resources. In order to address the problems, the DSCWM was mandated to plan and implement
mitigation, rehabilitation, and extension/education measures.
The main objectives of the soil conservation and watershed management plan of MPFS were:
 To contribute to meeting the people's basic needs for forest products through conservation and
management of watershed resources.
 To protect the land against degradation by soil erosion, floods, landslides, desertification, and other
effects of natural hazards and ecological imbalances.
To achieve the above objectives, the plan identified primary and supportive components. The primary
component included preventive measures, rehabilitative measures, as well as conservation education and
extension. The preventive measures included on-farm conservation, forest development and
management, shrubland and grassland management, and provision of watershed services in settlement
sites. Rehabilitative measures included treatment on hill slopes including road embankments as well as
control and improvement measures in valleys including waterways. The conservation education and
extension component included the provision of technical and material assistance in mobilizing the
community for soil conservation. Meanwhile, the supportive components included policy and legislation
development, organizational development, staff training, technology development, watershed resources
survey and management planning, and monitoring and evaluation.
4.6.1 Key Achievements
During the plan period a number of preventive, rehabilitative, and supportive measures were taken.
These included on-farm conservation activities in 5,746 ha of agricultural land; rehabilitation of over
10,000 ha of degraded land including 1,600 gullies and 1,000 landslides of various scales; protection of
1,489 drinking water sources; and construction of 847 conservation ponds and run-off harvesting ponds.
The DSCWM, through its 56 district offices, implemented a strong extension and education program.
More than 412,000 copies of extension materials were produced and distributed; 150 adult education
and conservation packages were implemented in rural areas. The physical targets set by the MPFS have
not been fully achieved. Much of the progress made by the DSCWM is not directly comparable with the
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target as many targeted activities were either renamed or merged together. New activities which were
not planned by the MSFP were also added. It is, unfortunately, a reality that the implemented activities
are very insignificant in comparison to the people’s demands and to the country’s conservation needs.
The periodic plans were implemented after the MPFS formulated their programs on soil conservation
and watershed management in line with the provisions of the MPFS. In the early years, the periodic
plans stressed land use planning/zoning, people’s participation, hazard mapping, vulnerability
assessment, risk analysis, and early warning systems. In later years, the emphasis was on Chure
conservation, integration of water and agricultural activities with watershed conservation programs,
upstream-downstream relationships, payment for environmental services (PES), and the empowerment
and mainstreaming of Dalits, Adivasis, Janajatis, Madhesis, and other disadvantaged communities.
To support the program implementation, a number of policy documents, plans, strategies, and guidelines
as per the provisions of the MPFS were developed. Nonetheless, the Soil and Watershed Conservation
Act of 1982 has been only minimally implemented to date. As a consequence, protection and regulatory
measures were not enforced in critical watersheds. Institutional arrangements related to the proper use of
land resources and the coordination of the agencies concerned could not be strengthened as envisioned.
Nevertheless, the project modality of the DSCWM was gradually replaced by a program modality as
envisioned by the MPFS. Over time, services were expanded from 25 to 56 districts during the plan
period. A number of trainings were organized to enhance the knowledge and skills of community
members and staff. The impacts of these trainings were, however, not assessed.
Surveys were conducted at the river basin, watershed, sub-watershed, micro-watershed, and community
levels for more effective watershed management planning. Till 2010, a total of 413 watershed
management plans, 304 sub-watershed management plans, and 1,167 community development plans had
been prepared. Some of these plans were also implemented at different scales. While the general
monitoring of these programs is continuing, the condition of critical watersheds has not been regularly
evaluated. Similarly, there has not been adequate research, demonstration, and appropriate technology
development for different physiographic regions.
4.6.2 Key Issues and Challenges
SCWM in Nepal is suffering from a number of institutional, policy, resource, technological, and
management related issues as discussed below:
I. SCWM services limited to small areas
While there is an increased nationwide demand for SCWM services, jurisdiction is limited to small
areas. At present, the SCWM service is provided through 56 District Soil Conservation Offices
(DSCOs), 45 permanent and 11 temporary. The sub-watersheds have been the planning and
implementation units in each district since 1992/93. A sub-watershed comprises an area of 15 to 25 km2.
Depending on its size, each district has from 20 to over 300 sub-watersheds with an average area of 20
sq. km each. Sub-watersheds are prioritized, with management plans prepared and implemented for five
years. About 60 percent of a DSCO’s total annual budget is spent on priority sub-watersheds. The
remaining 40 percent is spent on 'hot spot' treatments on landslides and gullies and on rehabilitating
degraded land. SCWM services cover less than 10 percent of the spatial area within the 56 districts
where they are active, thus leaving larger parts of the country unattended.
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II. Shortage of qualified and well-trained professionals
The DSCWM faces acute shortages of qualified professionals and mid-level technicians to plan and
implement SCWM activities with an integrated approach. There are only 90 technical officers and 229
mid-level technicians in the department. These numbers are too small to address the ever-increasing
needs and demands of people. Considering the extent and intensity of the problem, the existing capacity
of the DSCWM is inadequate to address SCWM in Nepal.
III. Lack of comprehensive policy, coordination, and legal enforcement
Watershed management is affected by a complex hydrological and social system with interaction
between upstream and downstream. This interaction changes over time and space, as population growth
changes the pattern of land use. The SCWM related policies are scattered in various sectoral policies.
However, the coordination of these policies is limited. The SCWM plans have attempted to develop
coordination mechanisms at different levels. But these coordination mechanisms did not work well. A
comprehensive policy, river basin management, and effective coordination among sectoral programs is
lacking in SCWM.
IV. DSCW receiving lower priority within forestry sector
Although SCWM activities are much in demand, the sub-sector has not received adequate priority
within the forestry sector. Of the total annual budget allocated to the forestry sector, the DSCWM has
received less than five percent over the plan period until 2010. The low profile of SCWM within the
forestry sector has also hampered the institutionalization process of the department.
V. Modality of people's participation and weak support system
The SCWM plan has stressed people's participation in all soil and watershed conservation activities.
However, the legitimacy, resources, and modality of peoples' participation are not properly addressed in
policy and practice. Different modalities of people's participation were adopted in different donor
supported projects. User committees were formed in an ad-hoc basis, with no emphasis on capacity
building. There has also been limited progress in linking users to other programs, particularly in water
resource management and agricultural development.
VI. Lack of coordination and collaboration
A number of organizations are engaged in soil, water, and watershed conservation. For example, the
department of Water Induced Disaster Prevention implements a number of projects and activities for the
management and conservation of rivers and river basins. The Water and Energy Commission engages in
policy, strategy, and coordination relating to water resources. The Department of Hydrology and
Meteorology engages in assessing hazards, vulnerabilities, and risks of floods in major river basins. The
Department of Roads, meanwhile, is responsible for roadside stabilization including bioengineering.
There is, however, limited collaboration, cooperation, and communication among these organizations.
VII. Organization and management
DSCWM's organization and management survey was carried out in 2005 to address human resources
issues as the problem limiting provision of services to 56 districts. The survey recommended the
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expansion of the program all over the country with increased staffing. However, this has not yet been
addressed.
VIII. Governance and decentralization
Weak governance in terms of participation, transparency, accountability, and predictability is not
unusual across government institutions in Nepal. Although no systematic studies have been published, it
is common knowledge that transfers and promotions are heavily influenced by political connections over
merit. Some staff members link the lack of professionalism with corruption and the production of poor
quality works. In 2012, four cases of alleged corruption at the DSCWM were under investigation at the
CIAA. The Auditor General has also reported an increase in financial irregularities at the DSCWM.
Internal reports produced by the DSCWM also indicate improper processes and negligence in
implementing technical specifications. A few technicians were reported to be implementing SCWM
activities without approved estimates, measurement books, and design plans.
IX. Institutionalization of community groups
All SCWM activities such as water resource protection, irrigation channel improvement, trail
improvement, gully and landslide treatment, and conservation pond construction/management are
implemented through local people's participation. User groups are either activity based or
settlement/village/ward based. Community Development groups or Poor Occupational Women
Empowerment in Resource Conservation (POWER) groups are formed where CFUGs or Water User
Groups do not exist. Most of these groups are registered at the CDO office, except CFUGs and Water
User Groups. The SCWM groups are neither institutionalized nor have sufficient capacity.
X. Gender, equity, and social inclusion
The MFSC envisioned a deep inclusion of GESI into its program with a vision of "an organization with
a gender and social equity, sensitive and socially inclusive, practicing good governance to ensure
equitable access to and decision making power over forest resources and benefits of all forestry sector
stakeholders". Rolling out of this vision in the context of SCWM is an important consideration.
XI. Limited work on climate change adaptation and mitigation
Although most SCWM activities relate to climate change adaptation, no emphasis was placed on
adaptation and mitigation during the MPFS period. More recently, the GoN approved a Strategic
Program for Climate Resilience (SPCR) with a component focusing on building climate resilience of
watersheds in mountain eco-regions. This pilot project will be funded by the Climate Investment Fund.
The project is to be implemented from January 2014 with the DSCWM as the executing agency.
XII. Erosion vulnerability in Chure area
Chure conservation has become a national issue since the last decade. Realizing the importance of the
Chure watershed, the GoN implemented several projects such as the Chure Forest Development ProjectSCWM Program (1993 to 1997), Chure Watershed Management Project (2000 to 2005), the BioDiversity Sector Programme for Siwalik and Tarai (2004-2010), and the Rastapati Chure Conservation
Programme since 2011. Chure degradation, however, still remains a serious threat. The majority of
people living in Chure do not have any land titles. Forest encroachment is increasing at an alarming rate.
These pressures are particularly felt as the geology of the Chure is fragile and vulnerable to soil erosion.
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To halt the increasing degradation in the Chure, an integrated approach with bio-physical, socioeconomic, and technological interventions is needed.
XIII. Acceleration of erosion through rural road construction
Over the last two decades, rural road construction has become a priority program of DDCs and VDCs.
Across the country, tracks have been bulldozed without considering that the consequent erosion
intensifies soil loss, flash floods, and gully formation. The DDCs and VDCs have paid scant attention to
the erosion, and the DSCWM has been unable to influence them. Such infrastructure projects should
have an environmental impact assessment built-in, alongside conservation provisions and budgets.
XIV. Excavation and haphazard collection of stones, pebbles, and sand in Chure
The massive construction of physical infrastructure in India, adjacent to Nepal, has created an excess
demand for stones, pebbles, and sand from Nepal. If excavation is properly managed, the demand is a
positive economic opportunity. Unfortunately, these products are illegally and haphazardly collected for
transport to India. Improper excavation has led to further soil erosion in the Chure as well as to
sedimentation in the Tarai and Bhabar areas.
XV. Political stability and commitment
Political stability and commitment is critical to the formulation of a comprehensive policy, institutional
development, and for the expansion of the SCWM services across the country. Nepal’s political situation
has, however, been unfavorable for the last decade. In just one example, DSCWM was unable to even
get parliament to discuss its proposed amendments to the Soil and Watershed Conservation Act and
Regulations.
4.6.4 Lessons Learnt and Way Forward
The review of the SCWM plan of MPFS suggests the following as key lessons learnt and way forward:



The existing policy and legal frameworks must be reformed to enhance the scope and extent of
soil conservation and watershed management. A comprehensive policy framework with a river
basin approach is needed. This framework should also influence the amendment of the following
policies and strategies: Water Strategy 2000, Water Plan 2005, and Land Use Policy 2012. The
administrative change the expected federal structure will bring about should be considered when
drafting the framework.
Soil and watershed conservation must be a multi-sectoral effort. Programs across departments
must be informed by an integrated strategy if we are to conserve the Siwalik (Chure) watersheds.
Given the profound need for SCWM services, the DSCWM’s existing organizational setting and
working modality will be unable to fulfill these demands. To overcome this problem, a practical
strategy would be to leverage other agencies’ services for SCWM goals. The policies of the
forestry, agriculture, irrigation, road construction, and local development sectors need to be
influenced to include soil and watershed conservation components in their jurisdiction. Similarly,
SCWM needs to be linked with water management, PES, and with climate change resilience.
As the SCWM is a cross-cutting program, the DSCWM needs to transform itself from
implementer to facilitator. The DSCWM should play an enhanced role in planning, research,
71


technology development, creating low-cost soil conservation techniques, technical backstopping,
as well as influencing policy.
Modalities for increasing people’s participation, especially strategies to reach the poor and the
vulnerable, need to be strengthened and institutionalized. Marginalized groups must have greater
control and ownership over conservation planning, program implementation, and monitoring and
evaluation. To this end, coordination mechanisms are needed at different levels of planning and
implementation.
Governance at the DSCWM and its district offices need to be strengthened in terms of
participation, transparency, accountability, and predictability. Reforms in these areas are central
to curbing tendencies to use political influence to get things done, to set aside professional ethics,
to misappropriate budgets, and to produce low quality work. To enhance good governance,
DSCWM must re-organize with appropriate regulations, trainings, staff management, and
monitoring systems. Similarly, to enhance the DSCWM’s physical facilities, motivational
components including rewards, capacity development, leadership, human resource management,
and space for innovation need to improve. The GESI vision of the MFSC also needs to be rolled
out in the department.
72
Chapter 5: Review of Supportive and Additional Programs
This chapter reviews the six supportive programs: policy and legal reform, institutional reform, human
resources development, research and extension, information and planning assistance, and monitoring
and evaluation programs. It also reviews the activities performed through GESI as well as through the
climate change programs. These two programs were not included in the MPFS. They have, however,
become directly relevant in the execution of forestry programs over the last decade.
MPFS implementation occurred during three distinct political regimes. Developed during the Panchayat
system, the MPFS continued to be implemented during the multiparty system of the 1990s and also
under the new federal republic system since 2007. Such political turmoil, including a decade of armed
conflict, has seriously affected the performance of the MPFS.
Although policy, legal, and institutional reforms are included only as part of the supportive program,
they have become instrumental in the performance of the MPFS. For example, the Forest Act of 1993
and the Forest Rules 1995 have become the main vehicles for mass mobilization in the restoration and
sustainable utilization of forests in the mid-hills. Similarly, amending the Wildlife Act in 1993 provided
a legal framework for involving local people in the management of buffer zones. The Rio Convention of
1992 and the CBD provided strong stimulus for expanding PAs from 7 percent to more than 23 percent
of the country over the MPFS period. Similarly, the jurisdiction of the DSWM has expanded over time,
although its effectiveness in conserving watersheds is debatable.
Some policies have, however, gone against the provisions of the MPFS thus adversely affecting the
forestry sector. For examples, policies as well as the operational environment on forest and NTFP/MAP
harvesting were not conductive to boosting the local and/or national economics. Similarly, sudden
reductions in the human resources allocated to the ministry, its departments, and district offices have
drastically hampered outcomes. Inadequacies in the operationalization of staffing policies, which
demotivate forestry staff from being proactive, are also a major concern. The lack of incentive
particularly impacts research and extension activities. Similarly, extension and publicity activities are
limited to the publication of annual progress reports and the distribution of some seedlings in the field.
The ministry and all the divisions do have monitoring sections which evaluate performance every
trimester, half-yearly, or annually. These evaluations are carried out as per a format generated by the
NPC. A broader review of the forestry program is only carried out during the preparation of periodic
national plans, which span from three to five years. Donors, meanwhile, carry out independent
evaluations for the projects they fund. They use these evaluations as criteria in extending or redesigning
projects. The community forestry division of the DoF holds a national seminar every four or five years.
At this event, multiple stakeholders deliberate on the emerging issues around community and
community-based forestry in Nepal.
5.1 Policy and Legal Reform
The MPFS was formulated during the last leg of the Panchayat regime. After the advent of multiparty
democracy, the MPFS’ concepts were implemented through the Forest Act 1993 and Forest Regulations
1995. During the armed insurgency period from 1996 to 2006, almost all state machineries failed to
73
operate in rural Nepal. Only community based systems remained active. Though the comprehensive
peace accord signed in 2006 ended the violent conflict, the political transition is still continuing.
Throughout the different periods of political turmoil, the provisions of the MPFS have never been
challenged. Nepal has also ratified/signed a number of multilateral environmental agreements after the
MPFS. They include the Convention on Biological Diversity 1992 and numerous climate change
conventions.
The policy and legal reform initiative is one of six supportive programs developed under the MPFS. The
program’s central contribution to the MPFS was the reinvention of forestry programs based on a
partnership between local organizations and the relevant government agencies. The policy and legal
reform program plays a key role in creating a supportive environment for the implementation of the six
primary programs. The MPFS has also identified policy implementation as one of its five strategies.
Table 5.1: Policy and legal reform strategy of MPFS under six primary programs
Primary program
1. Community and
private forestry
2. National and
leasehold forestry
program
3. Wood-based
industries
4. MAPs and other
minor forest
products
5. Soil conservation
and watershed
management
6. Conservation of
Proposed action agenda for policy and legal reform
 Update legislation with the aim of encouraging people to share benefits
and take responsibility for the management of CFs.
 Adopt new forestry policies, legislation, and operational guidelines.
 Reform laws to allow forests to be leased for industrial production.
 Improve leasehold forest laws to make investment attractive to the
private sector.
 Draft policy to provide 50 percent of the raw materials needed for
wood-based industry from leasehold forests.
 Address inconsistencies and ambiguities of policies, laws, and
institutional responsibility to maintain a supply of raw materials for
industries.
 Improve and expand existing wood-based industries through more
supportive industrial policies.
 Make DFOs responsible for the implementation of forest development
activities, production and supply of raw materials, and assisting
communities and private entities on forestry matters.
 Import and export laws should be guided by tax policy.
 Promote regional (SAARC level) treaties for the trade in wood-based
products.
 Develop comprehensive legal provisions and address existing
constraints.
 Calculate royalties based on link to price received by primary producers
and price of commodities/market price.
 Improve customs regulations.
 Develop legislation to empower the National Commission for
Conservation of Natural Resource.
 Develop national land-use policy.
 Declare more areas as protected watersheds.
 Develop policy on people's participation and decentralization.
 Improve legislation for the conservation of ecosystems and genetic
74
ecosystem and
genetic resources
resources.
 Formulate working policies for the consistent and effective
management of protected areas.
 Formulate a consolidated regulation system for parks and reserves,
providing specific regulations for particular parks where necessary.
 Develop working policies on the following:
 Categories of protected areas.
 Conservation of biological resources.
 Management of buffer zone and conservation areas.
 Community development fee and benefit sharing.
 Development of legal provisions on management plans.
Some salient features of the policy implementation strategy include:

Systematic allocation of more development resources to deficit areas.

