WORKING PLAN

                                         

Working Plan has been the main instrument of forest planning (more exactly forest working) in
the country for scientific management of forests. It is a very useful document for evaluating
the status of forests and biodiversity resources of a forest division, assessing the impact of
past management practices and deciding about suitable management interventions for future.
Periodical up-dating and revision of working plan is essential to keep pace with the trends
emerging out of forest–people interface and to address national and international obligations.
Brief historical reference of planned working of forests in India may be counted as under;
i.
The first planned working of forests in the country was crafted in 1837 by Mr. U. V.
Munro, the then Superintendent of Forests in Travancore. On the basis of his personal
observation and long experience of working in the woods he estimated that about
100,000 trees of teak were fit to be felled. Later in 1856, Dr. Dietrich Brandis propounded
the fundamental principle that the first class trees (trees over a prescribed diameter) to
be felled in a year should be restricted to the growing stock of the second class trees that
will eventually replace them in that year. Based on this principle of yield control, he
prepared the first forest management plan using strip sampling for the Pegu Yoma
Forests of Myanmar in the year 1860.
When the Forest Department was decentralised in 1882, it caused a major setback to the
progress of working plans. However in 1884, the diligent efforts of Sir Wilhelm Schlich,
Inspector General of Forests, resulted in a country wide unified approach towards the
preparation of working plans and scientific management of forests as per prescription of
working plans. The experience so gained in the past led W.E. D'arcy to bring out his
treatise “Preparation of Forest Working-Plans in India” (1891), providing guidelines for
systematic working plan preparations.
From 1906, the work of checking working plans was entrusted to the Superintendent of
Working Plans stationed at Forest Research Institute, Dehradun. It is from this time the
working plans in our country reached the stage of academic discussions based on
research undertaken in the institutional forum. Working plan officers based their
prescriptions on more definite information about the silvicultural characters of most of
the important tree species, techniques of obtaining their regeneration and their probable
response to the main silvicultural treatments. However, central control was once again
lost in 1935 and felling of forests was carried out in total disregard to the working plan
prescriptions.
After India became independent in 1947, the forest department undertook big drives to
recover substantial areas under the working plans. For the next half a century, the
state/provincial governments adopted their own provincial working plan codes. As per
regional requirements, provincial working plan codes were adopted in different states of
the country. However with the intervention of Hon. Supreme Court of India in 1996, it
was clarified that all working plans were to be approved by the Central Government on
account of forests being brought in the concurrent list. The Ministry of Environment and
Forests (MoEF), Govt. of India then adopted a uniform code, the National Working Plan
Code - 2004 for preparation of working plans for the management of forests under the
prescriptions of a working plan/scheme to standardize the procedure. The working plan
facilitates monitoring, evaluation and impact assessment of forest management practices
being followed in the country.
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2.
Preparation of working plan is a highly technical exercise under taken at regular interval in
each forest division. The preparation of the working plan is based on stock and vegetation
maps which is prepared through ground surveys. Recently, the use of modern tools like
remote sensing, GIS and GPS is being utilized for preparing the forest cover maps of forest
divisions. Every working plan includes the area specific scientific prescriptions for proper
management of forests of a particular forest division, while working schemes are prepared for
smaller areas for a specific purpose or for forest areas under the control/ ownership of such
bodies as private, village, municipal, cantonment, autonomous district council (especially in
north eastern states), etc. These prescriptions enable necessary co-existence of development
with nature for simultaneous implementation of Indian Forest Act, 1927, Wildlife (Protection)
Act, 1972, Forest Conservation Act, 1980, Panchayats (Extension to the Scheduled Areas) Act,
1996 (PESA), Biological Diversity Act, 2002, and Scheduled Tribes and Other Traditional Forest
Dwellers (Recognition of Forest Rights) Act 2006; and meeting the requirements of the
objectives of the National Forest Policy and other international conventions/agreements.
