Showing posts with label forest landscape restoration. Show all posts
Showing posts with label forest landscape restoration. Show all posts

Tuesday, February 2, 2016

36 Process projects in a world of physical objectives. Forest Landscape Restoration in India-VII.

Landscape approach and the art of 'muddling through'

As can be seen from the somewhat ambivalent results of various ‘integrated’ approaches in the past, implementation of the Green India Mission, GIM (or the forest landscape approach, FLR, in general) can be expected to be less than perfect. Given the predilection of academic researchers to judge the results against very exacting standards of equity and process integrity, the ultimate results are bound to fall short. However, state actors (e.g. forest departments) are answerable, based on a completely different set of  expectations, to the state organs (Parliaments, statutory  auditors, courts, etc.): that expenditures result in measurable physical outputs.  Processes are seen only as one component of the means to the ends, and there is no excuse for failure to produce physical output merely on the plea that the people are not ready, or the process did not throw up a consensus, etc.



(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)

Kemmangundi, Karnataka landscape: naural forest and coffee shade trees (silver oak) 

In a world where the official environment requires clear-cut physical results, certain precautions are essential in taking up projects or activities that are strong on the rhetoric of process-orientation.  A basic precaution is to ensure that the project has a core of sure-fire physical outputs that will be achieved through the normal working systems of the departments concerned, regardless of the success, failure or quality of the processes prescribed. No government department will even think of getting into any considerable expenditure programme unless there were some physical output guaranteed, especially a land-based department like the forest, where obviously some sort of crop has to remain at the end of the day. Because the process component is by definition bound to be a disappointment (especially with the constant changing of objectives and redefining of measuring scales by social scientists),  the implementing agency will be able to justify the expenditures only if there is a physical resource left at the close of project. That is why, in past project interventions, the forest departments (at least in India) have held almost fanatically to the crop development targets, much to the chagrin of the social analysts. This is also the reason why programmes like the social forestry (SF) projects, the DFID-funded Western Ghats Forestry Project (WGFP), and the joint forest management (JFM) programme, are seen as successes by the department, even though they are almost complete deemed failures from the sociologists’ viewpoint. Physical targets are the safety nets of the forest department, which operates in a remorseless world where inputs have to match with some concrete physical result. Indeed, if any substantial incremental (extra) expenditure is to be incurred, say for special project staff and project directorate and planning/management units, then it would be foolhardy for the department to ignore physical outputs (otherwise the extra expenditure cannot be justified, and will probably be recovered from the officials responsible, or disciplinary action initiated against them).

This is also the reason why exact synchronization of process with physical operations cannot be maintained: the plantations will be raised even if the committees are not formally present (which has been touted as a major deficiency), and communities may have to play catch-up with the physical progress at times. Sometimes, no doubt, believing is seeing (the thought precedes the reality), but most of the time in the real world, in fact people wait to adapt to a changing physical reality brought in by outside forces: seeing is believing. On the other hand, if a purely process-centered project is being pushed by policy makers (in our experience mainly the international donors and consultants, to which JICA is perhaps an honorable exception), then local counterparts in the recipient countries would be wise to rigorously eliminate all extra expenditure, all special staff and directorates, for example (which may end in zero physical output, but lots of workshops, and overseas consultants, whether paid for by the implementing agency or directly by the donor through the technical cooperation component). They should rather attach the additional work relentlessly to existing positions and agencies. In the Green India Mission (GIM), for instance, national coordination was entrusted to the existing National Afforestation and Eco-development Board (NAEB) at the ministry of environment and forests; in the states, the existing State Forest Development Agency (SFDA) and the district FDAs are to be entrusted the new responsibility, and the operations in the field also will be handled by existing structures; this is as well, since there is no guaranteed funding for the field operations.

The dilemma with such ambitious, over-arching, all-embracing, holistic, integrated, process-priority interventions like the landscape approach is that they want to bring together all players to indulge in exhaustive discussions and consultations before embarking on action, but the catch-22 situation is that they will not be able to pull in collateral actors unless they hold out carrots in the form of financial resources, infrastructure investment, perks like foreign visits or at least buildings, vehicles and computers, and so on. But the paradox is that money for such components can rarely be garnered (whether from government budgets or from international aid agencies) on any large scale unless there is a guaranteed physical result of appropriate magnitude. To incorporate such physical results, many decisions will have to be taken at the time of presenting the project proposal itself, thereby pre-empting the process activities. If communities feel that the department may have some substantial money in its hampers, they may deign to come to consultations; if they know that the department has still not got the funding, they may not be interested in mere talk.

Even with committed funding and guaranteed physical outputs, the state auditors may well pull up the departments if there is a mis-match between targets shown in the project document and the actual outcome on the ground, as may well happen if processes are permitted to dictate in-course corrections and modifications in operations.  Thus the deviation from the model-wise plantation targets in the approved project document was made a big issue in the audit of the WGFP described previously, because the donor agency’s stand against pre-determined models and targets (this was supposed to be a process project) was limited to oral and personal communications, and could not be put up to the audit authorities, who only recognized the cabinet-approved final project documents (FPDs).  Based on such unpleasant experiences, the author strove to incorporate in the GIM document a paragraph especially to the effect that being a process-based programme, actual achievements may not conform exactly to the model-wise areas indicated in the document. Whether audit will understand this during the inevitable post-mortem analyses is of course left to the future. In any case, if there are mid-corse deviations, implementing agencies should not neglect getting such changes approved or ratified at the highest required levels. Thus, if the original document was approved at the cabinet level, it should be ensured that all major deviations are also got approved by the donor and the state government at the Cabinet level.

One of the recurring dissatisfactions expressed by social analysts, with projects implemented by the forest departments, is their unwillingness to let go the control of the forest areas to the community. Social environmentalists want JFM and forest governance to go to the next level, where communities will be the sole masters rather than mere participants (see, e.g. Lele & Menon, 2014). The donor agency, DfID, was especially disappointed with the pace of this type of institutional change in the WGFP in Karnataka, which was probably the reason for not extending the project to a second phase after 2000. However, social environmentalists and aid agencies must understand that their interventions are usually short-lived (three to five years for a Ph.D. scholar, five to ten years for an externally aided project),   and the financial contribution is usually miniscule in proportion to the national budget; obviously it has to fit into the existing departmental set-up, and not vice versa. While the integrated approach looks good in theory, words come cheap, and if all these aspects are actually to be covered by action on the ground, there will probably be not enough resources for even one landscape, let alone for a national programme like the GIM. This does not mean that departments and communities should fold their hands in their laps and sit quiescent; it means, instead, that they will probably plan and keep on the shelf  a series of smaller interventions, and opportunistically fulfill whichever are possible depending on the funds and personnel available from different sources. This calls for a time horizon much longer than the five to ten years of an average externally aided project. At the end of the project, the forest department (or whichever is the main implementing agency) is still in place, and has to take care of things just as if the project never existed; not the least of the responsibilities being the continuing salaries of the staff added for the project, and further protection and tending of the plantations and community institutions set up during the project . Thus, the implementing departments have to be pardoned if they do not fall in with the more extreme urgings of the aid agencies and social experts to abdicate their role and position with alacrity.

The danger in over-arching concepts like ‘integrated’ or ‘holistic’ or ‘landscape’ or ‘national’ or ‘global’ is that they may lull the user into a sense of omniscience and omnipotence that is not justified. It is because of this fatal attraction of big words that many well-intentioned schemes and projects that have over-weening ambitions of social engineering do not work, as demonstrated by James C.Scott in his book Seeing Like a State (Scott, 1999) on ‘high moderrnism’ and its relevance to large projects (the sub-title being How Certain Schemes to Improve the Human Condition Have Failed). In this context, Lindblom’s contrast between ‘synoptic’ and ‘incremental’ programs and the option of “muddling through” rather than claiming some perfect solution is surely pertinent and cautionary to landscape approach enthusiasts (Lindblom, 1959, 1979).