Payment of market prices for forest products from the national forest to generate revenue for
forest development and management.

Freeing internal trade and transport of timber and fuelwood from all restrictions.

Allowing only finished forest-based products to be exported.

Extension of the land-holding ceiling for private land used in forest production.

Making parastatal organizations compete on equal terms with private enterprises.

Making low-cost financing availabe to private nurseries, forest plantations, and forest-based
industries.

Allocation of sufficient human resources to productive technical forestry work rather than focus
on administrative formalities.

Continuation of the master planning process on policy and legal reform with a comprehensive
legal review undertaken in the immediate term.

Reorganization of existing institutions in order to make them more efficient at and capable of
implementing the proposed programs.

Review of incentives and disincentives to increase participation in forestry programs, followed
by the necessary adjustments.
5.1.1 Key Achievements
The policy and legal program has played a significant role in the successful implementation of the
primary programs. Though many policies, thematic strategies, laws, and guidelines have been
developed, none of these instruments have been explicitly mentioned in the MPFS. Moreover, only a
few policies have considered international environmental commitments, trade standards, and the
75
situation of forest-based industries3. The following sections briefly review the progress made on policy
and legal reform in the forestry sector during the 25 years of MPFS.
I. Community and private forestry & national and leasehold forestry
Both these models of forestry are critical parts of the primary development programs outlined by the
MPFS. As a result, there are many legal instruments and guidelines governing these two programs. For
example, the Forest Act of 1993, an umbrella act for the forestry sector, has been instrumental in
achieving the goals and objectives of MPFS. This act contains the Forest Regulation of 1995 under
which guidelines related to various forest management regimes have been developed. The major legal
characters of these instruments in the context of national, community, leasehold, and private forests are
as follows:
Table 5.2: Legal instrument on all forms of national forests
Legal instruments4
Forest Act 1961
(4th amendment)
Forest Protection
(special
arrangement) Act,
1968
Forest Act 1993
(1st amendment
1999)
(Note that this act
repealed two
previous acts –
Forest Act 1961
and Forest
Protection (special
arrangement) Act,
1968)
Forest Regulations
19955
Amendments: 1st
1999, 2nd 2002, 3rd
20056
Date
1992
Approval
Parliament
1992
(6th
amendm
ent)
1993
Parliament
Parliament
 This umbrella act’s objective is to meet the
basic needs of the public, to attain social and
economic development, to ensure the
development and conservation and proper
utilization of forests, and to extend cooperation
in the conservation and development of all
forest management regimes.
 Provided for the management of forests,
punishment and sanctions against forest
offenders, and other miscellaneous provisions.
Cabinet
 Provided for the preparation, approval, and
implementation of management plans for all
types of forests.
 Provided for the management of private forests.
1999
1995
1999
2002
2005
Major provisions
 Legalized community forestry as envisioned in
the MPFS.
 After the Panchayat system was abolished, its
authority was transferred to the community
forestry user groups.
3
According to the Industrial Enterprise law of Nepal, forest-based industries are the priority industries in Nepal. The
government has been providing some facilities to the sector.
4
Legislative instruments reference the constitution, acts, regulations, directives, and associated guidelines. Note, however,
that guidelines are not legally binding.
5
This regulation repealed five previous regulations: Panchayat Forest Rules 1977, Panchayat Protected Forest Rules 1977,
Leasehold Forest Rules 1978, Private Forest Rules 1984, Forest Product (sales and distribution) Rules 1971; and Forest
Protection (special arrangement) Rules 1971.
6
Through these amendments, procedures for handing over leasehold forests to the private sector were included.
76
MFSC
 Established procedures for managing boundary
conflicts, for action against members engaging
in illegal activities, and on establishing forest
enterprises.
1989
DoF
 General procedure for the formation of user
groups and identification of forest areas to
handover as community forest.
1995
MFSC &
DoF
 Designed four phases of CF: identification
(users and forest) phase; FUG formation phase;
operational plan preparation phase;
implementation and review phase. This
document was one systematic guideline of CF.
 Described the process for forest inventory, data
collection, and using the information to prepare
an operational plan for CF in a participatory
way.
 Revised the 2001 guidelines. New provisions
include an empowerment component; revision
of the operational plan and stakeholder roles;
and monitoring and evaluation of CF.
Community
Forestry Directive
1995
1st amendment
1999
Community
Forestry
Development
Guideline 1989
Guidelines for CF
Development
Program 1995 &
2001 (replaced the
guideline of 1989)
Guideline for
Inventory of
Community Forests
2004
Guidelines for
Community
Forestry
Development
Program 2008
(revised)
Forest Carbon
Measurement
Guideline 2011
1995
1999
2001
2004
MFSC &
DoF
2008
MFSC
2011
MFSC
Collaborative
Forest Management
Directives 20117
2011
MFSC
Formation and
Operational
Directives on
DFSCC, 2011
2011
MFSC
Procedure for
handing over
leasehold forests
for commercial
purposes and poor
2011
MFSC
 Describes the steps and processes related to the
measurement of forest carbon. The guideline is,
however, inadequate to measure forest carbon
at a national scale.
 Directive to ensure sustainable supply of forest
products, environmental protection, and poverty
alleviation through collaborative forest
management.
 Fosters socio-economic transformation of local
communities through sustainable conservation
and management of natural resources.
Collaboration between stakeholders is a key
strategy.
 Describes the process for identifying areas and
conditions for getting leasehold forests, socioeconomic objectives, as well as tax provisions
and monitoring mechanisms.
7
Policies and directives are developed for CFM, with 17 management plans approved for implementation. Provisions for
CFM are, however, written only in the revised Forestry Sector Policy 2000 and in the directives. They do not appear in the
Forest Act of 1993.
77
families 2011
Presidential Chure
Conservation
Program Directives
2011
2011
MFSC
 Seeks to conserve the Chure region, alleviate
poverty, and strike a balance between
development and conservation.
The provisions of the following policies, plans, and strategies are relevant to national forests,
community-based forests, and private forests:
Table 5.3: Policy instruments on all forms of national forests
Policy instruments
Eighth Five-Year
Plan
Date
19921997
Approval
NPC
Ninth Five-Year
Plan
19972002
NPC
Tenth Five-Year
Plan
20032007
NPC
Three-Year Interim
Plan (1)
20072010
NPC
Three Year Interim
Plan (2)
20102013
NPC
Revised Forestry
Sector Policy 2000
May
2000
Cabinet
Leasehold Forest
May
Cabinet
Major provisions
 Increase and stabilize the supply of forest
products.
 Maintain the ecosystem and land fertility.
 Increase public and private sector participation
in forestry.
 Provide income-generation and employment
opportunities for poor and marginal families.
 Maintain supply of forest products through
community forestry.
 Promote export of processed products.
 Ensure regular supply of forest products and
support poverty alleviation.
 Emphasis on conservation of forests and
ecosystems.
 Improved access of the poor, women, and the
marginalized.
 Supply forest products regularly by formulating
and implementing a sustainable and balanced
forest development program with people's
active participation.
 Contribute to poverty alleviation and improved
livelihoods through promotion of ecosystem
services and climate change adaptation and
mitigation by adopting a decentralized and
participatory system.
 Describes the collaborative forest management
system with the support of local bodies.
 Includes new concept of forest management for
the Tarai, Chure and Inner Tarai: block forest
management in the Tarai, conservation in the
Chure, and handing over small areas as CF in
the Tarai and inner Tarai.
 Reemphasizes the MPFS policy.
 Provides for leasing forests to families living
78
Policy 20028
2002

Forest Fire
Management
Strategy 2010
Forest
Encroachment
Control Strategy
2008
June
2010
MFSC

2011
(2068)
Cabinet



below the poverty line.
Provides
for
industry,
institutional
organization, and eco-tourism aimed at poverty
alleviation and economic development.
Contains strategies to manage forest fires and
protect forests, biodiversity, as well as
private/community property.
Seeks to control forest encroachment.
Outlines plan to maintain 40 percent forest
cover.
Explores
alternative
employment
and
livelihoods for the landless.
The effective participation of local communities has positively impacted nature conservation and natural
resource management in Nepal. CFUGs have been instrumental in managing and utilizing natural
resources for community development in a sustainable manner, thus also mainstreaming forest
conservation in development (Khadka et al, 2012).
The latest Three Year Interim Plan (2010-2013) has acknowledged the role of community forestry in
forest conservation, community development, poverty alleviation, social inclusion, and local governance
(GoN/NPC, 2010). Community forestry has received similar acknowledgement in Nepal’s MDGs
Progress Report (2005), with Nepal successfully fulfilling seven environment related MDG goals
(NPC/UN, 2005).
II. Wood-based industries
Developing wood-based industries is an important primary program of MPFS. The MPFS had
recommended addressing inconsistencies and ambiguities in policies and a clear delineation of
institutional responsibility to maintain a sustained supply of raw materials for industries. After the
approval of the MPFS, (though there is no explicit link between the MPFS and the policy reforms), the
following legal and policy instruments were formulated.
Table 5.4: Policy and legal instruments on wood-based industries
Legal & policy
instruments
Industrial
Enterprises Act,
1992
Date
Approval
1992
Parliament
Forest Product
2000
(Timber/Firewood)
Collection and
Sales Directives,
2000
8
MFSC
Major Provisions
 Gives first priority to forest and agricultural
enterprises.
 Provides tax incentive and other privileges to
agriculture-based industries if they fulfill
environmental norms.
 Outlines legal provisions for marking, logging,
collecting, and auctioning timber in all types of
forests.
 Outlines provisions for collecting royalty on
timber supplied for wood-based industries and
The leasehold guidelines were developed nine years after this policy document came into being.
79
Forest Product
Auction Procedure
Directives, 2003
Micro Enterprise
Policy, 2008
2003
MFSC

2008
DoE


Industrial Policy,
2011
2011

Cabinet

for household consumption.
Describes procedure for auctioning wood-based
products to industries and/or private
companies.
Describes the process for establishing forestbased microenterprises.
Provides special privileges for the operation of
micro-enterprises.
Prioritizes industries based on agriculture and
forestry.
Emphasizes the development of cottage and
forest/agro-based microenterprises as sources
of rural employment.
III. MAPs and other minor forest products
The MAPs and other minor forest products program is the fourth primary program of the MPFS. The
MPFS recommended comprehensive legal reforms including of the customs regime for this sector. It
also argued that the royalty system needed to be linked to the price received by primary producers as
well as the final market price of the commodities. The following policy and legal instruments, a few in
line with MPFS, exist today:
Table 5.5: Legal and policy instruments on NTFPs/MAPs
Legal & Policy
instruments
Forest Act 1993
Date
Approval
1993
Forest
Regulation 1995
1995
Parliament  Promotes community forestry (Article 25), supports
leasehold forestry (Article 31), and encourages
conservation of NTFP (Article 70a).
 Continues strict regulation of community rights to
NTFPs/MAPs.
Cabinet
 Describes the restrictive procedures required to utilize
NTFPs and MAPs (Rules 11, 12, 13, 14).
Herbs and NTFP
Policy 2004
2004
National
Biodiversity
Strategy 2002
MFSC
Major provisions
 Seeks to bolster economic development through
sustainable management of herbs and NTFPs at all levels
 Stresses sustainable conservation, people's participation,
flexible tax system, verification processes, new
technologies for processing, capacity building, and
incentives.
 Legislative reforms were not made.
 Provides a systematic approach to the promotion of
NTFPs.
 Prioritizes equitable benefit sharing and sustainable
harvests.
 No legal mechanisms developed due to lack of follow up
post-NBS.
80
Guideline for
NTFP-Based
Enterprise 2005
2005
MFSC
Resin Collection
(Procedure)
Directives 2007
2007
MFSC
NTFP Inventory
Guideline 2012
2012
MFSC
Gazette
Notification (See
annex 2)
Eight
times
after
MPFS
MFSC,
DoF
 Provides a process to develop schemes for the promotion
of NTFP-based enterprises at the local level.
 The implementation status of this guideline is weak due
to the lack of coordination between and among
government agencies.
 Describes the area selection procedure, technology,
security measures, and monitoring system for resin
collection.
 Describes fire management and law enforcement
mechanisms used during resin collection by the
communities or private sector.
 While the directive is applicable to all types of forests, it
is particularly enforced in community forests.
 Describes the inventory process for leafs, roots, barks,
flowers, and whole parts of NTFPs.
 Explains the detailed inventory method for 30 prioritized
NTFPs and MAPs.
 GoN has been publishing gazette notifications to
regulate the collection, marketing, and export of various
NTFPs and MAPs.
IV. Soil conservation and watershed management
The MPFS had strongly recommended the development of a national land-use policy. It had also
recommended developing policy on people's participation and decentralization. For institutional
coordination, MPFS had suggested legally empowering the National Commission for Conservation of
Natural Resource (NCCNR). The following policies have been developed for the implementation of this
program.
Table 5.6: Legal and policy instruments on watershed conservation
9
Legal & Policy
instruments
Soil and Watershed
Conservation Act,
2039 (1982)
1st amendment
19929
Date
Approval
1982
Parliament
National Action
Program on
Combatting
2003
1992
MoE
Major provisions
 Seeks to conserve land and watersheds by
controlling natural calamities such as floods,
landslides and soil erosion.
 Keeps in mind the basic needs and economic
interests of the general public.
 Provides for a 'Conserved Watershed Area' in which
the act could be implemented.
 Developed for the implementation of UNCCD, the
program emphasizes the conservation of watersheds
with the participation of local communities.
Only the name of local bodies was changed in this amendment. No substantial changes were made.
81
Desertification
2003
Chure Area
Program Strategy
2008
2008
N/A
Nepal Land-Use
Policy 2069
2012
Cabinet
Presidential Chure
Conservation
Program
Implementation
Directives 2068
2011
MFSC
 Seeks to create an enabling environment for all
stakeholders so they can contribute to the
conservation of the Chure.
 Emphasizes the need to fulfill livelihood demands of
people dependent on forest resources in an equitable
manner.
 Seeks
socio-economic
and
environmental
development of the country through the optimum
utilization of land and land-based resources.
 Promotes utilization of land based on its
classification.
 Promotes conservation of the Chure region to
maintain ecosystem integrity, to contribute to
sustainable development, and to support poverty
alleviation.
In the past, the site-specific watershed conservation projects were implemented in Phewatal, Kulekhani,
Bagmati, Tinau, Begnastal/Rupatal, and Shivapuri watershed areas over a long period. Likewise, IRDP
projects were implemented in Mahakali, Karnali, Rapti, Rasuwa-Nuwkot, and Sagarmatha. The Soil and
Watershed Conservation Act 1982 has not been implemented since it was implemented in the Kulekhani
and Phewatal watershed area some years ago (GoN/ADB/FINIDA, 1988).
V. Conservation of ecosystem and genetic resources
The MPFS highlighted the need to reform policy guiding the conservation of ecosystem and genetic
resources. The MPFS had called for a set of consolidated regulations, with specific guidelines developed
for specific parks as necessary. The third and fourth amendments of the National Park and Wildlife
Reserve Act took this suggestion on board, providing for conservation areas management and buffer
zones across parks. Nepal has since developed a number of procedural and policy provisions for the
management of protected areas. Some important laws and policies are listed below.
Table 5.7: Legal and policy instruments on protected areas
Legal instruments
National Park &
Wildlife Reserve
Act, 197310
3rd amendment in
1989; 4th
Date
1973
1989
1993
Approval
Parliament
Major provisions
 Incorporated
provisions
to
manage
conservation areas through semi- or nongovernmental organizations (3rd amendment).
 Incorporated provisions on buffer zone
management, user committee/group formation,
10
Ten regulations are enacted under this act. They include: National Park and Wildlife Conservation Regulation 1974,
Chitwan National Park Regulation 1974, Wildlife Reserve Regulation 1977, Himalayan National Park Regulation 1979,
Khaptad National Park Regulation 1987, Bardiya National Park Regulation 1996, Buffer Zone Management Regulation
1995, Conservation Area Management Regulation 1996, Conservation Area Government Management Regulation 2000,
Kanchanjanga Conservation Area Management Regulation 2007.
82
amendment in
1993.
Wildlife farming
breeding and
research procedure
2003
2003
MFSC