All forests are to be sustainably managed under the prescriptions of a working plan/scheme.
The National Forest Policy clearly states “No forest should be permitted to be worked without
an approved working plan by the competent authority”. It is the duty of the manager or owner
of the forest area to ensure the preparation of the working plan / scheme. The authority as
designated by the MoEF, will approve the working plan and ensure its implementation. Even
working schemes have all major elements of a working plan and these schemes also need the
sanction of the competent authority.
There has been a paradigm shift in the objectives of management of forests and forest
management has become more people centric and oriented to provide the goods and services
from forests on sustained basis, with an emphasis on ecological services and harvest of
usufructs as well. The working plan should be in consonance with general planning, which is
village based. Therefore the working plan should encompass the village as a unit and realign
the compartments accordingly. Proper guidelines for sustainable use of community forests;
extraction, processing, market and trade of minor forest produce, etc. may be provided under
separate working circles. Forest community rights related to community forest resources,
minor forest produce, grazing grounds, water bodies, etc. recognized under the provision of
the Forest Rights Act, 2006, can be exercised within the framework of sustainable use. On the
other hand, management of forests adversely affected by mining, industries, urbanisation and
other non-forest activities is also of great challenge for which special planning initiatives are
needed.
For involvement and benefit of local stakeholders, micro plans are to be prepared within the
ambit of working plan prescriptions for Joint Forest Management (JFM) areas and eco
development plans are to be prepared for eco-sensitive forest areas adjoining the notified
protected areas. The microplan of jointly managed forests is prepared by the members of the
Joint Forest Management Committee (JFMC), through Participatory Rural Appraisal (PRA), with
the technical assistance of forest staff of the territorial division as per MoU, for sharing the
responsibilities of implementation and equitable sharing of usufructs among the stakeholders
within the broad prescriptions of working plan. Micro plan is approved by concerned Working
Plan Officer (WPO)/Divisional Forest Officer (DFO)/Forest Development Agency (FDA) as per
prevailing conditions in the state/UT. Proper implementation of the micro plan by each JFMC
should be reviewed at least once in two years by the Forest Development Agency (FDA).
3.
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National Working Plan Code– 2014
CHAPTER II
OBJECTIVES AND OTHER ESSENTIALS OF
  FOREST MANAGEMENT PLANNING
OBJECTIVES OF FOREST MANAGEMENT PLANNING
6.
Forest Management Planning must provide for sustainable management of forests and its
biodiversity as enshrined in the National Forest Policy, encompassing the ecological
(environmental), economic (production) and social (including cultural) dimensions. The
objectives for attaining this goal include conservation of forests and reducing forest
degradation, maintenance and enhancement of ecosystem services including ecotourism,
enhancement of forest productivity together with establishment of regeneration to improve
forest health and vitality as per ecological and silvicultural requirements of the species,
progressively increasing the growing stock and carbon sequestration potential, maintenance of
biological diversity, sustainable yield of forest produce, prevention of soil erosion and
stabilization of the terrain; improvement and regulation of hydrological regime; people’s
involvement in planning and management of forests fulfilling socio-economic and livelihood
needs of the people, albeit with simultaneous implementation of Indian Forest Act, Wildlife
(Protection)Act, Forest Conservation Act, Biological Diversity Act, PESA Act and Forest Rights
Act. All these entail that the specific composition and the structure of forests must harmonise
with the environment of the locality.
BIODIVERSITY CONSERVATION AND DEVELOPMENT
7.
Forests provide habitat for many plant and faunal species. The contribution of individual species
to the overall diversity within a community or ecosystem varies to a great extent. The
coexistence of organisms that differ widely from each other contributes more to overall
diversity than the co-existence of very similar species. Functional diversity is considered to be
one of the main factors determining the long-term stability of an ecosystem and its ability to
recover from major disturbances. Assessment of status of plant and faunal species and their
periodic monitoring can be helpful in formulating strategies for conservation, maintenance and
enhancement of overall biodiversity through sustainable management and use practices.