In conclusion, is submitted this statement made by the author, as DG Forests of India at the Roundtable on “Forests and People”, during the High Level Segment of the UN Forum for Forests, 2 February 2011:

“Forestry in modern India has, over the past one and a half centuries, built on two major foundations: firstly, giving protection to the resource itself by legal and administrative measures to identify and notify forest reserves, and secondly, working with the communities to maintain over the long term the productivity of services and materials from the forests, in support of their agricultural needs and livelihood occupations…  It has been our experience that all the different strands of the polity are important in ensuring the long-term survival and sustainable management of this precious resource: well-thought out legislation, a strong and independent judiciary, strong community and civil society participation, and a professional state forester cadre and other administrative personnel and apparatus”.

(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)


References (for all sections)

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Monday, February 1, 2016

35 Green India Mission (GIM): carbon with benefits. Forest Landscape Restoration in India-VI.

The Green India Mission (GIM): carbon sequestration with benefits

(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)

This brings us to the final (and most recent) application of the landscape approach in forest restoration in India, the Green India Mission (Government of India, 2010, 2011). This started out as a straightforward forest carbon sequestration programme statement  as one of the eight missions of the prime minister’s National Action Plan on Climate Change. However, it was apparent from previous experiences, such as the social forestry projects and the JFM based projects, that any intervention in the forest sector was bound to have a whole trail of collateral considerations, external effects, and social and environmental concerns, so that it would be foolhardy to design a project or programme solely for increasing carbon in the standing forest crops. Therefore, while at the core there remained the target of raising 5 million hectares (mha) of new forest and improving the condition (standing volume) of another 5 mha of existing growth, there had to be a process-oriented, bottom-up, participatory, approach to identifying the locations and character of these crops and interventions. As can be seen from the mission document and brochure, the actual interventions would be integrated with  restoration and improvement of a variety  of ‘ecosystems’ or ecological types, such as forest of various densities, wetlands, scrubland, grassland, mangroves, cold desert, abandoned mines, and agro-forestry, and social forestry-type interventions  on 3 mha non-forest land , not forgetting institutional lands, urban and peri-urban lands, and so on. Thus the programme would have multiple benefits apart from sequestering carbon, such as improving habitats and conserving biodiversity[1], restoring degraded lands and reducing soil and water loss, improving urban and rural environments, and supporting livelihoods through such interventions (this could be from agro-forestry, or from non-timber products in the forest or outside it, and integration with other rural sectors such as livestock/fodder, etc.). There are also to be a number of “cross-cutting” interventions like livelihoods enhancement, improving fuel efficiency of wood-burning stoves and promoting alternative energy, etc.

Hacked forest. Purdal, Shimoga, Karnataka, May 1990

Result of protection, Purdal, Shimoga, Karnataka, May 1990

Of specific interest here is the explicitly stated intention to adopt the “landscape approach”, which is interpreted as small to medium catchments around the village/ settlement of say 5000-6000 ha. The mission is to be multi-sectoral and multi-stakeholder, with the community  being in charge of identifying problems, devising responses, and monitoring the implementation, which is expected to be done through the gram sabha (GS) and the “revamped” JFM committees  and Forest Development Agencies (FDAs) in the districts under the aegis of the panchayat raj  institutions (PRI). The challenge lies in the fact that the government has not provided separately in the Plan document or annual budgets for the Rs.45,000 crores[2] (say USD 7 billion) that is the estimated  cost over the next 10 years; the mission is to be funded by convergence from other on-going programmes, schemes, and missions, such as the flagship Mahatma Gandhi National Rural Employment Guarantee Scheme (MNREGS) which has a budget of around Rs.50,000 crores a year (Government of India, 3 March 2015).  

Criticisms and problems of the landscape approach in GIM

Not surprisingly, social environmentalists and commentators have been quick to jump on the GIM on account of the possible equity repercussions (as in the case of the SF projects, JFM in general, WGFP in particular, etc.).  The Forest Rights Act website (www.forestrightsact.com) describes the “Dangers of the Green India Mission: A formula for more land and resource grabbing”, and states that it is all a ploy to grab the communities’ resources and convert them into carbon credits. Sourish Jha, Assistant professor at the Department of Political Science, P.D.Women’s College, Jalpaiguri, West Bengal, charges that “the so called community institutions implicitly or explicitly involve an inclusive technique of exploitation of forest communities under the rubric of ‘public-people participation’.” His paper seeks to “expose further the neo-liberal schemata for incentivization of the community service through GIM for raising carbon stock to promote an integrated carbon market which ultimately will lead to defacement of the organic relationship between the community and the forest” (Jha, no date, probably 2011?). The web-based journal Equations (December 2011) calls the GIM “India’s REDD+ Action Plan to disempower and evict forest communities from their own homelands”.  A parallel paper on the equitabletourism.org website (ascribed again to Equations) charges that “GIM targets these areas for large scale afforestation programmes with fast growing native species and closure to grazing on rotational basis thereby preparing the ground for displacing the forest communities from these last forest areas, so depriving them of their habitat and livelihood options”. In a more balanced critique, Sumana Dutta (2016) feels that the GIM document is handing down a pre-conceived menu of options, which may not all be appropriate in the specific situations of a locality, such as the Bankura forest of West Bengal that the author was familiar with. On a different note, Dutta very perceptively also comments that the experience of the ground staff needs to be brought in, which has been affirmed in this author’s  response in the Letters column of the following issue of EPW (Dilip Kumar, 2016).
Degraded Minor Forest, Honnavar, Karnataka, May 1990. Note plantation on hill-top

Some comments may be not out of place  here from the viewpoint of the forest administration. Firstly, it is very doubtful whether any carbon sequestered through increased growing stock on the ground, will ever be parlayed into dollars under the REDD+ scheme, since India is very unlikely to be a major candidate for international carbon funding, as explained previously by the author (Dilip Kumar, 2014b). Therefore, it may be an exaggeration to say that carbon markets are going to threaten local uses and communities. Secondly, the carbon captured has been seen consciously as a side benefit in the GIM document, although it is true that the first impetus came from the climate change mitigation interest. Although the initial drafts may have been cast mainly in terms of biomass accrual and carbon capture (much as the early draft of the WGFP was cast mainly in terms of improved status of the forests), those who were present at the discussions leading to the changed concept of multiple co-benefits will bear witness to the sometimes heated arguments that accompanied the drafting process. The point made by the foresters (among them this author) was very much on the lines that the social commentators are making, that it is difficult to make interventions in India’s forests without bringing in train social effects, and hence it is difficult, and inadvisable, to try to make projects aiming at increasing biomass on the ground, a purely technical problem.

Thirdly, almost any land-based intervention in India is going to have repercussions that may not always be equitable. The green revolution in agriculture, for instance, obviously has better benefits for the larger and better-off land owners, and mechanization and crop and composition technical change often has repercussions on the employment of low-skill wage labour (see previous references to Myrdal, 1968, pp.1344-45, 1367). But this does not mean that no change or progress should be attempted. Similarly in forestry, some interventions like closure of a particular patch of forest may impose costs on the landless or the women, especially in the initial years, but these could be compensated by earmarking other areas or developing sustainable harvesting practices, varying the density of planting,  and so on. In the single-interest schemes of the past, the forest department used to take up plantations on a restricted area without consideration for such spill-over effects, but under JFM and now the landscape approach, it is expected that the whole situation will be addressed, including provision for the landless, the women,  NTFP collectors, bamboo workers, etc. Perhaps the most important difference in the landscape approach would be the way the situation analysis and problem identification will be developed before finalizing the annual operational plans. The specific  models in the GIM document should therefore be taken as just suggestions, and the actual interventions are to be worked out on the ground through discussions.