Procedures for
handing over the
management of
protected areas to
NGOs and other
organizations 2003
2003
MFSC
Procedure for
handing over the
land of protected
areas for
infrastructure
development 2008
2008
Cabinet
Wildlife
Compensation
Directives, 2009
2009
MFSC
National
Biodiversity
Strategy 2002
Sustainable
Development
Agenda for Nepal
2003
2002
Cabinet
2003
Cabinet
Tarai Arc
Landscape (TAL)
Strategic Plan
(2004-2014)
Sacred Himalayan
Landscape (SHL)
Strategic Plan
(2006-2016)
2004
MFSC
2006
MFSC
National
Biodiversity
Strategy (NBS)
2006
MFSC


benefit sharing (30-50% for BZ), and
compensation (4th amendment).
Seeks to conserve wildlife sustainably to create
jobs and generate income.
Seeks to involve the private sector in wildlife
conservation.
Seeks to involve NGOs and other organizations
in the management of protected areas.
Creates policies to generate income for the poor
and create employment through the sustainable
management of protected areas.
 Seeks to mitigate the impacts of infrastructure
development.
 Seeks to contribute to national development.
 Seeks to maintain consistency in development
activities in protected areas.
 Seeks to generate extra resources for the
management of protected areas.
 Describes criteria and procedure for getting
compensation and the limitations on
compensation amount.
 Seeks to conserve biological diversity,
maintains ecological processes and systems,
and share benefits equitably.
 Promotes people’s participation in forestry
resource development, management, and
conservation.
 Ensures that protected areas bring economic
benefits to local communities by promoting
protected areas as tourist destinations.
 Envisions a globally unique landscape where
biodiversity is conserved, ecological integrity is
safeguarded, and sustainable livelihoods are
secured.
 Envisions a landscape where the biological and
cultural treasures of the world’s highest sacred
mountains and deepest valleys are safeguarded.
 Ensures people’s rights over resources and
sustainable livelihoods.
 Contributes to achieving the goals and
objectives of NBS.
 Identifies 13 priority projects spanning a five83
Implementation
Plan (2006-2010)
National Agrobiodiversity Policy
2008
Species
Conservation
Action Plans
year period.
2008
MoAD
2010
MFSC
2006
MFSC
MFSC
Rangeland Policy
2012
2012
Cabinet
National Wetland
Policy 2003
2003
MFSC
National Wetland
Policy 2012
(repealed previous
policy)
2012
Cabinet
 Seeks to conserve and sustainably use
agricultural genetic resources/materials and
associated traditional knowledge.
The Elephant Conservation Action Plan 2010
 Seeks to save elephants in the wild from
extinction by addressing habitat loss and
mitigating escalating people-elephant conflict.
The Greater One-Horned Rhinoceros Conservation
Action Plan (2006 - 2011)
 Promotes in-situ conservation to ensure
recovery of rhinoceros population numbers.
 Tiger Conservation Action Plan (2008-2012)
 Snow Leopard Conservation Action Plan
(2005-2015)
 Vulture Conservation Plan (2009-2013)
 Seeks to improve the livelihoods of rangelanddepended communities.
 Promotes sustainable management of rangeland
through scientific and customary practices.
 Seeks to conserve and manage wetlands
sustainable through participation.
 Conserves
wetlands
for
sustainable
development and environmental conservation.
 Promotes sustainable use of wetlands through
sustainable management.
VI. Influencing sectoral laws and policies
As the practices of other sectors impact forestry, the MPFS had called for the harmonization of all
policies and laws pertaining to natural resources management. In this context, the following policies are
important for forest management: Nepal Environmental Policies and Action Plan (NEPAP) 1993,
Environment Protection Act (EPA) 2053 (1997), Environment Protection Rules 2054 (1997), Local-self
Governance Act 1999, Nepal MDG (Goal 7), Sustainable Development Agenda for Nepal 2003,
Agriculture Perspective Plan (APP) 1995/96 and 2014/15, National Agricultural Policy 2061 (2004),
Agriculture Development Strategy 2013 (Draft), Irrigation Policy 2060 (2003), Hydropower
Development Policy 2001, Climate Change Policy 2011, NAPA 2010, LAPA framework 2012, Low
Carbon Development Strategy (in process), Biomass Energy Strategy (in process), Industrial Policies
2011, and the Water Resource Strategy 2002, among others. These policy documents are instrumental in
mainstreaming forest conservation into the development sector.
To give one example of why non-forestry sector rules are important, the Local-self Governance Act
1999 authorizes local governments to sell forest products, collect revenue, and impose local taxes over
forest products. They can also formulate plans to manage forests within their jurisdiction. Forest
84
protection is also linked to larger political issues. For instance, the High-level Land Reform Commission
2065 and High-level Scientific Land Reform Commission 2066 both recommended land reform as a
strategy to control forest encroachment particularly in the Tarai and Chure regions11. Protecting forests
becomes all the more challenging in a situation where there is rampant landlessness.
VII. International commitments
Nepal has ratified/accessed/signed more than 20 core MEAs (See Annex 3). As a party to these MEAs,
Nepal is formulating a series of bills to comply with these instruments/agreements. A series of bills such
as International Trade of Rare, Endangered and Protected Plants and Species Control Bill (2011), Access
to Genetic Resources and the Fair and Equitable Sharing of Benefits Arising from their Utilization Bill
(2000), Industrial Enterprise Bill (2012) and Wetland Management Bill (2013) are in parliament for
discussion. These bills are of high importance for the sustainable management of forest resources.
5.1.2 Key Issues and Challenges
The forestry sector in Nepal is beset with many policy related issues. Despite continued efforts at
reform, achievements have been mixed across sub-sectors. The major constraints are as follows:
 Weak capacity and institutional arrangements.
 Significant differences between policy and practice.
 Inconsistencies and contradictions among forest and other policies.
 Inadequate coordination between programs and inter-sectoral agencies.
 Conflicting roles of forest administration.
 Weak foundation in forest science and management.
5.1.3. Lessons Learnt and Way Forward
In a context where the majority of Nepal’s rural people depend on forest resources for their livelihoods,
there is a need to strike a balance between external driving forces, domestic interest, and local need
when preparing a new forestry strategy. Some key lessons to remember for the future are noted below.
I. Encouraging consistency and predictability of the policy framework
Sectoral policy and laws need to be consistent internally and with other sectors. A forest law may
contribute to policy convergence with other sectors, but it cannot reconcile all policy conflicts and
contradictions. A forest sector legal framework must therefore include a sound analysis of legal
linkages. Policy and legislation should provide consistent signals to decision makers. Changes in policy
should not only be made in consultation with those affected by the reforms but also be consistent and
predictable.
11
High-level Commission on Land Reform (2065), High-level Commission on Scientific Land Reform Commission (2067),
Report of the Commission (2068 BS).
85
II. Minimizing procedures, simplifying regulations, and improving the operational environment
Several examples given above demonstrate that inconsistencies in policies and lack of coordination
between agencies negatively impact governance. The following guidelines can assist in limiting
regulatory inconsistencies and enhancing the operational environment.

Ensure that a coherent and sound forest policy is in place prior to making laws.

Reduce the number of rules in response to legal analysis which identifies overlaps and
inconsistencies.

Adapt remaining rules to ensure consistency with other existing laws, including within and
among different sectors.

Translate new legislative acts into working norms and regulations as soon as possible.
III. Improving cross sectoral-linkages and collaborations
A better understanding of the linkages between different sectors and a coherent and overarching
approach to forest issues can help reduce uncertainty, maximize synergies, and minimize the occurrence
of illegal practices in the sector. Three levels of coordination may be defined (FAO, 2003):

Inter-sectoral (or horizontal) coordination, when problems are considered mainly at the same
level operating in different sectors.

Intra-sectoral (or vertical) coordination, when coordination is based mainly on interaction among
actors operating at different levels but within the same sector.

Multi-level cross-sectoral coordination, linking international and national efforts.
IV. Enhancing institutional capacity
Effective implementation of policy and legislations requires functioning institutions which are
accountable for their actions. In reality, institutions often function poorly. A significant barrier to
effective functioning in the forestry sector is the fact that staff are overworked and underpaid. This is
exacerbated by numerous other issues. Suggestions to address these problems and streamline forest
policies and laws are noted below.

Assess underlying social, economic, cultural, and political causes of non-compliance.

Modify the policy and legal framework based on above assessment, starting with the ongoing
forestry sector strategy formulation.

Analyze the performance and impacts of different sectoral policies and legal frameworks.

Increase clarity, transparency, and consistency of legislations. Draft legislation that is simple,
unambiguous, proven, transparent, and containing minimal discretionary powers.

Ensure a participatory approach to forest law design in order to promote transparency,
accountability, and predictability.

Ensure that laws do not contradict each other.
86

Minimize bureaucracy, streamline legal procedures, and simplify regulations.

Establish international and/or bilateral collaborations.

Ensure cross-sectoral linkages and collaborations to ensure a coherent and holistic approach to
forestry.
5.2 Institutional Development Plan
The IDP was drafted to guide and facilitate systematic organizational development as envisaged in the
MPFS, which had suggested specific institutional reforms. The main objectives of the IDP were as
follows.

Provide effective institutional structures for policy implementation.

Clearly delineate institutional, organizational, and individual responsibilities.

Establish or restructure organizations to ensure effective implementation of the programs.
The IDP proposed a reorganization of the various departments under the MFSC for short and long term
purposes. The short term restructure was intended to be a stop-gap measure while the long-term reform
was envisioned as a continuous process of strengthening the MFSC. The silent features of the plan were:

Institutional development was considered context specific, democratic, community and service
oriented, and flexible. Institutional reform was seen as a continuous process.

Effective utilization and capacity building of existing staff, instead of increasing the number of
posts, was highlighted. Special responsibilities were given to senior staff.

Rational distribution and management of the departments, divisions, and sections in relation to
the new forestry sector policy, revised legislation, and the regrouping of supportive functions at
the ministry level.

Moving donor assistance from a 'project approach' to a 'program approach'.

Stressing integrated forestry sector planning to rationalize and economize overall costs.

Increase the number of technical staff at the field level, reduce non-technical staff, and reverse
the tendency to prioritize hiring for central level posts.

Emphasize mainstreaming, strengthening, and coordination of research and development through
the Department of Forestry and Plant Research (DFPR).

Recognize law enforcement as a complementary strategy in forest, soil, and wildlife
conservation.

Stressed the need to review the overall outcome/impact of the various institutions established to
coordinate between the MFSC and other government agencies working on forage development,
alternate energy, R&D, energy conservation, forest land allocation, and the utilization of forest
products by forestry parastatals.

Explored the need for a new environmental authority structured for better coordination and
surveillance in response to national and international concerns.
87
5.2.1 Key Achievements
As proposed by the IDP, the MFSC and its departments – Department of Forests, Department of
National Parks and Wildlife Conservation, Department of Soil and Water Conservation, and Department
of Forestry and Plant Resources – were restructured. The Department of Forestry and Plant Resources
was created by merging the research part of the Forest Survey and Research Office of the Department of
Forests with the Department of Medicinal Plants. This was intended to centralize the resources needed to
conduct quality research in the forestry sector.
Similarly, efforts were made to restructure, dismantle, or privatize parastatals including: Forest Products
Development Board (FPDB), Herbs Production and Processing Company Ltd (HPPCL), Nepal Rosin
and Turpentine Industries Co. (NRTI), Timber Corporation of Nepal (TCN), Nepal Fuelwood
Corporation (FC), Bhrikuti Paper Mill (BPM), Nepal Paper Industries Ltd (NPIL), Butwal Plywood
Factory Ltd. (BPF), and Royal Drugs Ltd (RDL). Among these parastatals, the TCN and FC were
merged and the Royal Drugs Ltd was transferred, along with its staff, to the Ministry of Health. Bhrikuti
Paper Mill, Nepal Paper Industries Ltd, Butwal Plywood Factory, and the Nepal Rosin and Turpentine
Industries were privatized.
After the implementation of MPFS, drastic institutional changes in structure and staffing were made in
1993 and 2000. The reform of 1993 was much influenced by the recommendation of the High-Level
Administrative Improvement Commission of the then GoN. This Commission particularly emphasized a
reduction in staff, especially at the central level. A total of 171 (66.8 percent) positions were removed
from the MFSC headquarters, reducing the number of staff from a total of 257 to 86. The number of
posts at DoF headquarters was reduced from 186 to 130 (30.11 percent). The number of posts at the
DSCWM was reduced from 124 to 86 (30.6 percent). At the DNPWC, 26 (36.62 percent) posts were
removed, reducing the number of staff from 71 to 45. And at the Department of Plant Resources, 349
(54.87 percent) posts were removed, reducing the number of staff from 636 to 287.
A new semi-autonomous Centre of Forest Research and Survey was formed by merging together the
Forest Survey and Statistics Division of the MFSC and the Forest Research Division of the DFPR.
Similarly, a new Department of Plant Resources (DPR) was formed. Five Regional Forest Directorates
under the DoF were transferred under the MFSC.
Another restructuring was carried out in July 2000. The main focus of this reform was also to rename or
create several divisions and sections as well as staff positions. The semi-autonomous FRSC was
upgraded to the Department of Forest Research and Survey (DFRS). Both sets of reforms, undertaken
by the GoN in general and the forestry sector in particular, undermined the strategies set by the
IDP/MPFS. These reforms neither considered the spirit nor the long-term goals envisioned by the
MPFS. They also could not address issues such as the forestry sector's social image, leadership,
managerial skills, professionalism, and the retention of proactive forestry professionals or change agents
in government service. These reforms were more influenced by the High-Level Administrative
Improvement Commission and the Structural Adjustment Program of the World Bank than the
recommendations of the MPFS.
88
5.2.2 Key Issues and Challenges
Looked at from an organizational development perspective, the challenges of the forestry sector can be
categorized into four major areas: policy and legal instruments; governance system; enabling working
environment including human, physical and financial resources as well as personal administration
system, and cooperative political leaders; and staff attitude to change and learning. Some key challenges
the forestry sector faces today are as follows:

Across the sector, there is poor commitment to implementing policies, plans, and legislation.
Existing legal frameworks, plans, and programs were/are neither fully enforced nor implemented
effectively. Many legal instruments, such as the Soil Conservation and Watershed Management
Act, are developed as an ideal without considering the ground reality for implementation.
Similarly, the government’s fiscal and energy pricing policies are/were also not conducive to the
sector in terms of encouraging public investments in forestry development and promoting
alternative energy technology.

Government priority is not given to forestry sector. The GoN’s level of commitment to any
sector is reflected in its policy statement and resources, both financial and human. Though the
government made a commitment to keep at least 40 percent of the country’s land under forest
cover, the forestry sector has never been prioritized in terms of resource allocation.

The sector suffers from weak governance policies across the board. Despite continuous efforts by
the government and donor agencies to improve governance, there has been little improvement in
forestry governance. As per media reports and CIIA investigations, corruption is a mainstream
part of the institutional culture in almost all sectors.

The sector undermines the principles and norms of public administration and organization
management. The forestry sector is administered through the GoN’s public administration
system, which is heavily characterized by over-management or over-administration. The poor
state of the administration can be observed from the frequent and unpredictable change of staff.
In these, and other ad hoc decision, no basic principles or norms of public administration are
respected.

Different stakeholders such as informal institutions NGOs, and private actors undermine the
roles and responsibilities of the sector. Formal and informal institutions present in rural areas
(such as VDCs, CFUGs, NGOs etc) are undermining the government programs, frequently
resulting in counterproductive outcomes. The sector also undermines itself by assigning roles to
the forest administration which do not fit the current local, national, or international contexts.

There is weak coordination and communication across the board. Stakeholders in the forestry
sector are poor at coordination, cooperation, and collaboration within and outside the sector.
Within the government system, both intra- and inter-departmental/ministerial coordination is
very weak. The communication system and extension mechanism are still traditional and
fragmented.

The parallel project structures functioning in the districts are replacing government roles. The
majority of donors work directly with local NGOs, establishing parallel offices at the project
sites/districts. This greatly undermines the government institutions. The MPFS stressed a
89
“program approach” to forest investment and management to remedy the fragmentation of
foreign assistance in the forestry sector. However, the “project approach” has prevailed.
Similarly, donor policy on forestry assistance has not been harmonized with the Foreign Aid
Policy 2008, and in line with international commitments and instruments.
5.2.3. Lessons Learnt and Way Forward
This review of IDP combined with contemporary literatures on institutional, organizational, and
governance aspects of the forestry sector suggest the following lessons for the future.

Make policy instruments more decentralized and context specific to create an enabling working
environment. It is well-recognized that the policy and legal instruments of Nepal’s forestry sector
are pro-community and decentralized. However, their effectiveness in terms of addressing
prevailing issues is not encouraging. As policies and their implementation are determined by the
political economy in general, their design and effectiveness are changed as the political system
changes. In order to create an enabling environment within the context of the presently fragile
and unstable political environment, the following is needed:
a) Make policy environment more context specific and develop operational tools.
b) Make the monitoring and evaluation system more effective so that its outcome could be
used for policy feedback.
c) Make regulatory and fiscal policies more conducive to better performance.
d) Harness the comparative advantages from initiatives on environmental conservation and
utilization.
e) Synchronize and harmonize the sectoral and extra-sectoral policies.

Reinvent organizations and reorient forestry personnel. Experiences from past organizational
reforms are not encouraging; these reforms could not distinguish between superfluous and
fundamental changes. For effective reform, organizations need to be considered living or
learning organizations, capable of sensing emerging changes and adapting themselves. Shifting
the working approaches from 'command and control mode’ to the more appropriate 'coordinate
and connect' mode involves enormous challenges. Packages to enhance existing capacity have
not been effective. For significant impact, result-based capacity building programs must be
implemented. Further, these programs must be aligned with an organizational focuses on
developing new attitudes and initiating changes in the mindsets of staff. Such a reform can
improve the governance, service delivery, efficiency, and productivity of forestry personnel. A
reorientation of this scale would require the following:
a)
b)
c)
d)
e)
Reinventing forestry institutions and developing them as learning organizations.
Reorienting the mind-sets, skills, and roles of forestry personnel.
Assessing the relevancy, effectiveness, and productivity of existing institutions.
Mobilizing social networks and other new actors for forestry development.
Improve public relations of the forestry institutions so that they are trusted by the general
public.
90

Enhance coordination, communication, and collaboration with actors beyond forestry. Though
the forestry sector involves many interdependent actors with diverse needs, the basic principles
of coordination, communication, and collaboration are poorly internalized. There is a lack of
decentralized and context specific coordination mechanisms. Which institution will play the
coordinating role is a key question. Any organization from local government to the private
sector, civil society to media could play this role, becoming an 'agent of change' in providing an
enabling investment environment and required technology support.