Assessment of biodiversity especially the lower forms of life (algae, fungi, lichens, epiphytes,
parasites, etc.) of a forest division must be made an on-going programme with the support
from State Biodiversity Board as it may be difficult for the working plan officer (WPO) to do it
within two years, the normal time allotted for writing the plan. All these assessments will help
in updating and enriching the People's Biodiversity Registers (PBRs) as provided in Biodiversity
Act, 2002.
JOINT FOREST MANAGEMENT
8.
Joint Forest Management is sharing of responsibilities, authority and usufructs between the
village community or the forest user group and the forest department on the basis of a
memorandum of understanding (MoU) between the two. The management of the jointly
managed forests is done through the provisions of a micro-plan prepared by the community on
participatory rural appraisal (PRA) basis with the technical help of the officials of the forest
department. Micro-planning should be done in conformity with the overall working plan
prescriptions of the forest division and may be reviewed by working plan wing of the state
forest department. Approval of JFM micro-plan from MoEF is not necessary as they are covered
by the macro level prescriptions of working plan of the forest division. Any deviation from the
macro level prescriptions will require prior approval of the Regional Office (MoEF).The latest
directives issued by the MoEF /State Government for preparation of micro plans should be
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incorporated in the JFM overlapping working circle. The compartments falling within any JFM
may have to be realigned/ subdivided to keep them within the respective JFM/village
boundary. Analysis of implementation of JFM programme, grading of JFMC, award winning
JFMC, women's participation, etc. should be provided in the working plans. It should be made
necessary to assess the dependence of villagers on the forests for their livelihood needs. Field
works like socio-economic survey including NTFP survey, problems of grazing and firewood
needs should be analysed carefully before making prescriptions for JFM. The activities related
to JFM during the past working plan period along with results and comments over the results
should be included in the preliminary working plan report (PWPR) along with supporting data.
COMMUNITY FOREST MANAGEMENT
9.
Forest community rights related to use of community forest resources like minor forest
produce, grazing grounds, water bodies, etc. recognized under the provisions of the Forest
Rights Act 2006 or any other State Act/Rule (e.g. Van Panchayats in Uttarakhand), can be
exercised within the frame of sustainable management. The term “sustainable use” given in
section 2(n) of the Forest Rights Act, shall have the same meaning as defined under section 2(o)
of the Bio-Diversity Act, 2002. As per section 2(o) of Biodiversity Act, “sustainable use means
the use of components of biological diversity in such a manner and at such a rate that does not
lead to the long term decline of the biological diversity thereby maintaining its potential to
meet the needs and aspirations of present and future generations”. Details of existing rights are
to be provided so as to assess their sustainability, reasoning for their continuity and
enhancement of productivity. Therefore, special efforts in the form of good practice guidance,
capacity building, orientation, provision of incentives for the exercise of rights would need to be
provided not only for preparation of working plans of such community forests but also for
creation of various working circles as per the prevailing conditions of the division to maintain
the sustainability of these forests. This will also facilitate Gram Sabha to monitor the working of
the committee constituted under clause 4 (e) of Forest Rights Rules 2012, which shall prepare a
conservation and management plan for community forest resources in order to sustainably and
equitably manage such community forest resources for the benefit of forest dwelling scheduled
tribes and other traditional forest dwellers and integrate such conservation and management
plan with the micro plans or management plans of the forests.