During the formulation of the GIM and the public consultation sessions, feedback from many forest officers (privately to the author; the foresters were seldom given a hearing in public) was that the coordination of many different departments would be a problem, and that the only   feasible way to guarantee some useful outcome would be to give the implementing department a clear-cut objective and physical target, give it clear-cut and full responsibility for its own efforts, and provide the funds in a timely and dependable manner. For example, the forest department will be happy to take the responsibility for, say, raising nurseries and fuelwood and fodder plantations; but they would not be able to guarantee the timing and appropriateness of actions of other agencies, private or government, like the extension of compressed cooking gas fuels, minimum support price purchases of collected non-timber forest products, or provision of animal health services, and so on. This, of course, would relegate to lower priority the bottom-up, open-ended, consultative, community-led process envisaged in the landscape approach.

The GIM seeks to meet such problems by suggesting a somewhat convoluted management structure, by assuming that the central control will be with the district planning forum (a panchayati raj institution of elected representatives), while the funds may flow directly from the centre or through the district Forest Development Agency (FDA) which is looking after the National Afforestation Programme (NAP), and thence to the implementing entities which may be any of the bodies at the village or community level, under both the PRI umbrella (including, among others, the Forest rights Committees, Biodiversity Managememnt Committees, etc.), and the community-based organizations (CBOs) sponsored by the line departments (like the village forest committees, VFCs). Since synchronization of various components will depend on the willingness of other agencies not under the project’s control, the end result of an integrated project, however noble the intentions, may well be a lop-sided development of those elements that were in the control of the principal implementing department or agency.

A special problem with the GIM as rolled out in recent years is that funds have not been ear-marked in the national plan (see the author’s critique of the XII Plan, Dilip Kumar, 2015). On the other hand, most of the money is supposed to be brought in from other programmes like MNREGA, Plan schemes like the NAP, Finance Commission devolutions to the states, the Compensatory Afforestation funds (CAMPA), other Climate Change Missions, and so on. This poses the question, what is the real additionality contributed by the GIM. If the forest departments of the states  themselves may tend to see the GIM as an unnecessary addition to their work burden, with little financial backing, the other departments and agencies that are supposed to coordinate with the GIM management would tend to see it as a completely useless intrusion. Even the PRIs, the district planning structure, and the village bodies (Gram Sabha) may well see the GIM as an imposition, if it comes asking for funds from their budgets in addition to their time and efforts. This may well be the killer assumption that will make its success unlikely. The same would probably be true of any integrated, multi-sectoral approach: unless it comes carrying gifts (budget, expertise, technical cooperation, capacity building, infrastructure improvement, support for NGO and SHGs, foreign visits, and so on and on),  the target groups are liable to wonder why they should put their resources and time at its disposal.

Social objectives and the Forest Department

A question comes up, how far is the forest department responsible for social change and setting right inequities in the society. Sharachchandra Lele (Lele & Menon, 2014, p.52) accepts that poverty alleviation by itself is not a fair criterion to judge the success of JFM. In fact, if one makes a dispassionate economic assessment, it is not clear that poverty can be removed (even for forest-dependent tribals and others) by depending solely on forest produce, as returns from forestry are relatively low per unit effort and resource.  For example, after all the organizational effort for collection of tendu (Diospyros) leaves for the beedi (leaf-rolled smokes), the average collector is left with less than a month’s worth of wages in a year in Central India, at considerable cost to the trees’ growth as they have to be repeatedly cut to get a flush of leaves (and it may be added that beedis, the poor man’s cheroots, are a major cause of cancer). As for the forest department, it sees JFM mainly as a mutually beneficial way of rehabilitating degraded forest, but also as a way of generating and providing wage labour as a support to forest-fringe villages.

Bamboo plantation, Jabalpur, Madhya Pradesh. Oct 2011.


However, just because forest restoration is the starting point of JFM (or GIM, or the forest landscape restoration approach,  for that matter), this does not mean that the foresters are entirely neutral to poverty alleviation or equity considerations. After all, as a wing of the state executive, the forest departments also share in the national objectives of improving the condition of the poor, especially the socially and economically deprived (from whose ranks at least 25% of the forest personnel themselves are recruited), in addition to the environmental conservation goals. As a matter of strategy, also, if the department feels that rural poverty is part of the reason why people depend on sale of unsustainably collected wood and other forest products, then improving the rural incomes through other occupations can well become a part of the landscape conservation strategy.

Tussor silk moth larva, Jabalpur, Oct 2011.

Both the supply side and the demand side are then a candidate for the strategy. On the supply side, by creating more biomass (in fringe forest and non-forest lands) specially for the collectors (headloaders) and the local consumers, whether it be fuelwood or poles or bamboos for artisanal raw material, the programme will shift the users to a sustainable extraction regime, thereby saving the forest proper from unregulated hacking, cutting of saplings, setting of fire, etc. (the social forestry strategy). On the demand side, by providing other energy sources (e.g. liquid petroleum gas, solar water heaters and driers, biogas, etc.), the communities are gradually induced to reduce their requirement of forest biomass. By improving water harvesting and thereby supporting agriculture, pressure due to headloading, grazing, etc. on forest may be reduced. Therefore general improvement in the rural economy, e.g. by improving water availability, granting land (even marginal forest or shifting cultivation plots) to the landless (as in the Forest Rights Act, 2006), supporting new livelihoods (forest-based like lac, tussor silk cultivation, or others, like tailoring, computer operation), may well contribute to the ultimate goal of taking pressure off the forests. So the forest departments too may well have a long-term interest in poverty alleviation and equity considerations, and need not be condemned outright as opportunistically using the community as unpaid watchmen.




[1] The programme monitors and implementers would have to be extra vigilant in dealing with non-forest habitats like grasslands and wetlands, in order not to fall into the error of planting up all hectares with dense tree crops.
[2] Crore = 10 million

(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)

References

Dilip Kumar, P.J. 2014b. Climate Change, Forest Carbon Sequestration and REDD-Plus. The Context of India. Economic & Political Weekly, Vol. XLIX, No.22, May 24, 2014, p.22-25. www.academia.edu/11102870/...

Dilip Kumar, P.J. 2015. Forestry in the 12th plan. No tears for the Planning Commission India. Self-published as Forest Matters, No.7-9, February 2015. Available as a pdf at https://www.academia.edu/10833350/Forestry_in_the_12th_Plan_No_tears_for_the_Planning_Commission_India, and in blog postings at http://forestmatters.blogspot.com/2015/02/08-forestry-and-planning-commission-ii.html

Dilip Kumar, P.J. 2016. Green India Mission. Letters, Economic & Political Weekly, Vol.LI, No.5, Jan 30, 2016, p.4.

Dutta, Sumana. 2016. Continuing the Forest Conservation Debate: Rhetoric and Reality of Green India Mission. Economic & Political Weekly, 23 Jan 2016, Vol.LI, No.4, pp.49-55.

Equations. 2011. Green India Mission: India’s REDD+ Action Plan to disempower and evict forest communities from their own homelands. Equations, December 2011. Author Souparna Lahiri? Available at http://forestindustries.eu/sites/default/files/userfiles/1file/fileDocuments1131_uid18.pdf

Equitable Tourism Organisation (website). Forests, Communities and the “Green India Mission”: Promises and Failures of Ecotourism. (By Equations). Available at http://www.equitabletourism.org/files/fileDocuments1385_uid20.pdf

Government of India. 2010. National Mission for a Green India. National Consultations. Ministry of Environment  and Forests, New Delhi. Available at http://www.moef.nic.in/downloads/public-information/green-india-mission.pdf

Government of India. 2011. Green India Mission Brochure dated 26 March 2011 available at the ministry website, http://naeb.nic.in/documents/GIM_Brochure_26March.pdf

Government of India. 2015. Guidelines for convergence of MGNREGS with GIM. Memo .F.No.9-5/2015/GIM/MGNREGS dated 3 March 2015 of the Ministry of  Environment, Forests & Climate Change, New Delhi. Available at  http://envfor.nic.in/sites/default/files/MGNREGS-GIM_0.pdf

Jha, Sourish. 2011?. The Green India Mission (GIM): A Roadmap for Neo-liberal Exploitation in Forest.  http://www.iss.nl/fileadmin/ASSETS/iss/Documents/Conference_presentations/NatureInc_Sourish_Jha.pdf

Lele, Sharachchandra and Ajit Menon. 2014. Democratizing Forest Governance in India. Oxford University Press, New Delhi.