Make foreign aid consistent and compatible with Nepal’s needs and priorities. The foreign aid
policy is an integral part of Nepal’s development policies and priorities. But effective aid
disbursement is possible only when the aid policies and working mechanisms of all the donor
agencies are synchronized with each other and with those of the forestry sector. Such
synchronization would bring the donors in compliance with the Busan Partnership for Effective
Development Cooperation, 2011. Similarly, the GoN and the forestry sector should focus on
improving the quality of domestic policies and harnessing the capability of its human resources,
thereby creating an enabling policy and investment environment.
5.3. Human Resources Development
The HRD plan aimed to develop the capacity of the people involved in implementing forestry
development programs. The plan discussed the status of human resources at the MFSC, the parastatals,
and at organizations providing training services. Demand and supply projections were made to identify
possible gaps needing attention through the implementation of the human resources development
program.
The objective of the HRD plan was to provide the human resources needed to implement the MPFS
programs. The objective itself was very narrow, as many other important aspects of human resource
development were missing in the plan including transfer and promotion system, performance
management, career planning, workforce diversity, and succession planning.
5.3.1 Key Achievements
The two post-MPFS organizational restructurings were not compatible with the projection of human
resources made by the MPFS. These changes also appear to have missed the spirit of the MPFS.
Nevertheless, significant progress has been made in some aspects of human resource development, with
clear improvements seen in the training and forestry education sector.
The MPFS stressed “reorienting and retraining forestry professionals and technicians so that they will
shed their traditional ‘police’ roles and adopt new ones as the people’s partners in development”. The reorientation and re-training was particularly emphasized in the Community Forestry Development
Program. Since then the reorientation was emphasized by all institutions and projects within the forestry
sector, a HRD and Training Division was institutionalized at the center and at five regional
headquarters. Bilateral and multilateral projects under the MFSC have also provided a number of
trainings to develop capacity of forestry staff within their project areas. Staff member were encouraged
to participate in short-term training courses, seminars, workshops, and study tours at the district,
regional, national, and international levels. All these trainings have played a significant part in the
changing the role of forestry field staff from ‘policing’ to ‘facilitating’.
91
Forestry education has also been expanded over the years. The Institute of Forestry (IOF) has started
MSc, M.Phil, and Ph.D. programs to its existing bachelor level education. The Kathmandu Forestry
College (KAFCOL), a public company which offers a Diploma in Forestry Science, BSc in Forestry,
and MSc in Geographical Information Systems has been established. More recently, a new Agriculture
and Forestry University (AFU) was established in 2010. This is the first university in the country
offering a BSc in forestry. The AFU also intends to add masters and Ph.D. programs in forestry science.
Many students also continue their higher studies at the Master’s and Ph.D. level at overseas universities,
particularly in USA, UK, Australia, New Zealand, the Netherlands, and Thailand.
The use of technology by MFSC staff, for example computer literacy as well as use of GPS and GIS
technology has also increased. Staff members are also seen enhancing their social skills related to public
interactions, public speaking, and participatory skills.
A key achievement, at least on paper, is the MFSC’s human resource strategy prepared in 2004. The
strategy report outlines the HR vision, strategic actions to reach the vision, a set of staff development
and training principles, and a series of practical suggestions for implementation. The strategy is,
however, yet to be approved and implemented.
5.3.2. Key Issues and Challenges
The key issues and challenges in human resource management and development are as follows:

Human resource systems on appointments, transfers, appraisals, promotions, and
development/training are not streamlined as the MFSC does not have an operational HR policy.

The MFSC lacks a comprehensive HR information system database with personal information,
career data on postings, transfers, development, and promotion, as well as readily available
appraisal information.

A process of job/person profiling is needed to match people to jobs. Information is available to
create job profiles for all positions, including a summary of the characteristics of the person
suited to the particular job. However, comprehensive job descriptions including roles,
responsibilities, authority, access to resources, reporting relationship, and competencies required
as well as individual job profiles do not exist (Dearden et al, 2004). The absence of such
information, complemented by political influence, has made the ministry unable to select the
right person for the right job during recruitment/placement or transfer. Further, the orientation
given to new recruitments and the hand over between staff leaving and entering is not adequate.
This has resulted in discontinuity, with institutional memory not adequately transferred. In most
cases, transfers are unplanned, unpredictable, and untimely. Moreover, the transfer decisions are
adhoc, carried out without a consultative process and without following uniform criteria.

Employees working in hierarchic organizations are enthusiastic to reach top levels of the
hierarchy. But limited promotion opportunities force staff to remain in the same position for
many years. Promotions are based on numerical calculations obtained from performance
appraisal records of the current job. This puts the focus on accumulating points by fulfilling
requirements rather than on being innovative, productive, and competent. The promotion system
92
neither evaluates the innovativeness nor the productivity nor the ability to cope with higher-level
responsibilities.

The performance appraisal form is poorly designed, and the process is neither consultative nor
constructive. The outcome of the appraisal is used only for promotion purposes without
connecting to career path or development needs. The appraisal system does not identify the
strength and weakness of the staff, there is no feedback system to help them improve, and there
is no grievance handling system associated with the outcome.

In any organization, staff may have grievances related to structural and/or individual processes in
the work place. If the management listens to and addresses the problems of the staff, the
organizations performance increases. To effectively address issues, the organization must have a
grievance handling mechanism in place. Though the Ministry of General Administration has
prepared grievance-handling directives 2063 (2006 AD), it is has been found neither functional
nor effective in the MFSC.

A comprehensive Training Needs Assessment for MFSC was carried out in 1991. No similar
exercise has been undertaken since. As a result, there is a very weak linkage between training
and enhanced job performances. Further, poor records are kept of the training received by staff
members, making it difficult to emphasize expertise development. Overall, a system of training
staff members according to the organization’s objective has not been established.

The role of management and leadership is to create an enabling working environment and
motivate staff to do good work. However, the existing management and leadership style in the
forestry sector can be characterized as haakim culture, rooted in a feudal state. Such a style does
not inspire staff to provide quality services to people. The forestry sector has not able to make
use of recent findings on leadership and management in order to enhance the performance of
forestry organizations.

The attitudinal aspects of staff psychology including intention, commitment, enthusiasm, and
inspiration are often ignored in development organizations. Similarly, that unspoken cultural
aspects including beliefs, traditions, and practices influence staff perceptions of ideas such as
leadership and services is not considered (Pradhan 1993). It is widely believed that decisions in
the government system are manipulated by connection and kinship, source-force (influence by
power and connection), and afno manchhe12 (Bista, 1991). This feudal culture was inherited from
the sixteenth and seventeenth century Moghul regimes, and further nourished by the autocratic
Rana and Panchayat systems. This feudal culture continues to influence decisions about postings,
transfers, promotions, performance evaluation, accountability, and rewards within the forest
bureaucracy (Acharya et al, 2008).

During the beginning of the MPFS, the Panchayat regime was in place in Nepal. In 1990, a
popular people's movement established a multi-party democratic political system. In 2006, the
end of a ten-year armed conflict ended the constitutional monarchy and established Nepal as a
federal republic. Such political changes have implications for human resource development in
the government in general, as well as in the forestry sector. Because the country still does not
“Afno manchhe is the term used to designate one’s inner circle of associates. It means ‘one’s own people’ and refers to
those who can be approached whenever need arises.” (Bista 1991).
12
93
have a constitution, there is uncertainty over the future roles/responsibilities and
structure/mechanism of the MFSC in the anticipated federal system.

Following the political change of 1990, Nepal adopted a liberal economic policy which exposed
Nepalis to the international arena. Competent Nepali professionals are getting well-paid job
opportunities abroad. Similarly, donor projects, INGOs, NGOs, and the private sector within the
country are paying attractive remunerations. This has made it a challenge for the forestry sector
to retain competent human resources within the government system.

An update of quantitative human resource projection made by the MPFS is needed. A projection
of this sort is very challenging in a situation where the future structure of the state – federal,
decentralize, or unitary – is unknown.

Undue political pressure and personal bias are often reported in the placement and transfer of
staff. This often results in poor job implementation and significantly affects morale.

Gender, equity and social inclusion are considered contentious issues in forestry sector
governance. As in other bureaucratic organizations in Nepal, the forestry sector is dominated by
males of the Brahmin, Chhetri, and Newar (BCN) ethnic groups at numbers disproportionate to
their total population (Rai Paudyal and Ghale, 2008). This lack of inclusions is due to various
structural, social, and cultural factors including unequal access to and control over economic and
political assets across class, caste, and gender lines. With many of the same structural, social, and
cultural factors still in place, there are significant challenges to successfully implementing
gender, equity, and social inclusion programs.
5.3.4 Lessons Learnt and Way forward
The review of the HRD plan of the MPFS suggests the following as key lessons and way forward:

Although the MFSC’s organizational structure contains a planning and HR division, HR
management and development are of the lowest priority. The ministry needs to establish HRM
and HRD as a core function. This function also needs to be transformed from an administrative
orientation to managing people with an emphasis on performance, development, career, and
welfare.

The forestry sector needs to develop and adopt a series of HRM/D policies sensitive to gender
and social equity concerns. Such policies need to include affirmative action for the inclusion of
women, indigenous people, and Dalits; management from people’s perspective; selection and
appointment based on merit; performance based transfers and promotions; institutionalization of
learning and development; and a fair and effective grievance handling mechanism. The MFSC’s
Human Resource Strategy of 2004 must be updated to reflect the changed context and
subsequently implemented.

The MFSC must develop HR operational guidelines including principles, rationale, objectives,
strategies, and mechanisms covering a wide range of thematic areas from recruitment and code
of conduct to counseling and grievance handling in accordance with the civil service act and
regulations.
94

The MFSC must strengthen its formal and informal linkages with academic institutions
providing forestry education and training. This will enhance practical forestry education as well
as facilitate regular updates in the forestry curricula in line with new and emerging needs of the
sector. The MFSC also needs to build close links with the CTEVT to accredit many of the
forestry trainings delivered by MFSC and other organizations.

A comprehensive human resource information system database needs to be developed and
implemented at the MFSC in order to facilitate HR management. The database should include
personal information, career information, appraisal information, performance histories, and key
achievements.

A competency approach to staff development and training is necessary. In drafting a competency
framework, emphasis needs to be given to improving the qualities of pre-service and in-service
training. Training should not be simply treated as a reward to staff but an investment for better
performance in the future. Thorough training needs assessments and training evaluations must be
conducted across the forestry sector. To encourage learning and development, learning centers
and libraries also need to be developed.

Leadership and management are the primary function of all senior staff, DFOs, DSCOs, and
wardens. The MFSC does not, however, prioritize strengthening their management and
leadership skills. Nevertheless, a few senior staff are given opportunities to participate in
management training courses offered by the Nepal Administrative Staff College. The MFSC
needs to provide staff management education, training, counseling, and mentoring services.
Links have also to be developed with national and international management institutes.

Efforts need to be made to initiate a change in attitudinal and cultural aspects of the forest
bureaucracy. Developing a code of conduct and openly discussing behavior within the forest
bureaucracy can be a starting point. Concerted efforts need to be made to discourage misuse of
the afno manchhe, haakimi, and chakari behavior. Focus should be given to promoting positive
conversations, positive attitudes, commitment, and professionalism.

There is a need to initiate dialogue to identify/develop roles, functions, and structures of the
MFSC in the expected federal system of governance. Preparation of this nature will ensure that
the role change is not abrupt and chaotic.
5.4 Forestry Research and Extension
According to the MPFS, the main aim of this program was to strengthen the research and development,
as well as the forestry extension and public information capability of the forestry sector. Promoting the
utilization of the research was also a goal. Towards this end, some key strategies were drafted including
the promotion of research and extension in one package. A three phase extension method including mass
communication, field extension, and transfer of technology to be adopted was also planned. The other
key pillars of the program were strengthening research in collaboration with the IOF and other agencies
as well as decentralizing information dissemination and outreach activities.
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5.4.1 Key Achievements
The overall achievements of the forestry research and extension program remained mixed. Ambiguities
on the institutional arrangement, mainly the leadership’s short sighted decision to alternately classify the
forestry research agency a center created a lot of confusion. Overall poor budgeting in this program also
resulted in poor outputs.
A regular Radio program called Ban Batika and a publication called Hamro Ban were some of the
regular activities carried out by the extension unit. But, because the print and electronic media used were
of a more technical nature, they only attracted limited audiences and readers. The transfer of technology
component remained problematic as the focus remained on ‘scientific knowledge’ rather than a mutual
exchange of indigenous local knowledge and formal scientific knowledge.
Achievements of the decentralized extension activities also remained mixed. Though range posts were
established at the sub-district levels, each post covered more than one VDC. Forestry thus remained
isolated from and out-of-synch with the local government at the VDC level. The community forestry
programs of the mid-hills were an exception, benefitting from the extension services of the range posts.
An Extension and Communication Division at the ministry was envisioned but not implemented. At the
departmental level, the Department of Forests, the Department of Soil Conservation and Watershed
Management, and the Department of Plant Resources have extension sections. They are, however,
constrained by the lack of skilled human resources and an inadequate budget. The Department of
National Park and Wildlife Conservation has the Conservation Education Section and Department of
Forest Research and Survey has an Information Section. But neither is fully functional. Similarly, at the
regional level, the Regional Forestry Directorate was made responsible for the coordination, planning,
monitoring and supervision of all the forestry programs. The directorate, however, has to compete with
the respective departments for resources, power, authority, and functions. At the district level, forest
coordination committees were formed and guidelines prepared. These bodies have, however, remained
largely centralized. Ironically, no village level coordination mechanism was crafted. Coordination
between the extension sections of various departments and with parastatals remains poor.
The Institute of Forestry (IOF), though it has expanded tremendously over the years, does not impart
practical knowledge bolstered by internships. Despite the poor institutional coordination, some nongovernment and private sector institutions have emerged. These institutions, in collaboration with Nepali
and foreign institution, fill the research gaps of the forestry sector. For example, research has been
conducted in biomass growth, agro forestry, silvics, and silviculture by FRD/ FORESC/, DFRS, TISC,
and forestry projects. The dissemination of study results to the local communities has, however, been
weak. In terms of the research to be conducted on composition, age, size class distribution, natural
regeneration and yield of the major commercial species as stated in the MPFS, the Tree Improvement
and Silviculture Component (TISC) of the DoF has compiled biomass tables for several tree species.
Further, attempts have been made to respond to the research demand on the problems faced by farmers
on pine forests and Sisso die-back. DFRS has published two leaflets in Nepali related to survey in Sissoo
die-back and its treatment. A documentary was made to cover the preventive and remedial measures of
Sissoo die-back and broadcasted through TV. The problem of adequate distribution of study results,
however, remained.
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5.4.2 Key Issues and Challenges
There is no official research policy yet. A research strategy has been submitted to the MFSC, but has not
been approved. A working procedure of the DFRS and thinning guidelines on Pinus patula and Pinus
roxburghii are some examples of working guidelines developed so far. However, the implementation of
the guidelines is hardly reviewed.
The Forest Research Development Plan (FRDP) states that the reformed organizational structure of the
MFSC must be continued to establish a functionally integrated but physically decentralized institution.
Yet, attempts have never been made to decentralize research offices at the regional level, though
research buildings were constructed in each region for this purpose. The problem of hiring research staff
to work at the regional office is said to have hampered implementation. The FRDP had intended to
continue the National Forest Research Plan (NFRP) of 1981, with special attention given to research on
the transfer of responsibility for forest management and impacts of restricted reserves. But, the NFRP
was not brought into action.
As per the FRDP, the DFRS accepted degrees from relevant fields other than forestry in recruiting staff.
The DSCWM and DPR particularly recruited staff from different fields, other than forestry. Still, the
forestry research team is still low on staff from the fields of economics and sociology. As a result, little
research has been done to understand the linkage between forestry and poverty alleviation, tourism, and
other critical areas. While research from non-governmental organizations has filled some of these gaps,
the research from these bodies has hardly had any effect on policy reform.
The research sector is sorely missing a strategic partnership among government, universities, as well as
non-government and private research organizations. A partnership of this kind may be successful in
bringing attention to the problem faced by local users and farmers, an area receiving scant attention
currently. For instance, the knowledge farmers want on treatment of Sissoo die-back has yet to reach
them.
5.4.3 Lessons Learnt and Way Forward