FRINGE FOREST MANAGEMENT
10. In general, the forest fringe area is conspicuously different from the inner forest due to close
    contact with local communities. Although the dependence of forest fringe villages and their
    interaction with forest is almost same, but the kind of interaction and its severity may vary from
    one type of forest fringe to another. The communities living in the forest fringes depend heavily
    on the forest for their fuel wood and fodder needs. In rural households, fuel wood is used for
    cooking as well as for heating water and household heating, more so in the hilly regions. The
    dependence of villagers’ is heavy because commercial sources of energy are not easily available
    due to varied reasons. Non-timber forest products (NTFPs), referred to, in the system of
    national income accounts, as minor forest products are source of livelihood and food security
    for a large number of rural communities living in and around forests. They are important to
    rural households in terms of their contribution to health, food, energy and other aspects of
    rural welfare. The importance of management of the fringe forest lies in the fact that if properly
    managed, it can arrest people's entry into the forest by catering to their needs at the fringe
    only, thereby sparing the forest from the biotic pressure that has the potential to cause
    irreparable damage to the forest biodiversity and eco-system services. Forest fringe villages
    have been a major cause of forest fires due to increased dependency of people on forests as
    stated above, thus causing the forest more vulnerable in terms of fire. Alternatives may be
    discovered to reduce the dependency of people on forests residing in fringe forests.
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WATER RESOURCES MANAGEMENT
11. The forests are also sources of water (surface, sub-surface and ground water). Over exploitation
    of the ground water resources results in declining ground water levels; there is an urgent need
    to augment the ground water resources through suitable management interventions. It is
    desirable to have forest management practices dovetailed with the principles of watershed
    based development approach especially in the source areas of water. Such areas should have
    restrictions on tree felling but there should be operations to improve the water regimes and
    natural regeneration. As such, special provisions should be made in the working plan to sustain
    water resources and livelihood issues of the people living in and around natural inland water
    sources.
SOIL AND WATER CONSERVATION
12. Heavy rains and rapid run-off severely affect not only the top fertile soil but leads to formation
    of gullies within forest areas. Suitable management imperatives need to be formulated to stop
    forest degradation due to natural causes and calamities. Apart from silvicultural operations, it is
    also necessary to make appropriate prescriptions for conservation of soil and water in the
    forest areas. Areas susceptible to soil erosion such as steep slopes and areas in the vicinity of
    perennial streams, etc. should be focussed for soil and water conservation interventions with
    the provision of an overlapping working circle.
FOREST HEALTH AND DISEASES
13. The pests significant to the Indian forests in the recent past are the sal borer, leaf gall of
    Eucalyptus, shisham mortality, etc. Interestingly, these pest phenomena cover both natural
    forests as well as plantations. Based on generalized symptoms (spots, wilt, etc.) and signs
    (mushroom like fruiting bodies); nature of pathogen- whether fungi, bacteria, nematode, plant
    parasite, etc.; pathogen survival especially in relation to weeds; photographic documentation
    of the problem and their confirmation through internet sources and expert advice; mapping of
    disease distribution may be done. Such details are very vital for timely diagnosis and effective
    management of the problem. Role of silvicultural practices that can reduce the pest problem;
    knowledge of species phenology to collect healthy seeds from the trees before they fall off on
    forest floor; scientific felling to reduce the standing tree damage as injury serves as an infection
    court for many heart rots, etc.; nutrient status of the soil governing the susceptibility/resistance
    of the host in many cases; identification and selection of superior individuals also as a source
    for resistance against the disease; identification and evaluation of lesser known species (and
    weeds) of an area for their biochemical profiling including bio-pesticide properties, etc. can be
    an effective, eco-friendly, economical and easily available source for pest/disease management.
FOREST FIRES AND PROTECTION
14. Forest fires are as old as the forests themselves. They sometime pose serious threat to the
    biodiversity and ecology. Forest fires have environmental impact in terms of tropical biomass
    burning, which produce large amount of trace gases, aerosol particles, and play a pivotal role in
    troposphere chemistry and climate aberrations. Thus, there is a need to carry out fire frequency
    and burnt area mapping for fire vulnerability on one hand and operational fire monitoring in
    real time/near real time for effective response on the other. Real time monitoring of forest fires
    is being carried out by FSI using MODIS sensor fire alerts on-board two of the satellites - Terra
    and Aqua. The processed signals on forest hot-spots are being transmitted to SFDs on regular
    basis during fire season. Hence real time monitoring of forest fires is a process now in operation
    to curtail fire severity and sensitize SFDs at operational level to prevent normal fires in getting
    converted into wild fires. The online feedbacks on forest fires which are a part of this system
    could help estimate the actual loss of forest strata as well as the loss caused to top-soil.