Myrdal, Gunnar. 1968. Asian Drama. An Inquiry Into the Poverty of Nations. Twentieth Century Fund, inc. Reprinted in India 1982, 2004, Kalyani Publishers, New Delhi.


Saturday, January 30, 2016

33 Joint Forest Management (JFM) as precursor. Forest Landscape Restoration in India-IV.

Joint Forest Management (JFM) as precursor to the landscape approach

Contemporaneously with the expansion of Indian forestry into the non-forest areas, individual forest officers had been experimenting with versions of the  joint forest management approach in different parts of the country (Saxena, 1997, p.45). The earliest such initiatives seem to have been those made in Arabari forest of West Bengal in the 1970s, and another early experiment was the formation of Hill Resource Management Committees to undertake soil and water conservation in the eroded hills around Sukhomajri in Haryana state.  Participatory approaches were also initiated in Gujerat, Orissa, and other states. These encouraging results, and the favourable environment provided by the 1988 forest policy,  prompted the Ministry of Environment & Forests (and Climate Change from 2014, hence MoEFCC) to issue the famous letter of 1 June 1990, exhorting all the states to take up JFM as a general programme. All externally-aided forestry projects from the 1990s (such as the DFID-funded Western Ghats Foresry Project, discussed below) have adopted JFM as their underlying principle and principal framework, as also the National Afforestation Programme (NAP), the ‘flagship’ scheme of the MoEF (see below). As a result, there are now over 120,000 JFM committees taking care of over 20 million hectares of forest (an estimate up to March 2010 is 112,816 committees covering 24.65 mha, see ICFRE, 2012, p.24).



(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)
Since JFM in India has been one of the most prolific generators of papers and theses, it will not be necessary to recount its history in detail here, apart from a very brief account of its features (see Saxena, 1997, for an early account, and the author’s monograph, Dilip Kumar, 2014, for a more detailed analysis from the point of view of common property management and decentralization). The forest department places at the disposal of the village or hamlet community,  a tract of (degraded) forest, and works with the community over a period of a year or two to enroll members on the proposed Village Forest Committee (VFC). Every adult citizen is entitled to be an independent member; usually both male and female household heads are given individual membership. The committee usually has an elected Chairman or President from among the villagers, and a Secretary (usually the Forester) from the forest department (FD) to keep the records, write the cash accounts, and liaise with the government. The villagers get together to draw up a ‘micro-plan’ for a 10- or 20-year horizon, usually using a PRA-type exercise with the help of a local NGO that is compensated by the scheme  or project which is funding the programme. The micro-plan includes an assessment of the forest-related problems and needs, the state of the resource, ways to improve the supply-demand position of forest products and ensure long-term sustainability of the environmental services (especially water conservation), capacity building (training, workshops, visits to demonstration plots) and processing and marketing facilities, financial and physical resources required, management systems and protection regimes, etc. A significant part of the JFM regime is the authorization to share the incremental benefits with the community: in practice, this means that all the firewood and lops and tops, prunings, brushwood, etc. is taken by the villagers, as also all non-timber products (which have in any case been assigned to the Panchayats by law) and a portion of net revenues from final timber harvests (usually 50% to 75%). Wage labour payments are an added benefit where there is dearth of work. An important part of the exercise is the identification of so-called ‘entry-point activities’: perhaps repair of a foot-bridge or bridle path, restoration of a drinking water source, desilting of a pond, repairing a schoolroom, etc. The philosophy is that when the community sits down with the FD and the NGO, there will usually emerge some pressing non-forestry problems of their own, so that it would be difficult to talk of forestry matters (which are usually way down in their priorities) unless some solutions can be found for the immediate pressing problems. The provision of a discretionary fund for these is a good way to smoothen the way to setting up an effective village forest committee (the process is sometimes termed the ‘forest journey’), as it builds interest in the activity and confidence in the sincerity and competence of the sponsoring agency. Otherwise it will be taken as empty talk, especially as the benefits arising from forest protection tend to be fairly distant in time, entail some sacrifice in the current periods, and are often nebulous until some concrete instances are shown.

It can be appreciated that, in comparison with the Social Forestry/Farm Forestry (SF/FF) approach, the JFM/VFC framework is a closer approximation to the landscape approach we are discussing here. The JFM/VFC approach requires the community to be involved from an early stage in the programme (right from situation analysis, identification of issues, drawing up of plans) through implementation and garnering benefits. Further, all sectors are considered in the village micro-planning exercise, if at least peripherally. Especially when discussing entry-point activities, capacity building, livelihoods support, etc., it is expected that decisions will be taken either to integrate other schemes and projects, or at least to approach other departments and sources of funding or other support. Especially where an NGO is involved, there is a likelihood that other activities will be brought in, such as a medical camp or animal health camp, renewable energy (solar, improved stoves, biogas), etc. One of the common programmes is to initiate, and advance seed money to, a number of micro-savings and loan groups or Self-Help groups (SHGs), that may become quite active in other fields like processing and marketing of local produce. Forest restoration may in fact be only one of the benefits, and as agriculture improves (through water harvesting, better techniques, crops, infrastructure for processing etc.), the dependence on the forest may well go down. Another spin-off of improved agriculture is the reduction in periodic out-migration for wage employment, gradual down-sizing of ‘scrub’ cattle herds and switching to stall-fed, improved milch animals, and increased attendance of children in schools (who would otherwise have been assigned low-priority chores like grazing the scrub cattle and collecting dung).

National Afforestation Programme (NAP) and JFM

As the approach to forest development progressively veered to the participatory, bottom-up mode, the central schemes of the forest ministry also changed their character. The National Afforestation Programme (NAP) was  formulated by merger of four IXth Plan centrally sponsored afforestation schemes of the MoEF, namely, Integrated Afforestation and Eco-Development Projects Scheme (IAEPS), Area Oriented Fuel wood and Fodder Projects Scheme (AOFFPS), Conservation and Development of Non-Timber Forest Produce including Medicinal Plants Scheme (NTFP), and Association of Scheduled Tribes and Rural Poor in Regeneration of Degraded Forests (ASTRP), with a view to reducing multiplicity of schemes with similar objectives, ensuring uniformity in funding pattern and implementation mechanism, avoiding delays in availability of funds to the field level and institutionalising peoples participation in project formulation and its implementation.[1]   The NAP scheme is operated as a 100% Central Sector/ Centrally Sponsored Scheme by the National Afforestation and Eco-Development Board at the  Ministry (NAEB), set up in 1992. By 2011, 743 forest development associations (FDAs), a federation of JFM committees at the forest division level, had been operationalised, to treat some 1.23 mha as on 19.11.2007 (Ministry website, http://www.archive.india.gov.in/sectors/environment/index.php?id=9)
A comprehensive ‘Mid-Term Evaluation’ (MTE) of the NAP by the ICFRE Dehradun submitted in 2008 (available at http://naeb.nic.in/MTE-Complete_Report.pdf) found that the physical achievements were satisfactory, and that the entry-point activities, such as water conservation measures, wells, common utility buildings like school, anganwadi, primary health centre, eco-tourism, NTFP management, etc. have been well received, in the forest-fringe Village Forest Committees (including Eco-Development Committees, EDCs, in wildlife areas). “The programme, by and large, has been successful in mobilizing people in 28181 villages in forests protection and development activities covering over ten million hectare forests. It has worked well towards deepening of democratic ethos and their institutionalization through FDA-JFMC mechanism” (MTE, p.ii). Thus the FDAs have played a “catalytic role in development of rural production systems through improved irrigation, soil and moisture conservation, value addition in non-timber foresdt produce collection and processing, and enhanced biomass production”, resulting in successful protection of about 10 mha forests from illicit grazing, fire, etc. that are now “regenerating with vigour”. On the down side, the report comments that the micro-planning has been mainly restricted to forest schemes (and not truly multi-sectoral), training is seen to be somewhat  ad-hoc, and there are other weaknesses in the process.  JFM committees, like any  “nascent” institution, have been helped by capacity building exercises to understand the scheme, but “functioning of forest committees remain still beyond the grasp of a majority of forest committee members and forest department in majority of cases”, and there does not seem to be any clear idea of what will happen after the funding ceases (lack of an “exit strategy”). As estimated by Dr.Devendra Pandey for the India- Forest Sector Report 2010 (ICFRE, 2012), a cumulative total amount of Rs.23370 million was released over 8 years of the NAP until 2009-10, achieving about 1.69 mha afforestation; out of this some 40 to 45% is under Assisted Natural Regeneration (ANR), and 35-40% under artificial regeneration and mixed plantation (other models include silvi-pasture development, bamboo and cane plantation, regeneration of herbs and shrubs, etc.). The revised 2009 guidelines (available at http://naeb.nic.in/NAP_revised%20Guidelines%20English.pdf) seek to address some of these issues.     