Better leadership and coordination is needed. MFSC needs to direct the DFRS in forestry
research based on the forest research development plan. The upcoming forestry strategy should
recognize the government body as a coordinator of all stakeholders in the research sector.
A multidisciplinary staff and research center should be built. Research staff should be of both
genders, with expertise in ecology, economics, statistics, and forestry. At least 118 ecosystembased research stations to be coordinated by decentralized units in the five development regions,
should be established.
Research is needed on the contribution of the forestry sector to GDP and should be mainstreamed
with CBS/NPC.
A study is needed to measure feasibility of establishing a National Forest Research Council.
Detailed review of the existing DFRS is needed so as to know and design an appropriate
institutional arrangement to carry out and manage utilization focused forestry research in Nepal.
Previously, a Forest Research and Survey Centre (FORESC) was established but was later
dismantled and replaced with DFRS. However, the incentives and working culture of the DFRS
do not appear to be compatible with research results produced by the DFRS. A possibility is to
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
transfer the DFRS into a National Forest Research Council which will manage research and
coordination among the research institutions.
More research is needed on community based forestry. Existing research notes that community
based forestry and other devolution processes have contributed to increasing forest area and
quality together with social cohesion among forest dependent communities. There is, however,
need for further research on the cost and the benefits of such changes so that sustainability can be
measured.
5.5 Planning and Information
In the MPFS, both the resource information and planning components are lumped together under the
same program. However, the government institutions responsible for these two components are separate.
The Department of Forest Research and Survey is responsible for resource information mainly from the
forest inventory point of view. Meanwhile, the Planning and Human Resource Development Division of
the ministry, planning divisions of the departments, the Regional Forestry Directorate, and district based
organizations are responsible for planning and programming. Although this review combines both the
components, the nature of these two components is different. According to the MPFS, the main aim of
this component is to develop a forest resources information system within the ministry. The information
generated through such a system can be used for long-term and operational planning purposes by the
government, communities, and the private sector.
5.5.1 Key Achievements
The overall achievements of the resource information and planning program remain mixed. Though the
national capacity for resource information generation has not been satisfactory, tremendous progress has
been made in institutionalizing the bottom-up planning process. The two components are discussed in
detail below.
I. Resource information
During the plan period, the National Forest Inventory (NFI) was carried out two times under the
leadership of the Department of Forest Research and Survey. A third NFI is ongoing. The 1999 NFI
classified land-use and estimated forest coverage. Subsequently, data on land-use change from 1999 to
2001 was generated. The latest inventory report is expected to provide similar date for the post-2001
period. The 1999 NFI does not, however, provide disaggregated data and resource maps based on
physiographic regions in Tarai, Siwaliks, mid-hills and high mountain. These areas all have different
forest tenure systems and consequently different land-use change patterns. For example, various
qualitative and quantitative studies show that forests in the mid-hills are better managed, with the
community and private forestry programs having reversed degradation. These studies record a mean 21
percent biomass increase across community forests of all types and conditions measured over a 14 years
period (1.5 percent per year).
In the Tarai region, the forest land has been converted to other land-use categories, especially shrub and
agriculture land. As discussed in section 2.5, the forest area of plain Tarai is declining by an annual rate
of 0.44 percent in the last decade (2000-2010), which is higher than the average deforestation rate of the
last two decades (1991-2010). The quality of the growing stock of timber (over bark) from the reachable
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forests of Nepal has fallen from 519 million cubic metre to 387.5 million cubic metre between the period
of 1986 to 1998 (MPFS, 1988; NFI/DFRS,1999). The average standing timber for Tarai as estimated by
MPFS (1988) was 101.05 m3/ha. However, the latest inventory of 2010-2012 carried out by DFRS
shows that stem volume up to 10 cm diameter is 121.98 m3/ha (FRA/DFRS, 2014). Apparently, the
growing stock of standing timber in Tarai appears to be increasing even though the total forest area is
declining.
Apart from the national inventory, a number of departments have MIS and CFUG database systems with
national level information on protected areas, sub-watersheds, forests, forest products, revenue, user
groups, and membership. The information is recorded and updated annually. In addition, huge amounts
of social and ecological data are generated for the preparation of strategic and operational plans at the
district, sub-district, and local level. These include District Forest Plans, Protected Area Management
Plans, and Watershed Management and River Basin Plans. Similarly, community, leasehold,
collaborative, buffer zone, and soil conservation plans are being prepared and implemented by local
communities. These plans have a large amount of detailed information on both biophysical and socioeconomic attributes of the jurisdiction area. The problem is that the information is not being analyzed in
a way that allows local knowledge to feed into the policy and planning processes that take place at the
national and district levels.
II. Planning
The planning component of the MPFS has enjoyed encouraging results. The MFSC is one of very few
ministries with an institutionalized, participatory bottom-up planning process (see Annex 4). Each
district prepares periodic and annual plans through a consultative multi-stakeholder mechanism. Forestry
officials have realized the importance of bi-directional flow of information from community level to the
central level, and vice versa. Under the leadership of government agencies, civil society and private
sector actors have started to participate in the planning process at various levels – integrated planning
committees at VDC, VDC and DDC councils, regional directorates, departments, ministries, and the
national planning commission.
Through the community and private forestry program, thousands of local institutions have been
established at the community level. In addition, user group networks and a federation of forest user
groups have emerged to safeguard the rights of forest users. Additional service providers such as NGOs,
local government bodies, and private sector agencies have also emerged. These institutions have started
to collaborate not only on planning but also for implementation, joint monitoring, evaluation, reflection,
and learning.
Active players in the forestry sector are becoming increasingly aware of the multi-stakeholder approach
and collaborative mechanisms in forestry. All stakeholders involved in forestry have begun to realize the
need for the active participation of marginalized groups in all stages of project planning,
implementation, and monitoring. There is a similar growing awareness of the need for good governance.
This increased sensitivity on need for equitable benefit sharing in favor of the poor and women has also
become institutionalized. Policy provisions have established the following quotas to promote
participatory planning: 33 percent women in the committees, 50 percent women in key positions at the
user committees, and 35 percent of total expenditure to be allocated to people living below the poverty
line. Through these processes, ground level realities have started to feed into layers of governance.
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Ground realities are thus reflected in policy intentions, and also more or less translated into practice by
innovative officials, in collaboration with NGOs and other stakeholders.
Because stakeholders now work more collaboratively and collectively, power and positions are being
negotiated and redefined. Mutual trust, accountability, and transparency have begun to increase. People
who have gained experience in the forestry sector have contributed significantly to institutionalize local
democracy. The immediate effect has been seen at the local government level where an integrated
planning committee has been made responsible for coordinating the entire sector at the VDC.
5.5.2. Key Issues and Challenges
As noted earlier, the 1999 NFI did not generate information on forest resources disaggregated by
physiographic characteristics and forest management regimes. This is a challenge as detailed data of this
kind is key to effective planning. Similarly, few departments have qualified staff able to regularly update
MIS and the user group database system. Despite the newly emergent consultative and collaborative
culture in the sector, the power imbalance between government and other actors still exists. There is still
a tendency to take unilateral decisions through a non-transparent approach.
5.5.3 Lessons Learnt and Way Forward





Make available forest data and resource maps disaggregated by physiographic regions and forest
management regimes to all relevant stakeholders.
Make use of forest resource data and maps generated by NFI for the preparation of district and
forest management plans at forest, watershed, and protected area levels.
Build capacity of staff responsible for MIS and strengthen the planning and statistical units to
update MIS and data base of user groups.
A financing mechanism with multi-stakeholder representation should be established so that
forestry stakeholders do not suffer from underfunding.
Continue the bottom-up participatory planning process by involving all relevant stakeholders in
the operational planning. Further strengthen the capacity of stakeholders who are a part of the
consultative and decision-making process for policy and strategy development.
5.6 Monitoring and Evaluation
MPFS aimed to institutionalize a system for monitoring forestry development operations and their
impacts. It also sought to process the monitoring data into information that could guide the development
process. Monitoring and Evaluation was one of the supporting programs which envisaged the efficient
and effective implementation of MPFS. The M&E plan designed the following four sets of actions to
guide the process:
 Designing a M&E system for each program.
 Increasing capacity of staff working in M&E division and sections.
 Collaborating with the training section to provide further training in M&E.
 Using advanced techniques of M&E such as remote sensing and GIS.
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To this end, the MPFS developed a strategy to have continuous monitoring and evaluation of targets at
different organizational levels of the MFSC. It developed M&E as a separate component with a
budgetary allocation of NPR 25.2 million from government sources and NPR 113.4 million from
external assistance. The M&E component was largely concerned with progress and impact monitoring.
5.6.1 Key Achievements
The M&E system practiced in the MFSC followed the guidelines set by the NPC. The NPC guidelines
were general, designed to suit all sectors of the GoN. Thus, it did not capture the range and quality of
information required by the MPFS. The NPC itself, though it carried out a periodic review of programs
under the MFSC while preparing its five-year plan (recently three-year plan), was unable to steer and
lead the MPFS programs. On the technical end, the traditional paper-based monitoring used by the
MFSC made it difficult to store, analyze, retrieve, and communicate monitoring data easily. Those
working in the M&E division are also demoralized, as they feel that their job is inferior to other
activities.
A number of departments have, however, developed independent monitoring systems. For example, the
DoF has developed an Integrated National Database System on diverse issues including forest area,
encroachment, and forest products with source of extraction - ie national forests or community forests.
In another instance, the community forest division of the DoF is using a Community Forestry National
Forest User Group Database especially focused on CF. This database provides updated status on the
number and memberships of CFUGs and the forest area under their management. Similarly, the
DSCWM has a management information system, which is a national database system for the soil
conservation and watershed management programs. In the same way, the DPR has prepared a list of
indicators for different sub-components such as biodiversity conservation, biotechnology, cultivation, as
well as research and development of non-timber forest products. Currently, the DFRS is doing forest
inventory using satellite images, a program it had earlier implemented during 1992 to 1996.
Despite all the efforts noted above, progress has been almost nonexistent to date with regard to the four
sets of activities proposed by the monitoring and evaluation plan of the MPFS.
5.6.2 Key Issues and Challenges
 A wide information gap exists due to poor record-keeping and a weak system of reporting. There
are no regular or periodic reviews of current forest conditions or of changes in trends.

M&E systems are heterogeneous and weak. The field offices are required to fill-up and submit
mandatory reporting formats regularly. The offices find these progress reports burdensome. This
situation is more aggravated when different ministries, departments, regional offices, and a
number of donors each have their own formats. The field officers would prefer to fill out one
format, sending copies to different users.
 Motivation level of M&E staff is low. Working in M&E is considered a monotonous job, and devalued within ministries and departments. Often, staff members considered least useful/efficient
are assigned to the monitoring job.
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5.6.3 Lessons Learnt and Way Forward




Strengthen the monitoring divisions of the ministries and sections with appropriate human and
financial resources.
Develop software for monitoring information systems and train persons working on M&E on
how to use it.
Start monitoring governance and project-level monitoring and evaluation.
Establish a practice of Result Based Monitoring and Evaluation (RBME) for all programs under
the MFSC.
5.7. Gender and Social Inclusion
Gender is an important factor in sustainable forest management, community-based in particular, as has
been internationally recognized. Nepal has ratified over a dozen international commitments on
nondiscrimination, gender equality, and social justice. Initiated originally from the international
perspective, these commitments have now become part of the national priority. Government has
especially proven its commitment to good governance through effective decentralization after the
movements of 2006. The GoN now has concrete plans to reach out to women and other excluded
groups.
The MPFS was prepared at a time when gender issues were not as widely considered as they are today.
Nonetheless, the MPFS had ensured critical representation of women in decision-making processes,
especially in community forestry user’s committees. The MFSC developed the GESI in 2008,
identifying four areas of intervention:

GESI sensitive policy and strategy.

Good governance and institutional development.

GESI sensitive budgeting/programming and monitoring.

Equitable access to resources and benefits.
The objectives of the GESI strategy are twofold. First, GESI seeks to assist government, nongovernment organizations, donors, and private sector actors working in forestry to institutionalize social
inclusion into their organizations and programs. Second, GESI seeks to guide all organizations working
in the forestry sector to be responsive and inclusive.
5.7.1. Key Achievements
I. Status of gender mainstreaming in the forestry sector
The GoN has been committed to addressing gender discrimination since its first Five-Year Plan in 1956.
However, the paradigm shifted from Women In Development (WID) to Gender And Development
(GAD) starting from the Ninth Five-Year Plan (1997–2002). These plans have pursued gender equality
and women’s empowerment through a gender mainstreaming strategy. The Interim Constitution 2007
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addresses gender and social development through devolution, decentralization, gender equality, and
social inclusion. It also guarantees social justice and affirmative action for the marginalized and socially
excluded groups. In response, the civil service act and its regulations (1991) also provided 45 percent
reservation for the marginalized groups.
Similarly, the Human Resource Development Strategy (2004) of the forestry sector is GESI sensitive
and consists of a holistic implementation framework focused on affirmative action. There have been
various initiatives to institutionalize GESI concerns in the MFSC including institutionalization of a
Gender Focal Point (GFP) person in each department. There has also been the formation of a gender and
equity working group at the center led by the ministry but with the participation of civil society
organizations and development partners. These initiatives show a certain level of preparedness or
readiness to institutionalize GESI as a crosscutting issue.
Women’s concerns are incorporated in various sectoral management guidelines including the
Community Forestry Development Guidelines 2008, the Protected Area Management Regulations 1996,
Collaborative Forest Management (CFM) Guidelines 2003, Leasehold Forestry Guidelines 2006, and
National Biodiversity Strategy 2002. The significant incorporation of GESI into forestry, especially
community forests, may also be due to the growing interest and intervention of civil society in natural
resource management. For example, women make up 31 percent of community forest user committees,
also holding some key positions. Adhering to GESI provisions, the community forestry guidelines 2008
have specified that women should make up 50 percent of the executive body and occupy one of the two
– chairperson or secretary – executive positions. Additionally, it also mentions that both husband and
wife need to be included as a household member in the constitution of the forest user group. The
guideline provides for the use of 35 percent of the budget to be focused on the poor and on women.
Similarly in other community forest management modalities – leasehold, collaborative and buffer zone –
women’s representation is 39 percent, 12 percent, and 19 percent, respectively.
The state of women’s representation is, however, dismal within the government bodies.
Within the MFSC, women make up only 3.33 percent of employees in contrast to the 33 percent targeted
by the government. An analysis of 67 national policy documents and directives related to gender
responsiveness reveals that only one is negative, 29 are gender neutral, 20 are moderately responsive,
and 17 are highly responsive to gender issues. However, among the 35 forestry policy documents
reviewed, only the GESI strategy 2008, CF management guidelines 2008, and Buffer zone management
guidelines 1999 are highly gender responsive. The rest are either gender neutral or moderately gender
responsive. Among the 30 projects/programs being implemented in the forestry sector during the
2013/14 fiscal year, only 11 programs are directly gender responsive, 15 are indirectly responsive, and
the remaining four projects/programs are neutral.
The gender friendly policy documents reiterate provisions to ensure women's participation in the
field/community level. The increased trend/tendency towards internalization of GESI is found due to
increased awareness and sensitization of policy makers and civil society members. Nonetheless,
women’s participation in the planning and monitoring process is very low as there are no women in
decision-making positions. However, at the field level – particularly in the community forestry and
leasehold forestry programs – the inclusion of women and other marginalized groups is comparatively
high.
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In short, the progress in social inclusion has been uneven. The central problem is that while the
government is committed to GESI on paper, implementation has been patchy. Overall, the forestry
sector is still male-dominated, especially the government organizations. Community forestry is an
exceptional success in this regard, where GESI is incorporated in theory and practice.
II. International imperatives and commitments
Through the MDGs, the international community agreed on a common set of development targets,
including GESI. The country progress report states that despite the political instability, Nepal has
already attained MDG targets related to GESI.
III. Budget allocation
The GoN formally introduced gender responsive budget (GRB) to ensure equality for women during the
2007/08 fiscal year. GRB has since been institutionalized in all government mechanisms. The forestry
sector explicitly adopted this provision during the 2010/11 fiscal year. The total budget allocated to the
MFSC for the 2013/014 fiscal year is NPR 8.63 billion. Of this, approximately 3.55 percent and 66.19
percent fall under the direct and indirect gender responsive budget category respectively. The remaining
30.24 percent of the budget is gender neutral. Meanwhile, 21 percent of the overall government budget
is considered directly gender responsive for the current fiscal year. Looking at the government funded
forestry sector, almost all Red Book expenditures fall under the indirectly gender responsive category.
Analysis of some selected directly donor-supported activities reveals that direct funding is more propoor and pro-women in comparison to government funded programs.
5.7.2 Key Issues and Challenges
The following are key GESI related issues and challenges for the forestry sector.
I. Policy and legislation
Most forestry sector policy documents are gender neutral. But inadequate knowledge, low interest, and
weak institutional capacity on gender have led to poor advocacy for implementing provisions of the
existing gender responsive policy documents.
II. Institutional issues
The forestry sector is male dominated, with women grossly under-represented at the decisions-making,
management, and technical levels. Furthermore, GESI issues are given low priority within the formal
structure of the MFSC. Forestry professionals also do not have adequate knowledge and skills to ensure
gender mainstreaming.
III. Gaps in policies and implementation mechanisms
Most forest policy documents are either gender neutral or indirectly responsive. Poor coordination and
the lack of an accountability mechanism are also partially responsible for the patchy implementation of
GESI.
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IV. Gaps in awareness, knowledge, and capacity
There is no coherent strategy to communicate the importance of GESI to MFSC staff. Most of the inservice trainings are designed to plan and implement programs independently, rather than in integrated
ways.
V. Limited capabilities and opportunities to ensure benefits
The constraints faced by female employees within government organizations make it difficult for them
to participate in targeted programs and business enterprises at the scale necessary for commercialization.
The policies and mechanisms for harvesting natural resources, particularly non-timber forest products
(NTFP), are not conducive to the poor, women, and other excluded groups.
VI. Ad-hoc implementation of livelihood activities
Most micro-enterprises and income-generating activities are implemented as livelihood improvement
components of larger rural development programs. They bring minimal changes, in any, in the incomes
of targeted groups. Proper analysis and identification of products, markets, and capacities as well as
adequate investment in technology, infrastructure, and finances are also lacking.
VII. Right to natural resources
The right to and ownership of natural resources, particularly forests, in Nepal’s proposed federal
structure is an emerging issue. This will have implications on people and groups directly dependent on
natural resources, particularly indigenous peoples and socially excluded groups.
VIII. Weak service delivery
Most well-intentioned policies, plans, and programs have failed to reach and benefit women and
excluded groups, particularly in remote areas. This is largely due to the weak service delivery
mechanisms and poor implementation.
IX. Under-representation and inadequate participation
The under-representation and passive participation of women and socially excluded groups in economic,
political, and legal institutions has resulted in deficits in power and voice. This allows many inequalities
to remain unchallenged from the local to the national levels.
X. Lack of system for collecting desegregated data and weak monitoring
The forestry sector does not have a sound system for collecting desegregated data from the GESI
perspective. As a result, GESI considerations are not incorporated into monitoring, auditing, and
reporting systems in the forestry sector.
XI. Socio-cultural beliefs
There is a myth or misconception in Nepal that forestry is not a suitable profession for women. This
view exists within and outside the sector, and is a major challenge.
5.7.3 Lessons Learnt and Way Forward
Based on the experience of GESI, the following suggestions are proposed to improve gender balance
and social inclusion in the forestry sector. These suggestions are grouped in four categories.
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I. Institutional leadership and commitment

Operationalize existing policies (HRM/D and GESI strategy) and philosophical rationale of
GESI analysis in the sector.