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FORESTS AND CLIMATE CHANGE
15. Climate is an active factor in the physical environment of all living things. Climate change and
    variability are impacting forest ecosystem processes and functioning. Response time of forest
    ecosystems to disturbances ranges from a very short duration to decades and even centuries,
    depending on the condition of the system and the type, intensity and duration of the external
    stimuli. The actual state of forest ecosystem largely depends on processes and practices of the
    past. Therefore, forests are extremely complex to understand their functioning. Climate change
    further magnifies those complexities and adds more uncertainties. Forests are linked to climate
    change in three ways; i) they are source of greenhouse gas (GHG) emissions; ii) they offer
    mitigation opportunities to stabilize GHG concentrations; iii) they are impacted by climate
    change. Impacts of climate change on forest ecosystem are getting manifested as species range
    shifts, changing biodiversity, physiological changes in plant life cycles, forest growth pattern of
    species, changing boundaries of ecosystems and other biotic and abiotic responses/ stresses.
    There are evidences of increase in the frequency and severity of forest fires, changing water
    regimes and expanding forest insect infestation. Since forest ecosystems operate on large
    temporal scales, long observational studies are necessary to identify the key changes.
    Accordingly grid based sampling is designed to provide relevant information to cover the
    characteristic time scales.
CARBON SEQUESTRATION AND MITIGATION
16. Forests and wood products can effectively reduce the process of climate change in several
    ways. Growing trees absorb carbon dioxide from the atmosphere and store the carbon so
    efficiently that about half the dry weight of a tree is carbon. This carbon remains locked up in
    the form of wood and wood products. Sustainably grown and harvested wood (and other
    biomass) also provides a renewable alternative to fossil fuels and enhance carbon storage.
    Enhanced carbon sequestration through recognised and innovative silvicultural practices, eco-
    restoration of degraded/mined out forestlands, improved biomass productivity, etc. will help in
    improving forest health and vitality. Forest soil must be kept healthy and fertile. The growth of
    forest crops must be kept vigorous to attain the most desirable level of biomass production
    within an optimal time scale.
REDD+
17. REDD stands for reducing emissions from deforestation and forest degradation. REDD+ (Plus)
    includes forest conservation, sustainable management of forests and enhancement of carbon
    stocks, and has been adopted by the United Nations Framework Convention on Climate Change
    (UNFCCC) as a tool for climate change mitigation. Deforestation happens when forests are
    cleared and such land is put to other than forest land use. Forest degradation implies a gradual
    depletion of forests driven by demand for biomass and disturbances like fire and soil erosion,
    which, result in dwindling carbon density and ultimately leading to complete loss of forests.
    Implementation of REDD+, therefore requires efforts/mechanisms to measure forest carbon,
    interventions and payments to local people in addition to alternative activities such as fodder
    development to avoid lopping of tree branches, efficient cooking energy devices, etc.
APPLICATION OF MODERN TECHNOLOGIES
18. Geomatics (Remote sensing, GIS and GPS) has got a wide range of applications in forest
    management. One can find application of geomatics in almost every forest management
    practice e.g. forest cover mapping in different canopy density classes, change detection
    (degradation as well as improvement), forest fire detection, burnt area mapping, biodiversity
    mapping, afforestation planning, wildlife habitat suitability mapping, boundary demarcation,
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encroachment mapping and so on. For many of these applications, there are no practical
alternatives to geomatics based methods.
19. A spatial database on forest in GIS is a set of geo-referenced layers of spatial data of an area on
    different themes relevant to forest manag