Criticism of the JFM approach

As with SF, the JFM programme has also attracted its share of the ire and disapproval of social environmentalists (for instance, Lele’s chapter is titled frankly “What is Wrong with Joint Forest Management?” in Lele & Menon, 2014; see also Lele, 2003). This is puzzling and disheartening to the forest department, which feels that the JFM/NAP has been a useful, and fairly successful, programme, and the improvement in forest cover after 1997 has been generally ascribed to the improved protection and fire prevention achieved by the VFCs. The disapproval seems generally to be based on the fact that the forest department still holds the reins, by monopolizing the Secretary post and controlling the bank accounts of the VFC, for example. Some observers also find that women’s interests are down-graded, as men prefer to go for cash returns from the timber harvest, and often put controls on collection of fuel and fodder, which is predominantly the women’s responsibility. Equity concerns are also pointed out, as landless families need income from collection, grazing, etc., which may be prohibited in the regenerating plots. These gender and equity effects are criticized as a flaw in the JFM set-up, which tends to favour landed, dominant sections of the village community.

However, foresters tend to discount such criticisms, on the ground that the VFC process also has a lot of support for livelihoods built in, such as capacity building and training for subsidiary occupations (both forest-based and otherwise), infrastructure building for processing and marketing (drying and threshing floors, work and storage sheds , transport, credit, minimum support price for certain products, etc.), especially where a project has more flexibility in the types of activities that can be funded. In the final analysis, the benefits of almost any rural programme tend to go disproportionately to the dominant elements (a feature already noted in the agriculture sector and the Community Development pragramme, by Myrdal, 1968, Vol.II; see pp.1344-45, 1367, for instance), but where support is given to activities not favoured by the better off (such as collection of low-valued forest products), the landless wage-earners are likely to be benefited.

Choice of Institutions: between community-based, state and panchayat

Social environmentalists, finally, demand the shift of VFCs from the control of the forest departments to the jurisdiction of the elected panchayats (or village general body, Gram Sabha). As explained by the author in his survey of VFCs and JFM in three states (Dilip Kumar, 2014), this antagonism to what are termed Community-Based Organisations (CBOs) outside the official panchayat raj institutions (PRI)system, is probably a creation of the social activists. The villagers themselves do not see any antagonism between CBOs and PRIs, as each has its role and status, and the CBO (VFC) is actually preferred by all the communities contacted in the above study. This is because the CBOs (such as the VFCs) are closer to the settlement or hamlet level of the community, where all the members are equal, and know each other and can take up joint activities, as posited by Ostrom (1990) and others. The village panchayats (the lowest rung of the PRIs) are much larger, are farther away from the village or hamlet, and are less responsive to the felt needs as they are meant to take up large infrastructure programmes of the state. In any case, the villagers like the sense of control they have in the CBO, and would like these to be independent of the PRIs so as to keep away the political divisions of the electoral process. Further it was commonly expressed that the two are not mutually incompatible, and can easily be reconciled by making the CBO based on the whole village general body (Gram Sabha), and designating it as a sub-committee of the PRI (se Dilip Kumar, 2014).




[1] (Operational Guidelines for the Tenth Five Year Plan, available at http://www.indiaenvironmentportal.org.in/files/NAEBwebst.pdf, and revised 2009 guidelines at http://naeb.nic.in/NAP_revised%20Guidelines%20English.pdf).


(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)

References


Dilip Kumar, P.J. 2014. Managing India’s Forests: Village Communities, Panchayati Raj Institutions and the State. Monograph No.32. Institute for Social and Economic Change, Bangalore. Available at http://www.academia.edu/9235210/Managing_India_s_Forests_Village_Communities_Panchayati_Raj_Institutions_and_the_State


Government of India. 1988. National Forest Policy. Resolution  No.3-1/86-FP dated 7 Dec 1988, Ministry of Environment  and Forests, New Delhi. Available at the ministry website, http://www.moef.gov.in/sites/default/files/introduction-nfp.pdf

ICFRE. 2008. Mid-Term Evaluation of the National Afforestation Programme. Published by the Indian Council of Forestry Research and Education, Dehradun, on behalf of Ministry of Environment  and Forests, Government of India , New Delhi. Available at  http://naeb.nic.in/MTE-Complete_Report.pdf

ICFRE. 2012. Forest Sector Report India -2010. (Lead author Devendra Pandey). Published by the Indian Council of Forestry Research and Education, Dehradun, on behalf of Ministry of Environment  and Forests, Government of India , New Delhi. Available at http://www.icfre.org/FSRI-REPORT_English.pdf

Lele, Sharachchandra. 2003. Participatory Forest management in Karnataka: At the Crossroads. Community Forestry, Vol.2, Issue 4, May 2003, p.4-11. Available at: http://www.ces.iisc.ernet.in/biodiversity/sahyadri_enews/newsletter/issue21/pdfs/PFM%20in%20Karnataka.pdf

Lele, Sharachchandra and Ajit Menon. 2014. Democratizing Forest Governance in India. Oxford University Press, New Delhi.

Myrdal, Gunnar. 1968. Asian Drama. An Inquiry Into the Poverty of Nations. Twentieth Century Fund, inc. Reprinted in India 1982, 2004, Kalyani Publishers, New Delhi.

NAEB. 2008. Mid term Evaluation of the National Afforestation Programme (NAP) schemes implemented through Forest Development Agencies (FDAs). Final report submitted by Directorate of Extension, ICFRE Dehradun to the National Afforestation and Eco-Development Board, Ministry of Environment & Forests, New Delhi. Available at naeb.nic.in/MTE-Complete_Report.pdf

NAEB. 2009. National Afforestation Programme Revised Operational Guidelines – 2009. National Afforestation and Eco-Development Board, Ministry of Environment & Forests, New Delhi. Available at http://naeb.nic.in/NAP_revised%20Guidelines%20English.pdf

NCA. 1976. Report of the National Commission on Agriculture. Part IX, Forestry. National Commission on Agriculture. Ministry of Agriculture and Irrigation, Government of India, New Delhi. (Available at http://krishikosh.egranth.ac.in/bitstream/1/2041449/1/CCS323.pdf)

Ostrom, Elinor. 1990. Governing the Commons. The evolution of institutions for collective action. Cambridge Universities Press, Cambridge.