Unlock the social inclusion aspects within the current systems, advocating for its review.

Develop a GESI implementation action plan for the short term, the medium term, and the long
term, including budgetary provisions.

Review and amend the Forest Act of 1993 as well as all other related regulations,
program/budget guidelines, and operational plans to ensure the inclusive and effective
participation of women and other socially excluded groups.

The position of GFPs should be strengthened across the board by assigning them well-defined
roles and facilitating proper coordination and linkages between their functions. They should be
strengthened with sufficient financial and human resources. A GESI unit should also be formed
under the HRM/D division. This unit should be a gender focal point with ToR.

Provide an enabling environment for the retention of female staff at all levels.
II. Capacity enhancements

Conduct a comprehensive capacity-development needs assessment, and carry out relevant
trainings on capacity building and knowledge management.

Mainstream GESI in long-range strategic planning across the subsectors and prepare a userfriendly participatory GESI manual to guide implementation.

Establish a forest resources information system with desegregated data, including participation of
different sex, gender, and socio-economic groups.

Develop strategic partnerships with stakeholders who have core competencies in GESI.

Properly implement the HRM/D strategy into practice to address the issue of low representation
of women in the MFSC structure and decision-making positions.

Encourage as well as attract female forestry experts towards the MFSC.
III. Organizational culture and assurance of accountability

Transform policies, contracts, and grants in harmony with gender-mainstreaming goals and
approaches.

Identify good practices and lessons learned from participatory methods and disseminate
desegregated information to staff and stakeholders at the community level.

Manage changes in institutional cultures and values to enhance appreciation of GESI.

Provide full power, authority, and resources to the implementing body of the MFSC to
mainstream GESI.
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
Develop participatory indicators for monitoring and evaluation of project processes, outputs,
outcomes, and impacts related to GESI.

Follow the GRB guideline of the MoF during planning, programming, and budgeting.
IV. Gender-responsive strategic plan

Develop and disseminate gender mainstreaming guidelines.

Equip staff at all levels with participatory approaches and gender analysis tools.

Produce a gender mainstreaming strategic plan.
5.8 Climate Change and Forestry
This paper reviews the MPFS from the perspective of climate change. Climate change was globally
recognized as a pressing issue in 1992 with the creation of the United Nation’s Framework Convention
on Climate Change (UNFCCC). As the MFPS was drafted before climate change became a global issue,
the plan does not have a dedicated climate change component. With all the compelling research that has
emerged on climate change since 1992, the issue should be closely integrated in future policies related to
the forestry sector. To this end, this section contains an in-depth discussion on the inter-linkages
between climate change and the forestry sector.
This review begins by highlighting global developments in climate change, including the international
and national conversations around REDD. With clear changes in precipitation and temperatures in
Nepal, the country is undertaking measures on climate change adaptation, especially NAPA and the
promotion of REDD. Since Nepal’s contribution to greenhouse gas emissions is negligible, but its
effects and impacts are significant, the forestry sector should seek additional resources from the global
climate community for adaptation and mitigation.
The climate-related challenges ahead are clear. The main immediate risks resulting from climate change
are flash floods, glacier lakes outbursts, and significant changes in downstream water flows over the
long run (CCNN 2007). Climate change will also affect human well-being, increasing disease risk, water
shortages, drought, and food insecurity. In addition, some case studies from Mustang, Manang, and Ilam
districts have further stressed the risks associated with climate change in Nepal. The key message is that
climate change is already a reality.
Climate change also has implications for the wider forestry system. This is especially true in Asia, which
is likely to suffer severe losses because of high temperatures, severe droughts, flood conditions, and soil
degradation. In boreal Asia, forest ecosystems will suffer from floods and increased volumes of runoff
associated with the melting of permafrost. The process of permafrost depletion resulting from global
warming reinforces the vulnerability of all relevant climate-dependent sectors, thereby affecting the
economy in high-latitude Asia. Countries in temperate and tropical Asia are more likely to have
increased exposure to extreme events, including forest die-back, increased fire risk, typhoons and
tropical storms, floods and landslide, and severe vector-borne diseases. The stresses of climate change
are likely to disrupt the ecology of mountain and highland systems in Asia (Gupta S. 2010).
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5.8.1 Key Achievements
The Ministry of Environment successfully drafted the Climate Change Policy 2011. In the section on
climate friendly natural resource management, the policy has mentioned a few points relating to forestry,
which include:

Proper utilization, promotion, and conservation of forest resources as a means of alternative
livelihoods.

Prioritizing and implementing programs on the sustainable management of forests, agro-forestry,
and soil conservation to address the impacts of climate change.

Encouraging carbon sequestration and investing some benefits from forest products for
controlling forest fire and conserving forests.

Adoption of basin approach for water management through regular monitoring of water
resources availability.
I. National Adaptation Program of Actions (NAPA)
NAPA is a set of programs around adaptation produced by developing countries to address the most
urgent problems brought about by climate change. Adaptation is defined as an adjustment of natural or
human systems in response to actual or expected climatic stimuli or their effects. The adjustments are
intended to moderate harm and exploit beneficial opportunities.
II. Clean Development Mechanism (CDM)
The first commitment period of the Clean Development Mechanism (CDM), one of the most innovative
features of the Kyoto Protocol, ended in 2012. Under the CDM, emission-reduction projects in
developing countries can earn certified emission reduction credits. These saleable credits can be used by
industrialized countries (Annex I countries) to meet a part of their emission reduction targets under the
Kyoto Protocol. The CDM was created in 1997 by Article 12 of the Kyoto Protocol. Parties to the
Protocol have since elaborated the full modalities and procedures for project activities. The CDM
Executive Board (EB) is the operational decision-making body, which is assisted by various expert
panels and working groups. As a part of CDM, Nepal generated some revenue through the promotion of
biogas plants.
III. REDD+ in Nepal
At the UN Poznan Climate Change Conference (CoP 14) in December 2008, the subsidiary body for
scientific and technical assistance (SBSTA) referred to ‘reducing emissions from deforestation and
forest degradation in developing countries, and the role of conservation, sustainable management of
forests and enhancement of forest carbon stocks in developing countries’ (Field, 2012). Since then, the
concept of REDD+ has become popular and widely accepted by the global community. The CoP 19,
held in Warsaw Poland, adopted an agreement on the "REDD Rulebook", which established guidelines
for determining national deforestation baselines. This was a key step for allowing compliance-based
REDD finance to flow. Among other donors, REDD+ is backed up by pledges of USD 280 million
financing from the US, Norway, and UK.
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A number of donors are supporting REDD+ in Nepal. The World Bank’s FCPF is supporting Nepal in
preparing a REDD strategy, and has committed to supporting a pilot implementation subsequently.
Similarly, the UNREDD program is also supporting the REDD program in Nepal. Bilateral forestry
projects funded by DFID, USAID, SDC and the government of Finland also have strong components of
REDD in field implementation.
REDD+ has been optimistically awaited due to its potential benefits, including:

Avoiding deforestation is one of the cheapest options to tackle climate change (Stern, 2006).

Unlike emissions from fossil fuels, REDD+ can offset the emissions in one place by reforestation
or enhancing carbon stock elsewhere (Skutsch and DeJong, 2010).

Apart from carbon benefits, REDD+ also contributes to generating or enhancing social (poverty
reduction, sustainable development) as well as ecological benefits (ecosystem services such as
conservation of water, soil, harboring biodiversity). These are commonly known as co-benefits
(Busch et al. 2011).

REDD+ can successfully bring together many actors at different levels, from the global to the
local; REDD+ has successfully generated global excitement with dozens of countries having
already prepared REDD+ programs.
5.8.2 Key Issues and Challenges of REDD+
When implemented, REDD+ is likely to face the following challenges in Nepal:

The possibility of elite capture for the benefit provided by the grassroots.

Uncertainty of carbon markets and its trading rate; the present market value of carbon is less than
USD 5 per ton.

Domination of international experts in deciding the amount and value of carbon.

The high costs of carrying out a need Measurement, Reporting and Verification (MRV) process
by an accredited international organization.

Complex methodologies which make it difficult to create a baseline scenario for
carbon monitoring in a way that satisfies both the carbon credit suppliers and buyers.

Ensuring the rights of local and indigenous peoples while selling secured carbon credits.

Enhancing the capacity of both government and civil society institutions to implement
REDD+, which requires strong technical and institutional capabilities (Ojha 2009).
5.8.3 Lessons Learnt and Way Forward
The preventive role of forests has become widely recognized in recent years. There is unanimity about
the role that forests can play in climate change both through carbon sequestration on one side and
reducing global carbon emissions on the other (Gupta 2010). It is for these reasons that the forestry
sector occupies centre stage during international climate change policy negotiations. This has been the
case since the 13th CoP was held in Bali in 2007. Bass et al. (2000) have cited three forest related
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approaches that have been used in various combinations within the strategy to reduce greenhouse gases
from the atmosphere:

Carbon conservation or halting/slowing down deforestation by preserving current carbon
reservoirs.

Carbon sequestration or increasing vegetation cover through forestation so that it can hold carbon
for a longer time.

Carbon substitution, or converting vegetation into timber products, which store carbon, or which
substitute bio-energy for fossil fuels so that less carbon is emitted into the atmosphere.
With the threat of climate change looming, it is important to manage forest resources more aggressively
than outlined in the earlier MPFS. Whatever the challenges in implanting REDD+, it is important to
envision it as an opportunity to get assistance from development partners to preserve Nepal’s forests and
adapt to climate change.
Beyond REDD, two other areas need to be explored in the days to come. One is the contribution of
forests and agroforestry in adaptation. The second is the knowledge that Nepal needs to generate
linkages and relationship between climate change and its impacts on forest ecosystems.
5.9 Financial Allocation in Forestry over Time
The MPFS had projected an expenditure of USD 1.742 billion (at constant 1988 prices) over the 25-year
implementation period. The MPFS identified three major sources of financing – private, government and
external assistance. We do not have information on the amount of private investment in forestry.
However, the plan had projected private sector investments to be 35.4 percent of the total projected
expenditure. The government was supposed to bear 34.4 percent of the cost, with external assistance
covering the remaining 30.2 percent. Excluding private investments, the projected allocation amounts to
USD 1.125 billion at constant 1988 prices.
Figure 5.1: Comparative study of estimated vs actual MPFS expenditure
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Assistance to the forestry sector is channelized through two windows – the regular government treasury
system and the off-treasury system. The former is known as indirect Red Book funding and the latter as
direct funding. Since the indirect funding has to be spent through the regular government accounting
process, it is audited by the auditor general’s office. It is thus reflected in the government’s accounting
reports. The direct funding is, however, spent through the projects and not shown in the government’s
accounting records. Thus, the external assistance figures recorded in the government budget are but a
fraction of the total foreign assistance. This graph only includes foreign assistance reported in annual
budgets and economic survey reports. The significant amount of foreign assistance spent through direct
funding, a figure that has only increased since the start of the conflict in 1996, are not included in this
analysis.
An analysis of the total expenditure incurred through the MFSC over the period of the MPFS reveals
that the allocation to forestry is declining over time. We transformed the current expenditure incurred in
each fiscal year into USD at 1988 constant prices so as to compare projected investment to actual
investment in each of the MPFS programs. The total expenditure of the ministry over the plan period is
about USD 390 million constant at 1988 prices. The share of foreign assistance is about 16 percent. The
actual expenditure is about 34.7 percent of the total projected expenditure without considering the inputs
from the private sector and direct external funding. In addition, the section also contextualizes
expenditures and revenues of the forestry sector in relation to total government budgets.
Figure 5.2: Share of revenue and expenses from MFSC to GoN
As the above diagram shows, the highest percent of government budget allocation to the forestry sector
was 3.75 percent in 1991/92, just after the formulation of the MPFS. Since then, the government share
of the budget allocated to forestry has declined, and was about 1.5 percent in 2010/11. The revenue
share of the forestry sector has also declined from 2.5 percent in 1992/93 to about 0.25 percent in
2010/11. The analysis shows that the actual fiscal outlay to the forestry sector has been low in
comparison to the projections of the MPFS. Moreover, the share of budgetary allocation to forestry has
also been declining over the years in relative terms. In another study, Kanel (2012) shows that only
about nine percent of the total budget allocated to forestry has been used for forestry investment; the
remaining share has been used as current or regular expenditure. The total budgetary expenditure on
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different forestry programs show that the highest share of the budget for forestry over the years was
allocated to the Conservation of Ecosystem and Genetic Resources program.
Table 6.0: Budgetary allocation in different programs of MPFS
MPFS Programs
Community and Private Forestry
Program
National and Leasehold forestry
Wood-based Industry
Medicinal and Aromatic plants
Soil Conservation and Watershed
Management
Conservation of Ecosystem and Genetic
Resources
Policy, Legal, and Institutional Reform
Human Resource
Research and Extension Program
Planning and Resource Information
Monitoring and Evaluation
Total
Real Expenditure of MFSC during 1888/89 to
2010/11
NPR
USD
USD
% of total
current
constant
8,108.71
7,320.57
Negligible
392.29
129.66
116.67
Negligible
6.28
91.98
81.85
Negligible
4.41
23.05
20.81
Negligible
1.12
4,507.60
71.53
50.18
12.82
13,230.7
81.62
256.52
808.70
184.21
281.96
35,172.89
207.83
1.28
3.70
12.80
2.86
4.38
556.98
144.37
0.88
2.40
8.82
1.95
2.99
389.84
37.62
0.23
0.73
2.30
0.52
0.80
100.00
5.9.2 Key Issues and Challenges
The above analysis shows that financial allocation to the forestry sector has lagged below its potential.
Although, it is estimated that forestry contributes to about 8/9 percent of the total GDP of Nepal, the
percentage share of government allocation to forestry has decreased over time. In part, this is because
forestry is a low priority for the government. Another problem is the lack of a formal mechanism to
calculate the amount of foreign assistance to forestry channelized through direct funding; the
government assumes that donors are directly funding the sector, and thus reduces its contributions.
Transparency in the allocation of funding to the forestry sector is, therefore, an issue requiring attention.
Similarly, there is no adequate means to estimate private funding and the opportunity cost of
communities contributing their labor for the restoration, management and utilization of forest resources.
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5.9.3 Lessons Learnt and Way Forward
The lessons that we can draw from the existing issues in the scale and allocation of funding for different
forestry programs can be listed below:

The financial outlay in the forestry sector is too low. It should be increased substantially to really
contribute to the prosperity of Nepal.

Budgetary allocation should match the priority of the programs.

Most of the funding from donors is channelized through direct funding and it is not transparent.
It is necessary to make direct funding more transparent and recordable in the government system.

The contribution of communities and private households in the promotion of community and
private forests should be periodically assessed through macro-level studies. If their contribution
is in terms of labor deployed to restore the forests or plant and manage trees, that should be
accounted as opportunity cost in the periodic assessment.

The investment by the private sector in forest-based enterprises and marketing should be
assessed through periodic studies.