Saxena, N.C. 1997. The Saga of Participatory Forest Management in India. CIFOR Special Publication. Center for International Forestry Research, Indonesia. Available at www.cifor.org/publications/pdf_files/Books/SP-Saga.pdf


Tuesday, January 26, 2016

31 Forest policy and the integrated approach. Forest Landscape Restoration in India -II.

Background of Empire forestry in India

India has had no less than three comprehensive statements of forest policy, the first as early as 1894 under the British Raj. The foundation of organized or ‘scientific’ forestry  in India is often ascribed to the Memorandum of 3rd August 1855, issued by Lord Dalhousie, the then Governor-General of India (FRI,  1961, Vol.II, p.63), which Stebbing (1922, Vol.I, p.206) termed the “Charter of the Indian Forests”.  The forests of the sub-continent had been depleted in the preceding decades by two forces: one, the prior practice of relatively unregulated timber ‘mining’ by contractors (both British and native), and then other, the frequent slashing and burning for expanding cultivation. Dalhousie’s memorandum laid the basis of scientific forestry, by enunciating the principle that valuable forests should be worked, not to swell the profits of traders, but to maximize their value to the state in conformity with their “future proper  maintenance” (Stebbing, op. cit., p.207). Stebbing states that “Lord Dalhousies’s pronouncement was the act of a far-sighted statesman and proved him to be a man far ahead of his times”. It was Dr.Dietrich Brandis, who started as the Superintendent of Forests in Pegu in 1856, who subsequently worked tirelessly to establish scientific forestry in India, earning him the name of the “Father of Indian Forestry”, endowed as he was with “both the requisite scientific forestry knowledge, fitness of character and the equally  necessary tact to carry through the policy determined upon in the face of the most strenuous opposition” (ibid.).



(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)

This ‘scientific’ forestry has been reviled by social environmentalists and environmentalist  historians  as an exercise of naked imperial avarice and high-handedness that dispossessed the people of the sub-continent of their rightful habitats and their traditional rights (for a recent adumberation, see Lele & Menon, 2014). However, a less adversarial assessment  would be that the colonial foresters and administrators were actually trying to preserve the existing large forest belts (specially in the higher altitudes and upper river catchments), for what we now term environmental and ecological values (see Barton, 2002), while the intermediate belt of high timber value would be worked on sustained yield basis for commercial timber and other products (including non-timber products like oleo-resins and pitch, gums and tannins, medicines etc. which were significant commercial products). At the same time, it is not as if the colonial forest conservators like Brandis and others were completely oblivious of the great dependence of the population on the common lands and community forest for a myriad of products and services. In his Report on the Improvement of Indian Agriculture, Voelcker (1893) drew a number of conclusions on the interdependence of the agricultural economy and livelihoods to the state of the forests and supply of forest products. For instance, because farm-yard manure (cattle dung) was so important to maintain soil fertility, he urged that government should help in supplying fuelwood so that the manure need not be burnt, through the development of “Fuel and Fodder reserves” for the rural population, even if it proved to not financially profitable, in the greater interests of the rural population (Voelcker, op. cit., p.xi). In his chapter on the forests,  Voelcker recognizes that the initial mandate to the forest department had been to make the working of the forests more sustainable financially, but because of the expansion of cultivation closer to the forest borders and increase in population and the needs of the people, it “has become necessary to extend the benefits of forests, so that they may more directly serve the interests of agriculture” (p.xii).  Voelcker also suggests “the increase of plantations along canal banks and railway lines”, “the further encouragement of arboriculture”, the carrying out of an enquiry into “the needs of different cultivating districts in the matter of wood supply”, and the setting aside of a portion of the forest revenue for “the extension of ‘reserves’ to meet agricultural wants” (p.xiii). In his Chapter IX on “Grass”,  he maintains that “the provision of grazing in forests is a desirable and legitimate object”, and in times of drought it may even become “invaluable in keeping the cattle of the country alive” (p.xiii). He again stresses the importance of raising fodder in the fuel and fodder reserves, and in the Chapter X on “Fodder-crops and Hedges”, he advocates the growing of fodder and hedges on farms (p.xiv). As is apparent, these ideas not only foreshadow the concepts of social forestry and agroforestry that  were developed in detail in the 1970s following the National Commission of Agriculture (Government of India, 1976), but also imply an integrated, multi-stakeholder approach that took the whole gamut of land use and livelihood practices and patterns for its field of action.

Brandis himself was a strong proponent of the desirability of community control of such local resources. Although, based on the experience of different states in Europe, he felt that handing over full control to private entities would end up in sale of forest, he also expresses the highest concern for the need to respect the customary rights of the people, which calls for “much care, patience, and conciliatory treatment of the people concerned”, and definitely not to treat the clearing and burning of forests by the native communities as a grave offence, as “…the tribes of India have the same claim as the holder of prescriptive forest rights in Europe to demand that provision be made for their reasonable wants and requirements”. Brandis had the vision that once the forests had been restored to a productive state, the village communities would be in a position to take responsibility for their future conservation and management as fuel and fodder reserves (Brandis, 1897, repr. 1994).

Forest Policy Resolution, 1894 of colonial government

Based on Voelcker’s report and the considerations outlined in the government memoranda, the Government of India issued the first Forest Policy resolution dated 19 October 1894 (available as an Appendix in 100 Years of Indian Forestry, FRI, 1961, Vol.I). The underlying principle is that the state forests are to be administered “in the public benefit”, which may be in some cases the whole body of tax-payers, but in others “the people of the tract within which the forest is situated”. Regulation and restriction of rights and privileges may be necessary to safeguard the forest, but are justified “only when the advantage to be gained by the public is great”; and must be done only to the absolutely minimum degree. The state forests are broadly classified under four headings: (a) Forests to be preserved on climatic or physical grounds (hill slopes, hill torrents, etc.), (b) Forests for valuable timbers for commercial purposes, (c) Minor Forests, (d) Pasture lands. It is not intended that existing state forests should each be assigned these classes; they are only “to afford a basis for the indication of the broad policy” to be applied, and always with “the fullest consideration … given to local circumstances”.  

One of the implications of making the interests of sustainable agriculture and livelihoods paramount is that “wherever an effective demand for culturable land exists and can only be supplied from forest area, the land should ordinarily be relinquished without hesitation” (subject to certain precautions e.g. avoiding the honey-combing of the forest etc.). Therefore, the local governments were given the discretion to divert forest land to agricultural purposes without previous reference to the Government of India, a position that was reversed only in 1980 with the passing of the Forest (Conservation) Act.

Protection and management of the minor forests and fuel and fodder reserves are to be done with full consideration of the local needs and traditional practices, and not to generate profit for the state and even though scientific principles may demand strict control. “The customs of generations alter slowly in India; and though much may and should be done to lead people to their own profit, yet it must be done gently and gradually – always remembering that their contentment is no less important an object than is their material advantage”.

It can thus be seen that the colonial policy on forests and village commons was, at least conceptually, a fairly ‘integrated’ one that sought to keep a balance between the needs of the rural and urban populations as well as the interests of what we would term today the environmental and ecological health of the region. On the one hand, therefore, the colonial administration proceeded with diligence in notifying the better forest tracts and settling the rights and privileges of the communities, while on the other, the expansion of settled agriculture was encouraged following on the establishment of ‘Pax Britannica’ in tracts hitherto subject to the vagaries of fickle nature and the  depredations of wild animals – and of lawless humans (see Tucker & Richards, 1983, for an account of nineteenth-century deforestation and expansion of settled agriculture).