The benefits of forestry in terms of household and commercial activities have not been estimated
so far. Such studies including the contribution of forestry to the national income could assist in
highlighting the importance of forestry in the national economy of Nepal, and persuading the
government to allocate more funding to the forestry sector.
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Chapter 6: Other Factors and Actors Driving MPFS Performance
Factors beyond the MPFS also contributed to the performance of the forestry sector within the master
plan period. National political, economic, and demographic changes played significant roles.
International factors such as the Rio conferences of 1992 and 2002; globalization and liberalization all
over the world; and international conventions on forestry, biodiversity, and climate change also have
repercussions on how forestry is conceived and practiced in Nepal. Further, the pressure on forests
leading to deforestation and forest degradation has compelled the forest agencies of developing
countries to rethink forestry from new perspectives. These international experiences have also
stimulated Nepal to reinvent and redesign its forestry program over time.
6.1 Political Changes
The MPFS was designed during a time of absolute monarchy, when political parties were banned. The
central government policy was to meet the basic needs of the people. In fact, the MPFS was also
formulated for this purpose. However, the programmatic thrust was to enlist local communities in the
conservation, management, and utilization of the local forest resources. Thus, the plan suggested
people’s participation in the management of the forests located mainly in the mid-hills and mountains of
the country. The Tarai forest was supposed to be managed by the government or by private entities on
long-term lease.
Once the absolute power residing in the king was removed and a multi-party constitutional monarchy
was restored in 1990, people’s power loomed large. Party representatives in the newly created
parliament were enthusiastic to devolve more power to the local communities. This devolution of power
was formalized through the Forest Act 1993 and the Forest Rules 1995, giving significant rights to local
community forest users groups (CFUGs). CFUGs were also recognized as independent, autonomous,
and self-governing bodies responsible not only for the management of the local forests but also for
undertaking other beneficial activities of their choosing. This new paradigm of forest management could
not have been so encompassing without the political change in 1990. Subsequently, the Forest Rules of
1995 was amended to make room for group-based pro-poor leasehold forestry. In a similar vein, the
concept of buffer zones and conservation areas managed by local people were incorporated into the
existing Wildlife and National Park Act. The post-1990 regime also liberalized the criteria to run a civil
society organization; more than 40,000 NGOs are registered in Nepal today. Some of these NGOs are
actively engaged in promoting community-based forestry.
The armed insurgency (1996 to 2006) hampered the functioning of government agencies in rural Nepal.
However, CFUGs were the only grassroots organizations that could function without much disturbance,
further reinforcing their legitimacy. The new political order ushered in by the end of the conflict in 2007
enshrined the provisions of social inclusion and proportional representation in every organ of
governance. The exclusion of distant forest users in the Tarai has emboldened them to demand their
rights, leading to the practice of Collaborative Forest Management.
These political changes have gradually empowered communities to manage the common pool resources
such as forests, water, land and watersheds through collective institutional arrangements.
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6.2 Economic Changes
The structure of the economy and population density has significantly changed since the MPFS was
formulated. During the time of MPFS preparation, about 60 percent of the total GDP came from the
agriculture sector which included forestry and fisheries. Now, the share of the agriculture sector
(including forestry) in total GDP is only about 33 percent. Similarly, only a few youths worked overseas
during the 1990s. Now, about 5/6 million youths are working overseas, bringing in about NPR 434
billion or about one fourth of the total GDP in the fiscal year 2012/13. Remittance has been instrumental
in reducing poverty and meeting the trade deficit.
Figure 6.1: Contribution of industry, service, and agriculture to national economy
Change in Economic Structure
60
Contribution percent
50
40
30
20
10
0
1990/91
1995/96
2001/02
Fiscal Years
2005/06
2010/11
Industry Sector
Service Sector
Agriculture Sector
Although economic growth was hovering around three percent over the plan period, the remittance
economy has significantly helped in reducing the level of poverty. For example, population living below
the national poverty line decreased from 42 percent in 1996 to 30.8 percent in 2003 and dropped to 25.4
percent in 2009 (CBS, 2009).
Table 6.1: Average per capita income of households in NPR
Particulars
1995/96
Nominal average household income in NPR
43,732
Nominal average per capita income in NPR
All Nepal
7,690
Poorest 20% of population
2,020
Richest 20% of population
19,325
Source: CBS,1996; CBS,2004; CBS, 2011.
2003/04
80,111
2010/11
202,374
15,162
4,003
40,486
41,659
15,888
94,149
The increased income of the households is due mainly to the remittance economy. The increased income
along with growing urbanization has led to households switching from fuelwood to other clean energy
sources such as LPG. This is even true in some rural parts of Nepal.
Significant social changes have also occurred in Nepal. The level of literacy has significantly increased
from 30 percent in 1991 to 66 percent in 2011. Similarly, road access has also improved over time. The
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total length of road was estimated to be about 6,000 km in 1985 compared to about 10,900 km today.
The increased expansion of road has improved accessibility to forests, and thus bolstered their value,
while depleting the forests during construction. Significant achievements have also been made in other
human development index areas. These improvements in social development indicators as well as the
scarcity of youth due to temporary migration, has also increased the scarcity of labor. This has led to
reduced dependency on forests for fuelwood, fodder, and leaf litter collection. The overall balance has
been negative mainly in the Tarai and Chure regions in comparison to the mid-hills and mountains.
6.3 Demographic Changes
The population of Nepal has increased from 18.5 million in 1991 to 26.5 million in 2011. Since more
than 80 percent of households still use fuelwood as a source of energy, and wood is a central material in
constructing homes, the increase in population has a direct impact on forests. However, the total demand
for wood (both fuelwood and timber combined) has not increased in proportion to the growth of the
population. This is due to increased household income, labor migration and increased labor scarcity, and
demographic shift among the ecological zones.
The population growth rate has declined from 2.6 percent in 1991 to 1.6 percent in 2011. The urban
population of Nepal was a mere five percent in 1991. As per the 2011 census, the urban population of
Nepal is about 17 percent. Similarly, people have migrated from the mid-hills and mountains to the
plains. In 1991, about 40 percent of the population lived in the Tarai. It has now increased to more than
half. In 26 mid-hill and mountain districts, the total population has decreased over the last ten years.
These demographic shifts coupled with labor shortages and cash flow have led to the expansion of forest
areas in the marginal agriculture land of the mid-hills and mountains. The pressure on forests for
consumptive use has significantly declined, and thus helped in the increase of biomass in both
community, private, and even government forests (Niraula et al, 2013).
6.4 International Experiences
The MPFS process was greatly influenced by the Tropical Forest Action Plan (TFAP), a global tool to
stem increasing deforestation and forest degradation in developing countries. Similarly, international
agreements, conventions, practices, and experiences in other parts of the world have also assisted in the
implementation of MPFS in Nepal. The Rio Conference of 1992 was instrumental in bringing about the
Convention on Biodiversity (CBD), United Nations Framework Convention on Climate Change
(UNFCCC), and the United Nations Convention to Combat Desertification (UNCCD). The conference
adopted non-binding principles on forest management which have yet to be ratified by the international
community.
These conventions and frameworks have stressed the global significance of forestry in conserving
environment. Forests are acknowledged for providing invaluable ecosystem services for the prosperity
of present and future generations. The United Nations Forum on Forestry (UNFF) is presently working
on devising globally binding forest principles that would be applicable for all types of forests of the
world. Similarly, other relevant international organizations such as FAO, CIFOR, WWF, IUCN, ITTO
and the World Bank convene meetings and produce reports based on experiences, trends, and lessons
from various developing countries. These studies have shown that the involvement and engagement of
forest-dependent people has increased significantly over the past years. Indeed, the sustainable forestry
116
principles developed by FAO, ITTO, and CIFOR include significant roles for indigenous and local
communities in decision-making and forest management. Similarly, the REDD+ has also considered the
role of communities and indigenous groups in the architecture of forest governance.
Studies carried out by the Rights and Resources Initiative (RRI) have shown that forest tenure and
governance reform have increasingly become the dominant theme in forest management in developing
countries. Across the world, forest areas administered by governments have declined from 79 to 73
percent over the last 10 years. In the same timeframe, forest areas managed by local or indigenous
communities have increased from 9 to 12 percent. Looking at Asia, the percent of forests under
community and indigenous group-based management has increased from 32 to 38 percent. Legal and
polycentric governance reforms in forestry have increasingly expanded and strengthened the rights of
local and indigenous communities in developing countries. These global experiences have also helped in
transforming the paradigm of forest management in Nepal.
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Chapter 7: Conclusions
This conclusion chapter reviews the lessons learnt from 25 years of MPFS implementation and
explores possibilities for a new forestry strategy. The lessons are grouped in the following five
categories:
7.1 Lessons Learnt
7.1.1 Management and utilization of forest resources and conserving biodiversity

Participatory approaches have proved to be highly effective in ensuring local commitment,
local benefits, and local awareness of plans and processes. They have been applied to
community forestry, leasehold forestry, collaborative forest management, buffer zones,
watershed management, and other forest and land management modalities. The
participatory approach has also been adopted for national and local planning, including for
MFSC annual bottom-up planning, DFSPs and VDC level forest sector planning, LAPAs,
and even for national processes such as REDD+ and NAPA.

There is improved growing stock in many forests (particularly community forests) that
have been effectively protected and managed over the past 25 years. However, they are not
being used for value addition, employment generation, and income growth.

A critical factor for the success of CF is that CFUGs and other forest user groups can
operate as autonomous, independent, and self-governing entities. The legislation that
provides this mechanism needs to be ensured in the future.

Improved coordination between the primary programs of MPFS is needed. This would lead
to better achievement across all programs. For example, community and private forestry
can supply raw materials for wood and non-wood based industries and they can also
contribute to the conservation of ecosystems and watersheds.

A large part of the government-managed forest estate lacks effective forest management
and stakeholder participation. This leads to unmanaged forests that are effectively openaccess. Coupled with past political instability and the lack of rule of law, large parts of the
national forest are being converted to other land uses or are subject to illicit timber
harvesting and forest degradation in the Tarai and Chure areas.

DSCWM cannot fulfil the entire demand for soil conservation and watershed management
services. It is necessary to leverage services from other agencies also concerned with
watershed management and ensure that the sectoral strategies of forestry, agriculture,
irrigation, roads, local development, environment, and hydropower, among others, include
soil and water conservation components. The DSCWM needs to re-invent itself from
implementer to facilitator with a critical role in planning, research and technology
development, development of appropriate techniques, technical backstopping, facilitating,
and policy influence. A clear institutional, legal, and policy arrangement is required for the
management of critical watershed areas (including the Chure) that does not place sole
responsibility on the DSCWM.
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
Poaching and illegal trade in forest products continues to be a critical issue. These have
been exacerbated by civil unrest and poor rule of law during and after the conflict despite
the resources set against them (such as the Nepal Army and forest guards). The solution
appears to lie elsewhere – through effective management of resources, reducing poverty,
and enhancing good governance.

Successes in biodiversity conservation can have adverse impacts. The concentration of
visitors to certain spots in PAs and the need to develop associated visitor facilities is
necessary to avoid environmental damage. Improved numbers of certain species e.g.
elephants and tigers has the downside effect of increasing the level of human-wildlife
conflict. For this, compensation processes for loss of life or property need to become
meaningful and more responsive.

Forest resource information systems and planning need to be improved. Current levels of
forest resource information (and data management systems) are insufficient for effective
and transparent planning in the forest sector. Forest related data and information should be
disaggregated based on district and physiographic regions e.g. Tarai, Siwalik, mid-hills and
high mountains. The data could also be based on forest management regimes. MFSC has
too few qualified staff responsible for updating and analysing such MIS systems.
Outsourcing for data generation, analysis and synthesis to private agencies within the
country can mitigate this shortfall.

There is a need to balance natural resource conservation with the needs of development.
Roads, hydro-schemes, power-lines, and urban expansion are all necessary for Nepal’s
development. But they also adversely affect forests and protected areas resulting in habitat
fragmentation, higher levels of illicit use, and pressure for over-use of resources and land.
Conservation cannot be tackled in an isolated way through a process of exclusion. Instead,
conservation is only possible by involving and informing decision-makers, planners, and
civil society in decisions.
7.1.2 Policy and legal framework

The policy framework must be backed up by supportive legislation. Nepal’s 1989 Forest
Policy, strengthened by the powerful legal provisions of the 1993 Forest Act was
fundamental to the successes of the Community Forestry Program and to a large extent
with that of the Conservation of Ecosystems and Genetic Resources Program. Where
supportive legislation was not put in place (in the case of the National and Leasehold
Forestry Program) or where policy and legal provisions were not fully implemented (as in
the case of the Wood-Based Industries Program) programs have failed to deliver.

Policy process is critical. To be effectively implemented, policies need the consensus of
those who are affected by them or of those who will be responsible for their
implementation. A deliberative and open policy development process will ensure that this
happens.

Other sector policies and laws affect the forest sector. A better understanding of the
linkages between different sectors and a coherent and overarching approach to policy
development can contribute to achievement of policy goals. Recently Nepal’s NAPA and
REDD+ processes are starting to recognise this necessity. This approach needs to be
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continued beyond policy-making to policy implementation and to the development of a
supportive and unambiguous legal framework.

Various government orders, directives and regulations are inconsistent with forest policy
and laws. This has particularly affected the wood-based industry, community forestry, and
the national and leasehold forestry programs. In these areas, government restrictions on
collection, transportation, and marketing of forest products and price controls have been
frequently issued. The following steps may be useful for limiting regulatory proliferation
and inconsistencies, and enhancing the operational environment:
a.
b.
c.
Ensure that a coherent and sound forest policy is in place prior to law-making. Reduce
the number of rules by identifying overlaps and inconsistencies. In short, do not simply
create more rules.
Adapt the remaining rules to ensure consistency with other existing laws, including
those within and amongst different sectors.
Translate new legislative acts into working norms and regulations as soon as possible
after new laws have been approved. This is essential to ensuring correct
implementation and to avoiding uncertainty.

Implications of the Local Self Governance Act of 1999 need to be considered. There is a
critical need to engage with local government at all levels (local, district and national) to
enhance accountability and to follow the spirit of decentralized legislation. Inconsistencies
between the LSGA and the Forest Act of 1993 need to be clarified.

The application of Environmental Regulations for the forest sector needs to be reviewed
since IEE/EIAs are legally binding for a range of forest management operations. It is also
necessary to reconsider whether these regulations intended for environmental protection
are really necessary if applied to a sustainable forest management situation.
7.1.3 Forest sector institutions


A constraint for most programs is a lack of speciality staff. Despite the wide-ranging
training and educational opportunities that have been provided there is an ongoing need to
continue to develop new knowledge amongst forestry professionals. More specifically:
a. Forestry staffs need to be trained in technical, managerial, and communication aspects
of forestry. As forest management is gradually decentralized to entities outside the
government, the staff should be more skilful in regulation, monitoring, and facilitation.
b. Many skill areas in forestry are also available outside government institutions and
there have been successful experiences of utilising these through contractual, service
providers, or other arrangements. This approach can be extended to cover other areas of
activity.
The strongly protection-orientation as well as command and control attitude of MFSC
administration has not shifted significantly over the period of the MPFS. These attitudes
are inconsistent with people-centric policies and with the increased capacities of
individuals, civil society, and communities. These attitudes are also in conflict with the
needs of a modern democratic society. Policy shifts need to be matched by institutional
reforms in the changing context, and changes in attitude amongst individuals.
120


Government forestry institutions are characterised by weak management and out-of-date
HR systems. While many individuals within MFSC are skilled and highly competent, they
work within an institutional structure following HR management systems designed for old
problems and are inconsistent with present-day needs. Key issues are:
a. Lack of overall HR policy or set of operational guidelines covering the critical
procedures for recruitment, appointment, terms and conditions, performance appraisal,
career path development, codes of conduct, counselling, training, promotion and
grievance handling.
b. Lack of a comprehensive and readily available HR database.
c. Particularly weak recruitment, placement and transfer systems resulting in decisions
that are unpredictable, untimely, and subject to ad hoc influence. Promotion systems
that do not encourage innovation, productivity, or demonstrated performance.
d. Training and staff development that are not based on individually assessed needs.
Weak linkage between training and job performance.
e. Poor representation of women and other disadvantaged groups at all government levels
(although this is true for all government organisations not solely MFSC).
f. Loss of quality staff to international organisations and projects (implying that
incentives to stay within the government system are insufficient).
Forest sector institutions are becoming increasingly diverse. It was assumed that most
aspects of implementation of MPFS would be via government institutions. There are now
many organisations and individuals outside government with capacities and skills to fulfil a
wide range of roles and services that were formally exclusively carried out by government.
The challenge is to capitalise on these and maintain a balance between the capacities and
varying roles of different types of organizations working in the forest sector. Clear roles
and opportunities need to be created for all types of forest-sector institutions including civil
society, academia, community-based organisations, the private sector, and government
itself.

MFSC staff is overburdened with administrative tasks. The focus for most field-level forest
sector activity lies at the DFO. DFOs have largely become administrators rather than sector
specialists. They are expected to undertake a very broad range of administrative tasks,
often beyond their management capability. This is not sustainable and some functions of
DFOs need to be altered or assigned to other parties (as has happened in other technical
ministries of Nepal such as roads and telecommunication) to address this issue.

The sector lacks sufficient political engagement and support. Despite the internationally
recognised achievements of community-based forest management in Nepal, political
leaders rarely acknowledge the sector. Forest legislation does not give enough space for
local level government leaders and political parties in the decision-making process. New
institutional mechanism taking into account the concept of federalism and power-sharing in
natural resource management need to be developed while formulating a new forest sector
strategy.
7.1.4 Forest sector’s contribution to economic development

Over-regulation is a constraint. Whilst the Forest Act (1993) and its associated rules
diversify the management regimes for national forests, they also over-burden forest
121
managers with excessive regulation on the harvest, transport, process and sale of forest
products. Similarly over-regulation of the harvest and utilization of forest products from
private forests reduces the incentive for private forest or tree owners to produce and grow
more of these products.

Fiscal policy is a constraint. MPFS proposed that royalty rates for forest products be
adjusted to make them compatible with production costs. Revisions of royalties have taken
place on a rather ad-hoc basis. Wood traders and consumers feel that the present royalty
rates for wood are set too high and comparison of Nepal’s royalty rates with those of other
countries seems to confirm this. For instance, 13 percent VAT is imposed on timber sales
and some NTFPs produced from private land. Meanwhile, there is no VAT on the
production and sales of agricultural commodities, thus stifling private landowner
involvement in the commercialisation of forest products.

Sufficient supplies of raw materials are not being generated from government-managed
forests. Whilst MPFS sought to utilize government-managed national forests to promote
the forest industry, the lack of proper management planning and harvesting control has
stifled the supply of wood from this management regime. Comparatively small quantities
of forest products are legitimately supplied to industry from government-managed forest
and overall supplies of forest products are far less than could be potentially produced. Not
only does this reduce government revenue, it also limits the expansion of the wood-using
industry and the commercialisation of the forest sector with associated benefits such as
cash incomes and jobs.

TCN has a distorting impact. Although the role and functions of FPDB have been
drastically reduced, the government still gives preferential treatment to TCN for the supply
of timber (logs) at reduced rates. Despite this, TCN is unable to operate on a commercial
basis. Consequently, it distorts markets and creating a dis-incentive for private sector
investment.

Coordinating mechanisms for the wood-using industry are lacking. The wood-using sector
is becoming increasingly diverse as governmental/semi-government agencies, private
industries, as well as forest user groups and their cooperatives are now operating woodbased industries. These actors are also operating other forest product-based industries,
supplying timber and NTFPs into the market. The private sector, although recognised as
being critical to the achievement of economic goals in through forestry, is rarely engaged
in a meaningful and productive way. A representative body with expertise and knowledge
of the commercial aspects of the forest sector is lacking at present.

There is a need for a stable regulatory environment to attract investment. The more than
5,000 wood-based industries registered and operating in Nepal, face the following
problems: impractical environmental standards, dual taxation, inconsistency in the auction
system, lack of private sector participation in the policy-making process, and lack of
transparency in decision-making processes. These problems result in erratic regulations,
creates uncertainty and challenges to the growth of wood-based industries. A considerable
amount of unregulated trade in and utilisation of forest products exists. This is partly a
consequence of the excessive regulatory restrictions placed on the wood-using sector.
122


Sources of finance for small-scale forest-based industries are inadequate. Taxation, loan
regulations and land-related laws are also not favourable for the establishment of smallscale private and community-based enterprises. The smaller players in the sector need bank
loans and tax breaks to enable them to become established. Compared with this, larger
scale industries have easier access to finance, taxation opportunities, and banking facilities.
The potential of commercial leasehold forestry has not been tapped. The MPFS aimed to
stimulate private sector investment in forestry through commercial leases on forest land.
But the approach failed as the Forest Regulations (1995) only focused on degraded forests
and not on natural forest areas. Even where provisions do exist for leasing degraded forests
to private players for re-afforestation or ecotourism, factors such as high annual rental fee
act as disincentive to uptake.
7.1.5 Addressing poverty and social exclusion

The sector provides good opportunities for addressing poverty and social exclusion.
Nepal’s national development policies focus on poverty reduction as an overarching goal.
A high percentage of people in Nepal still live in poverty and still depend on forests for
their livelihoods. Experience has shown that there are good opportunities for the forest
sector to contribute to their livelihoods. Such opportunities can be enhanced through
prioritising and expanding those programs that have the greatest impact such as
community-based forestry (of all kinds), job creation (through wood-based industry), and
climate resilience.

There is an imbalance in roles, responsibilities and powers. Across the board, there is
acknowledgement that participatory processes are needed in all parts of the sector. And
forest sector stakeholders do work collaboratively. There still, however, exists a disparity
in roles, responsibilities, and power between government and other actors. Key sector
stakeholders such as women, poor people, and disadvantaged groups (Dalit, and other
marginalized indigenous communities) have little genuine power and voice. Though these
groups are usually represented in various decision-making forums, there is still a tendency
towards unilateral decision-making. There is a marked lack of transparency on the part of
government and more powerful civil society actors.

Governance is the key to addressing issues around poverty and social exclusion. Early
experiences with community forestry showed that elites would continue to predominate
and exclusion of others would continue. This critical issue was partially addressed by
focusing on enhancement of group governance – changes in the way such groups make
decisions that affect all their members. As a result of this approach, local forestry groups
are now becoming more inclusive and pro-poor in the country. The MFSC GESI strategy
attempts to do this amongst MFSC institutions. However, many elements have not yet been
implemented.

Supportive regulations based on field-based learning can contribute to poverty reduction
and social inclusion. It is, of course, not normally possible to legislate against entrenched
attitudes and behaviours. There are, however, examples – the impact of CF Guidelines on
benefit sharing and representation in CFUGs being one – that regulations based on field
experiences and good practices can have a positive impact.
123
7.1.5 Nepal’s climate change agenda

The forest sector is critical to Nepal’s climate change agenda. The progress of developing
Nepal’s response to climate change has enhanced public awareness on the important role
that forests play. This is strongly conveyed in Nepal’s NAPA as well as in the strategic
processes being followed for REDD+.

Strategic climate change processes need to be integral to Nepal’s forestry sector strategy.
Considerable progress has already been made in developing strategic processes as well as
local planning processes to tackle climate change related problems. Strategies for climate
change relevant to the forest sector (whether for climate change adaptation or for
mitigating climate change) must be integral to any future forestry sector strategy. Climate
change is a cross cutting issue and must therefore be considered across all programs.

REDD+ is fully compatible with forestry sector goals. REDD+ aims for a healthy and
vibrant forestry sector. Expansion of forest, carbon, soil, and watershed conservation
measures using systems for Payment for Ecological Services (PES) to leverage funds is a
potentially viable approach for Nepal. But significant action-oriented piloting and testing
will be required to implement it successfully.

Local forest groups provide a strong institutional base for community-based adaptation,
planning, and implementation. Community forest groups of various kinds can be effective
in implementing actions to enhance the climate resilience of the most vulnerable
households.

Climate change is already affecting Nepal’s forests. These effects include invasive species,
forest fires, effects on forest regeneration and growth, soil and water conservation, floods
and water source depletion. Although quantitative data is mostly lacking there is sufficient
local experience to demonstrate these effects at present.
7.2 Way Forward
This section synthesizes recommendations for the future direction of Nepal’s forestry sector based
on suggestions from various stakeholders, the review of past experiences, and the lessons learned.
Future directions are determined by the need to address current and future issues/gaps as well as
by the need to capitalize on learning that has taken place. Plans for the future are also affected by
Nepal’s national and international development commitments.
Below, the review team has grouped considerations for the future into key themes representing the
main areas Nepal’s National Forestry Strategy will need to heed:






Forest sector governance and administration
Management of forest resources
Forest sector contribution to economic development
Forest sector contribution to social inclusion and poverty reduction
Forest biodiversity and environmental conservation
Forest sector response to climate change
124
7.2.1 The nature of Nepal’s forestry sector strategy (FSS)
Nepal’s new FSS will differ from the MPFS in its content and structure. FSS will not be an allencompassing plan but will be a much shorter document. Its key purpose will be to set out a
strategic vision and goals for the forestry sector. It will also identify approaches and priorities for
achieving the visions, also tasking the different actors with key responsibilities. Some broad
guidelines for the FSS include:

It should be ‘owned’ across the sector. This will be necessary for it to be implemented by
all relevant stakeholders including those in other sectors affected by or affecting the forest
sector.

The mode of implementation needs to address the many cross-cutting issues such as
governance, gender and social inclusion, and climate change.

The FSS must name the forestry sector stakeholders to be involved in monitoring and
assessing the strategy, and making any necessary future changes in direction.

A multi-stakeholder entity needs to be established to finance the future forestry programs
in an intensive way. An institutional structure needs to be devised to best use the bilateral
development funds to support implementation of the new FSS. Similarly, the future role of
the Forestry Sector Coordination Committee needs to be clarified.

Disadvantaged groups need to be provided with an effective voice in various levels of
coordination committees and in sector governance more generally.

Criteria and indicators need to be developed as part of FSS to enable regular monitoring
and changes of direction if needed.

The FSS needs to be harmonized with other strategies, including in the following sectors:
REDD+, biodiversity, conservation, agriculture development, low carbon, biomass energy,
and NAPA.

The proposed themes and programs needs to be linked within FSS and become mutually
supportive.

The FSS must be made compatible with the upcoming constitutional provisions such as
new state structures.
7.2.2 Forestry sector governance and administration
Suggested future directions include:

Reorganise MFSC institutions to:
a. Better utilise the capacity and potential of non-government actors in the forest sector by
promoting private-public-community partnerships.
b. Reduce the administrative burden on government forestry sector staff.
c. Enhance technical skills and management capabilities.
125
d. Minimise bureaucracy.
e. Bring better communication and management skills to enhance the image and
performance of the forestry sector.

Revisit and implement the MFSC HRD strategy to put in place HR systems appropriate to
the needs of a modern government organisation.

Improve the gender and social balance within MFSC institutions in accordance with GESI
and institutionalise GESI within the new FSS.

Align MFSC institutions with local government (at different levels) thus reducing
centralised control and improving linkages with accountable bodies. Formalise district
forest coordination structures and plans.

Draft new legislation to increase clarity, transparency, and consistency of legislation
ensuring that it is unambiguous, based on tested approaches, and allows for minimal
discretionary powers. Also ensure the role of the private sector in the management of
forests and the development of forest enterprises.

Revisit the regulatory framework – especially government orders, circulars, and directives –
with the aim of deregulating these and removing inconsistencies.

Investigate social, economic and political causes of non-compliance (with policies and
laws) and adopt strategies to address these causes.

Develop partnerships between academic institutions and MFSC to ensure the provision of
sufficient numbers of professionally qualified staff to meet the future needs of the forest
sector.

Carry out a detailed study to determine which of Nepal’s commitments under international
law are not yet implemented and identify ways in which compliance with these can be
improved.

Build on international best practice by pursuing a programme for forest law enforcement
(and trade) in Nepal’s forest sector.

The role and function of the MFSC departments and divisions must be clarified. There is
currently confusion as to whether departments should primarily implement the FSS or
whether they should create and support an enabling environment for others to carry out
implementation.

The DSCWM need to evolve into an enabling agency to provide technical support for soil
and watershed conservation actions implemented by other departments, local government,
and communities.

The future role and function of DFRS and parastatals need to be clarified. The question of
whether the DFRS can function as a semi-autonomous entity is an important one. The
parastatals, especially TCN, HPPCL, and FPDB, must be made competitive and productive
through privatization.
126
7.2.3 Management of forest resources
Suggested future directions include:

Develop a forest land-use strategy for Nepal to identify the most appropriate management
modality for each patch of forest. This strategy can exist at the district level. But it is
necessary to recognise the need for this land-use strategy to be agreed to by all sectors and
not just the MFSC. This is especially true for the Tarai, Chure, and high mountains where
allocation under different modalities is still contested.

Bring all forest areas under the remit of a management plan. Promote active sustainable
harvesting and management of forests in good condition to generate forest products for
forest-based industries, both small and larger scale.

Merge the pro-poor leasehold forestry with the community forestry program for
administrative purposes. Nonetheless, the strategy must recognize the unique evolution and
potential for both these models

Strengthen the regulatory environment to enable patches of national forest not demanded
by communities to be leased to private entrepreneurs, or managed under a PPP model for
commercial sustainable utilisation.

Develop a cross-sectoral watershed conservation policy as part of FSS to integrate soil and
watershed conservation actions into the strategies and plans of other sectors. Climate
change adaptation funds can be used for the implementation of the cross-cutting strategy.

Identify appropriate forest management modalities for forests in the high mountains and
Chure. A similar approach is needed for forests that are not community based or included
in protected areas.
7.2.4 Forest sector contribution to economic development
Suggested future directions include:

Place more emphasis on commercialisation of forest products. Develop strategies to
support and foster forest-based enterprises, especially small-scale enterprises in rural areas.
Focus on strategies to create sustainable jobs, cash incomes, and legitimate forest-based
enterprise that will benefit poor people and disadvantaged groups.

Work closely with the private sector to identify viable investment opportunities and
sources of finance. Work with the private sector to provide a stimulating and supportive
enabling environment for investment and growth in the forest sector.

Take advantage of the high demand for forest product-based commodities to follow a more
strongly commercial direction for the forest sector. At the same time, the FSS must
recognise that many poor households are dependent on subsistence forest products for their
livelihoods. Maintain a balance between local needs, commercial interest, and economic
growth.
127

Deregulate harvesting and transport of forest products and enterprise establishment rules to
create a more supportive environment to enable private tree and forest owners and CFUGS
to generate ‘green jobs’.

Promote Nepal’s forest products internationally and remove barriers to the export of niche
and high value products (but low volume) to international markets.

Promote the commercial cultivation of medicinal and aromatic plants on private lands
through extension and demonstration. This will reduce pressure on wild resources.

Develop and manage information and monitoring systems for Nepal’s forest-based industry
sector.

Forest products coming from private land or cultivated NTFPs/MAPs products must be
exempt from paying VAT.

Permit regimes for private forests and trees need to be simplified to stimulate greater levels
of planting and management of forest and trees in private land.
7.2.5 Forestry sector contribution to social inclusion and poverty reduction
Suggested future directions include:

Continue to support local forest groups in governance. Targeted actions are required to
address the needs of the groups’ poor and socially disadvantaged members. Enable the
local forest groups to develop opportunities for jobs and cash incomes in rural areas.

Strengthen necessary legal provisions by revising the Forest Act to ensure that the legal
autonomy of local forest groups is strengthened and ensured.

Ensure intellectual property rights, patent rights, genetic resources, and other relevant
knowledge is used to benefit poor people.
7.2.6 Forest biodiversity and environmental conservation
Suggested future directions include:

Develop a scientific basis with participatory and open process for the establishment of new
PAs and botanical gardens. While creating new protected areas, take into account local,
national, and international needs of biodiversity conservation.

Explore opportunities for biodiversity conservation outside formally protected areas
through land-use management incentives and regulation.

Develop a more fair and transparent compensation system for dealing with the aftermath of
human-wildlife conflict.

Work closely with the private sector to continue to promote Nepal’s PAs as tourist
destinations while at the same time spreading the pressure of visitors and infrastructure
more widely and away from critical habitat areas. Rejuvenate critical habitats to reduce the
pressure.
128

Develop a workable mechanism for investing a part of hydro-power royalty for the
conservation of concerned watersheds.
7.2.7 Forestry sector response to climate change
Suggested future directions include:

Harmonize Nepal’s REDD+ strategy fully into the framework of the new FSS. Ensure that
REDD+ does not become separate from other forest sector strategies focusing on poverty
alleviation, economic growth, or biodiversity conservation.

Promote the use of local forest groups as implementers of LAPA. Build climate resilient
actions into management plans for forests under all management modalities.

Integrate adaptation actions defined in NAPA into forest sector planning and
administration.

Explore the future options for the compliance market for carbon in Nepal’s forest sector –
for example focusing more on other climate-related services such as water or biodiversity.

Continue to pilot PES activities with a view to expanding this approach to financing for
forest management and conservation in future (including carbon finance and other
environmental services)
129
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Yadav, B.R. (2007). Human-Elephant Relationships and Conflicts in Eastern Nepal. The Initiation
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Yonzon, P. (2004). Threats to Nepal’s Protected Areas. Parks 1491, 35-39
132
Annex 1: Reports Prepared by the Master Plan for the Forestry Sector (MPFS)



Executive summary
Main report
Sub-plan reports
 Forests development plan for the supply of main forest products
 Forest-based industries development plan
 Wood-based industries
 Medicinal and aromatic Plants









Soil Conservation and watershed management plan
Plan for the conservation of ecosystem and genetic resources
Forestry sector policy
Institutional development plan
Human resources development plan
Forestry Research development plan
Forest resources information; status and development plan
Impacts and monitoring Plan
 Environmental impact assessment
 Financial and economic analyses
Supporting report
 Country background
133
Annex 2: Gazette notification on NTFPs
Date (BS)
20/12/2051


Notice published under art 70a of Forest Act 1993
Ban on collection, collection, use, transport and export of Cordyceps
sinensis and Dactylorhiza hatagirea
Ban on export of Nardostachys grandiflora, Rauwolfia serpentina, Lichean
spp., Rock Exudat, Abies spectabilis, Taxus spp. without processing.
08/10/2053

Ban on export of Nardostachys grandiflora, Rauwolfia serpentina, Lichean
spp., Rock Exudat, Abies spectabilis, Taxus spp. without taking permission
from DoF and without processing.
01/11/2057

Ban on collection, collection, use, transport and export of Dactylorhiza
hatagirea, Juglans regia and Picrorhiza scrophulariiflora
16/09/2058

Ban on export of Rock Exudat and Cordyceps sinensis without process
01/08/2060

Picrorhiza scrophulariiflora can be exported on the basis of permission
provided by DoF considering the availability of this species
18/06/2061

Cordyceps sinensis can be exported without processing
09/05/2065

Mark of banned species can be exported by taking permission of DoF
16/07/2066

All banned species will be regulated under the Import and Export (control)
Act 2013 (BS) Note: this notice was published by the Ministry of
Commerce and Supply.
134
Annex 3: Ratified/accessed/signature by Nepal in MEAs
1. Convention on Wetlands of International Importance Especially as Waterfowl Habitat (Ramsar
Convention), 1971
2. Convention on for the Protection of the World Cultural and Natural Heritage, 1972
3. Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES),
1973
4. International Tropical Timber Agreement (ITTA), 1994
5. Convention to Combat Desertification in those Countries experiencing devious Drought and or
Desertification, Particularly in Africa 1994
6. United Nation Convention on Biological Diversity, 1992
7. Cartagena Bio-safety Protocol to the CBD, 2002
8. ILO convention No. 169, (Indigenous and Tribal Peoples Convention, 1989)
9. (a) United Nation Framework Convention on Climate Change, 1992
(b) Kyoto Protocol to the UNFCCC, 1997
10. (a) WTO – Trade Related Intellectual Property Rights (TRIPs)
(b) WTO-Agreement on Agriculture (AoA)
(c) WTO- Agreement on application of sanitary and phytosanitary Measures
11. International Plant Protection Convention (IPPC), 1952
12. Plant Protection Agreement of the Asia and Pacific Region, 1956
13. Rio Declaration on Environment and Development 1992 (Rio Principles)
14. Rio+ 20 declaration 2012 (Future we want)
15. UN Millennium Development Goals (MDGs)
16. UN Non-legally binding instrument on all types of forests, 2006
17. 16th Summit (2010) Thimphu Silver Jubilee Declaration “Towards a Green and Happy
South Asia”
135
Annex 4: Bottom up planning process in the forestry sector
136
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