National Forest Policy, 1952 of independent India

If we fast-forward to the post-independence era, it appeared to the policy-makers that the country had probably taken the priority of agriculture to unreasonable extents, and a corrective was seen to be required if the remaining forest areas were to be safeguarded for posterity. Thus the National Forest Policy of 12 May, 1952 (Government of India, 1952; available as Appendix III in the publication 100 Years of Indian Forestry, FRI, 1961) called for a “re-orientation” of the forest policy in the light of the changes since the colonial era, the better understanding of “the part played by forests in maintaining the physical conditions of the country”, and the realization of the “unsuspected dependence of defence on the forests” during the World Wars. The National Forest Policy was based on the following paramount needs of the country: (1) the need for balanced and complementary (and the most appropriate) land-use, (2) the need for checking denudation, soil erosion, invasion of sand dunes on the coast and desert regions, (3) the need for establishing treelands wherever possible, for amelioration of climatic conditions and general well-being, (4) the need for increasing supply of grazing, small wood, firewood etc., (5) the need for sustained supply of timber and other forest produce for defence, communications and industry, and (6) the need for the realization of the maximum annual revenue in perpetuity consistent with the fulfillment of the needs enumerated above. The following functional classification of forests was proposed: (A) Protection forests, which “must be preserved or created for physical and climatic considerations”, (B)  National forests, to meet the needs of “defence, communications, industry and other general purposes of public importance”, (C) Village forests, to provide fuelwood, small timber, fodder, grazing, etc. for local requirements, and (D) Tree-lands, “outside the scope of the ordinary forest management”, but “essential for the amelioration of the physical conditions of the country”.  All the forests, “irrespective of their functions and ownership”, should be administered “from the point of view of national well-being”; hence the claim of local communities, and the interests of agricultural requirements, must necessarily take a second place to the national interests. Thus the first national forest policy of independent India is seen to have rejected some of the basic premises of the previous (colonial) forest policy. According to the  1952 policy:

 “The accident of a village being  situated close to a forest does not prejudice the right of the country as a whole to receive the benefits of a national asset. The scientific conservation of a forest inevitably involves the regulation of rights and the restriction of the privileges of user…however irksome such restraint may be to the neighbouring areas”.  

Again, local needs should be met to a reasonable extent, but not at the cost of national interests. The old policy of liberal relinquishing of forest lands for agricultural purposes,  although subject to certain safeguards that unfortunately have been “honoured only in their breach”, should be given up. Each land parcel should be put to the appropriate land use “under which it would produce the most and deteriorate least”. The forest vegetation on vulnerable tracts like mountain and hill slopes, river valleys and river banks, catchment areas,  coastal areas, desert areas, etc. needs to be restored “by establishing protective forests over larger areas, and preserving the existing ones”.  Village forests should be managed in a sustainable manner for local needs, but not for commercial returns. This will require the imposition of controls, which “render the entrusting of the management of village forests to panchayats, without appropriate safeguards, a hazardous undertaking as has been demonstrated in some of the States” (probably pointing to the experience in Tamil Nadu, where the panchayats had found themselves unable to safeguard the village wood lots raised under forestry schemes).  There is “vast scope for an all-round increase in the area under treelands”,  on agricultural land, institutional and departmental lands,  etc. outside the conventional forests, and a systematic programme for this should be drawn up for raising nurseries, raising public awareness, etc. Free grazing (especially of sheep and goats) should be curtailed where it is damaging the vegetation. Shifting cultivation, which damages the forest over wide tracts, should be gradually reduced, but by “persuasion, not coercion; a missionary, not an authoritarian, approach”.

National Commission on Agriculture, 1976

The 1952 forest policy thus aimed at maximizing the value of the forest resource, and consolidating the forest estate, a response to the free-handed conversion of forest to cropland in the early decades of independent India. This techno-centric and national-economic orientation was further strengthened by the report of the National Commission on Agriculture (NCA, 1976), the main points of which are summarized below. One of the issues that seems to have deeply impressed the NCA is that with a forest estate of almost half the cultivated area, the contribution of forestry and logging to the NDP was only some 1.5% (1972-73), which obviously weakens the case for retaining land under the forest department. The resolution of this conundrum is seen in working toward the general increase in productivity and economic returns (per hectare per year), which would call for, and also attract, higher investment from commercial banks, overseas development agencies, and the corporate sector. But to achieve this higher productivity and economic returns, the forests would have to be put under “scientific management on modern lines” (op. cit., p.20), which meant that the existing low-valued, mixed growth of all sorts of low-valued miscellaneous trees and scrub ought to be replaced by the most efficient, fast-growing, species, implying the testing and adaptation of exotics that had been proven in similar ecological conditions elsewhere in the world (like the poplars, Australian eucalypts, acacias, sub-tropical and tropical conifers like the pines and Cryptomeria species for the hill regions). At the same time, free supply of forest produce to all and sundry was resulting in a feeling that the forests were of no value and could be treated in a cavalier fashion:

“There are a lot of subsidised supply of timber and forest materials to the rural population. From this an attitude has developed that forest material can be given to others without going too much into the economics of production… In the name of encouragement to industry, forest material has been leased out for longer period at a very nominal rate of royalty… If the forests are bled both by the rural sector and industrial sector, there will be no incentive or initiative left to change over from the present low-cost low-yield forestry to a commercial high investment economic forestry development” (NCA, 1976, Part IX: p.3-4).

The recipe, then, was to convert the mixed low-value jungles into highly productive plantations yielding industrial material that would be sold at fair prices (for which forest development corporations were to be set up to attract institutional finance), while local needs like fuel, fodder, artisanal raw materials, etc. would have to be met from farm forestry or social forestry, and from improved degraded forests in the rural areas (using development funds and foreign aid agencies’ support). “Production of industrial wood would have to be the raison d’etre for the existence of forests” (NCA, Part IX:p.32-33). Development of minor forest products through state agencies for collection, marketing, etc. was expected to assure employment and a reasonable minimum wage to tribals and others dependent on this activity (p.34). The detailed recommendations were set out in the NCA’s two “Interim reports”: one on Production Forestry – Man-made Forests, and the other on Social Forestry (NCA, Part IX:p.22).

A mention may be made of the NCA’s approach to the interrelations of forest economy with the rural and tribal economy. Apparently the Commission saw employment (wage labour) as a main avenue for involving the local people and lessening their pressure on the forests: “Employment could be offered as an alternative to rights of user, if forest development is properly organized” (NCA, IX:p.22). The rural labour could also be engaged in increasing the production as well as improving collection and processing of minor forest produce  for maximizing its contribution to rural employment. However, the forests under use by communities have deteriorated mainly because of their over-exploitation, so ‘they cannot in all fairness expect that somebody else will take the trouble of providing them with forest produce free of charge” (p.25).  However, the NCA also stated that “growth should lead to social justice…the increased yields of forest products will have to be equitably distributed between industrial needs and the demands of the rural population” (p.34) and so on.

The 1952 forest policy and the NCA report of 1976 gave a fillip to forest development on a large scale in India. The achievements are impressive (and condemnable in the view of environmentalists) in terms of conversion of natural forest into monocultures of industrial wood using mainly exotics like eucalypts and acacias, as well as, complementarily, a huge programme of social and farm forestry in the countryside. This  is, in a manner of speaking, an integrated approach, approximated by the term “high modernising” (Scott, 1999): it seeks to take care of diverse, competing needs, but at a macro-, national policy-making level. In doing so, it tends to ignore the specifics of the relationship of local communities with the habitat and its resources. The high-modernist approach tends to abstract use of resources to the level of the broader national economy, and claims to maximize the benefits to the wider economy. Under this model, benefits would have to circulate back to the community not directly as extractors, but by way of their participation in that economy, either as processers or wage-earners etc.

Unfortunately, the local community is often unable to participate in the wider economy because of various reasons: lack of education and awareness, centuries of discrimination by the caste or class system, remoteness and lack of communications and infrastructure, lack of credit  and marketing facilities, and so on. This could well be the crucial difference in the landscape approach that we are discussing now: it has to be at the level of the local community, taking into account the actual specifics of their interrelationships, rather than leaving it to the broader economy and markets to sort out their issues. At the other extreme, the village common lands, with no caretaker institution, were left to a process of local appropriation which rendered them “unable to meet local demands for fodder and fuel, leaving the villagers with no other recourse, but to turn to the Forests which increased pressure on them” (Saxena, 1997, p.13).

Ironically, even as the state was developing this ‘high-modernistic’ approach in accordance with the National Commission on Agriculture, other currents were already starting to move in the ‘political economy’ of the forest  that would in time result in the almost complete reversal of that policy and the proclamation of a revised forest policy of 1988, and the formalization of a revolutionary new phase of Joint Forest Management (JFM) for the degraded notified forests of India. Thanks to the activism of a group of social environmentalists, who came to examining the forest sector fairly late in the game according to Guha (2012), the direct relationship of the local communities was legalized in the Scheduled Tribes and Other Forest Dwellers Recognition of Forest Right (ROFR) Act, 2006, which vested considerable rights (and duties) in the Gram Sabha or village assembly in replacement of the formal forest department in the traditional habitat of the communities.

Revised National Forest Policy of 1988

The Revised Forest Policy of 1988 (Government of India, 1988) derives the need for a new policy statement from the “serious depletion” suffered over the ensued years, the “relentless pressures arising from ever-increasing demand for fuelwood, fodder and timber”, “inadequacy of protection measures”, “diversion of forest lands… without ensuring compensatory afforestation and essential environmental safeguards”, and “the tendency to look upon forests as revenue earning resource”. The statement of “Basic Objectives” in Section 2 also seems to indicate the hierarchy of priorities given to different objectives: it starts with “maintenance of environmental stability” and “ecological balance”, “conserving the natural heritage”, controlling erosion, sand dunes spread, etc.; then “increasing substantially the forest/tree cover… through massive afforestation and social forestry”, “meeting the requirements of fuelwood, fodder” etc.; and finally, “increasing the productivity of forests to meet essential national needs”, “encouraging efficient  utilization… and maximizing substitution of wood”.  A final objective is listed: “Creating a massive people’s movement with the involvement of women, to achieve these objectives and to minimize pressure on existing forests”. However, an overall caveat is given that the principal aim is “to ensure environmental stability … ecological balance… including atmospheric equilibrium”, etc., and that “derivation of direct economic benefit must be subordinated to this principal aim”.

Perhaps the most telling feature of this revised policy is the total reversal of the strategic role between reserved forests and social forestry: now the “domestic requirements of fuelwood, fodder, minor forest produce and construction timber” of the “tribals and other poor living within and near forests” should be “the first charge on forest produce”. Use of industrial wood needs to be reduced by substitutes, while as far as possible, forest-based industry “should raise the raw material needed… preferably by establishment of a direct relationship between the factory and the individuals who can grow the raw materials…”. Farmers would be encouraged to grow industrial wood, on marginal lands not required for cultivation or pasture purposes, and forest department/ corporations likewise on “degraded forests, not earmarked for natural regeneration”.  The practice of supplying forest produce to industry at concessional prices should cease, encouraging the industry to use substitutes, and import of wood and wood products should be liberalized. In essence, then, this has been interpreted as down-playing the commercial harvests from the state forests (fresh clear-felling and conversion of natural forest is precluded, so only the already existing plantation working circle areas are being harvested and replanted in rotation), while industrial raw material comes predominantly from trees outside forest (TOF). The policy also gives highest importance to supporting the tribal people and involving them closely in the protection and development of forests, safeguarding their customary rights and interests, “undertaking integrated area development programmes… including the provision of alternative sources of domestic energy”, etc.

However, this does not mean that the revised policy has no place for attention to the state forests beyond use for “subsistence and consumption” (Saxena, 1997, p.34) of local poor. The aim of achieving one-third of the total land area under forest or tree cover is reiterated. A massive programme of tree growing on all degraded and denuded land, both forest and non-forest, is urged, along with modification of laws and rights to encourage community afforestation, social forestry, farm forestry etc. Projects that interfere with forests on hill slopes etc. should be “severely restricted”. To met the “growing needs for essential goods and services which the forests provide”, it is “necessary to enhance forest cover and productivity” through “application of scientific and technical inputs”, however, without resorting to “clear-felling of adequately stocked natural forest”, nor through introduction of exotic species, “unless long-term scientific trial undertaken by specialists in ecology, forestry and agriculture have established that they are suitable and have no adverse impact on native vegetation and environment”. Shifting cultivation should be contained within areas already affected, “and area already damaged by such cultivation should be rehabilitated through social forestry and energy plantations”. There should be “no regularization of existing encroachments”, fire should be controlled, and grazing regulated.     

Antecedents in Indian experience with ‘integrated’ approach


A plethora of schemes, programmes, and projects have been pursued in India that go under the general rubric of ‘integrated’ approaches, a precursor to the landscape approach. The earliest was probably the Community Development Programme immediately after independence, which however was faulted on the grounds that works were decided by officials, and not in consonance with people’s felt needs. This prompted the move to set up local representative governance structures (panchayati raj institutions, PRIs) as discussed in the author’s monograph on village communities and forest conservation (Dilip Kumar, 2014). Other integrated projects and schemes include the Integrated Tribal Development Projects, Watershed Development Programme, Integrated Rural Development Programme, and others. Each of these has thrown up valuable learnings regarding many issues: the role and method of genuinely bottom up planning, empowering communities, addressing issues of gender and equity, mechanisms of consultation, planning and implementation, and so on. Space precludes a detailed consideration of these, unfortunately, so this paper goes on to consider only three major programmes in the forest sector: the Social Forestry/Farm Forestry programmes of the 1970s to the 1980s, the Joint Forest Management (JFM) framework adopted in the National Afforestation Programme (NAP) and in most ongoing externally aided projects from the 1990s, and the Western Ghats Forestry Project (WGFP) in Karnataka during the 1990s.

(A pdf file of the entire article is available at https://www.academia.edu/21490696/Forest_Landscape_Restoration_in_India_Antecedents_experience_and_prognoses)

References

Barton, Gregory Allen. 2002. Empire Forestry and the Origins of Environmentalism. Cambridge University Press, Cambridge.

Brandis, Dietrich. 1897. Forestry in India. Origins and Early Developments. Reprinted 1994 by Natraj Publishers, Dehradun. 

Dilip Kumar, P.J. 2014. Managing India’s Forests: Village Communities, Panchayati Raj Institutions and the State. Monograph No.32. Institute for Social and Economic Change, Bangalore. Available at http://www.academia.edu/9235210/Managing_India_s_Forests_Village_Communities_Panchayati_Raj_Institutions_and_the_State

FRI. 1961. One Hundred Years of Indian Forestry, Vol. I and II. Forest Research Institute, Dehradun, India.

Government of India. 1894. Resolution No.22.F dated 19th October, 1894. (Available as Appendix IV, The Old Forest Policy,  in the publication 100 Years of Indian Forestry, FRI, 1961).

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Government of India. 1976. Report of the National Commission on Agriculture. Part IX, Forestry. Ministry of Agriculture and Irrigation. New Delhi. Available at http://krishikosh.egranth.ac.in/bitstream/1/2041449/1/CCS323.pdf

Government of India. 1988. National Forest Policy. Resolution  No.3-1/86-FP dated 7 Dec 1988, Ministry of Environment  and Forests, New Delhi. Available at the ministry website, http://www.moef.gov.in/sites/default/files/introduction-nfp.pdf

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Lele, Sharachchandra and Ajit Menon. 2014. Democratizing Forest Governance in India. Oxford University Press, New Delhi.

NCA. 1976. Report of the National Commission on Agriculture. Part IX, Forestry. National Commission on Agriculture. Ministry of Agriculture and Irrigation, Government of India, New Delhi. (Available at http://krishikosh.egranth.ac.in/bitstream/1/2041449/1/CCS323.pdf)

Saxena, N.C. 1997. The Saga of Participatory Forest Management in India. CIFOR Special Publication. Center for International Forestry Research, Indonesia. Available at www.cifor.org/publications/pdf_files/Books/SP-Saga.pdf

Scott, James C. 1999.Seeing Like a State. How Certain Schemes to Improve the Human Condition Have Failed. Yale University Press.

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