Long-Term Tracking of Multiple Beneﬁts of Participatory Forest Restoration in Marginal Cultural Landscapes in Himalaya (SITR6-4)

23.04.2021

SUBMITTING ORGANIZATION

Jawaharlal Nehru University, School of Environmental Science

DATE OF SUBMISSION

23/04/2021

REGION

Asia

COUNTRY

India

KEYWORDS

Bamboo · Biodiversity · Carbon stock · Medicinal plants · Farm · Integrated landscape management · Livelihood · Multipurpose trees · Payments for ecosystem services · Temperate

AUTHOR(S)

Krishna G. Saxena, Kottapalli S. Rao, and Rakesh K. Maikhuri

K. G. Saxena
School of Environmental Sciences, Jawaharlal Nehru University, New Delhi, India

K. S. Rao
Department of Botany, Delhi University, Delhi, India

R. K. Maikhuri
Department of Environmental Sciences, HNB Garhwal University (Central University), Srinagar, India

LINK

Satoyama Initiative Thematic Review Vol.6 (SITR-6)

Abstract

The literature is abound with references to the potential of indigenous and local knowledge (ILK) for sustainable landscape management, but empirical on-the- ground efforts that demonstrate this potential are still lacking. To identify interventions for improving the effectiveness and efﬁciency of forest restoration, participatory trials were set out in the Indian Himalaya, where per capita degraded land far exceeds per capita cropped/healthy forest land. Treatments were designed based on pooled indigenous and scientiﬁc knowledge taking into account farm-forest-livelihood interactions in cultural landscapes. The multipurpose tree-bamboo-medicinal herb mixed restoration plantation reached a state of economic beneﬁt/cost ratio >1 in the eighth year and recovered 30–50% of ﬂowering plant species and carbon stock in intact forest. The communities maintained but did not expand restoration in the absence of policies addressing their genuine needs and aspirations. Transformative change for sustainable restoration would include (1) nesting restoration in participatory, long-term, adaptive and integrated landscape development programmes, (2) formally involving communities in planning, monitoring, bioprospecting, and ﬁnancial management, (3) assuring long-term funding but limited to the inputs unaffordable for local people, (4) stimulating the inquisitive minds of local people by enriching ILK and cultural heritage, (5) convincing policymakers to provide the scientiﬁc rationale behind policy stands, to support the regular interactions of communities with researchers, traders, and industrialists, to commit to genuine payment for ecosystem services in unambiguous terms at multiple spatial (household, village and village cluster) and temporal (short, medium and long-term) scales, and to support long-term participatory action research for development of “landscape restoration models” in varied socio-ecological scenarios.

1. Introduction

Ecological restoration became a global priority at the turn of the twenty-ﬁrst century, with the Convention on Biological Diversity aiming to restore at least 15% of degraded ecosystems by 2020, the Bonn Challenge to bring 350 million hectares of degraded and deforested land into restoration by 2030, and the United Nations declaring 2021–2030 as the Decade on Ecosystem Restoration. The envisaged targets can be achieved only through transformative change in current restoration approaches (IPBES 2019). A realisation of the key role of socio-economic and institutional factors in sustainable restoration (Chazdon et al. 2016; Reed et al. 2016) paved the way for community-centred forest landscape restoration and forest management (Baynes et al. 2015). Lately, the potential of indigenous and local knowledge (ILK) in overcoming technical barriers to restoration has also been recognised (Reyes-Garcia et al. 2019). Nonetheless, empirical efforts demonstrating this potential are rare (He et al. 2009; Stanturf et al. 2014). Forest restoration has been attempted largely through sponsored projects (Le et al. 2012; Burton 2014) and sustainability after cessation of funding has rarely been assessed (Rudel et al. 2005; Chazdon et al. 2016; Reed et al. 2016).

Himalaya is a biodiversity hotspot facing the entwined challenges of enhancement of livelihoods and environmental conservation. Forest restoration is a win-win option for conserving biodiversity, mitigating climate change and enhancing livelihoods (Brandt et al. 2017; Forest Survey of India 2019). We elaborate herein on the transformative change needed for sustainable forest restoration based on a participatory trial in a temperate socio-ecological production landscape.

2 Materials and Methods

2.1 Study Area

At the time of initiation of the study in 1991, Khaljhuni was a typical marginal, un-electriﬁed village of the moist temperate region around the Nanda Devi Bio- sphere Reserve, a UNESCO World Heritage Site. The village territory comprised 68 hectares of terraced private farms and 436 hectares of community forests (Fig. 4.1 and Table 4.1).

Fig. 4.1 Village of Khaljhuni in Central Himalayan Region of India

Table 4.1 Basic information of the study area

Cultural heritage concerning the treatment of agricultural abandonment and purchase of foodgrains, as well as hiring of labour, from outside the village as evil omens, had checked agricultural expansion and strengthened social bonding at the time of the trial’s initiation in 1991. Around 305 hectares of forest were intact and 131 hectares were severely degraded. The degraded forests were nearer to the dwellings than the intact forests. Degradation occurred because of lack of restoration after logging in 1910 by the Forest Department of the colonial government. The Department had created community forests to alleviate people’s resentment against its disregard for their well-being and cultural heritage, which viewed logging as a bad omen, and had sanctioned income from wild non-timber forest products only to small farm holders, allowing only collection of edible/medicinal products from forests which checked storm ﬂows and recharged springs. Conﬁnement of ILK to passive forest restoration and prohibition of developing tree-crop mixed systems on forest land led the community to restore traditional practices in the intact forest and to use logged areas as free pasture, driving them to a severely degraded state.

2.2 Participatory Community Forest Restoration Trial

People’s expectations and underpinning reasons for being against forest restoration were discerned from participatory discussions. People desired early and high income by growing medicinal herbs and understory bamboo. They dismissed the planting of trees due to long waiting periods for production of non-timber commodities, cultural restraints on income from timber, as well as hesitated to make cash or labour contributions to establish practices with uncertain returns. They seemed willing to reciprocate support for restoration addressing their expectations by (1) free sharing of ILK, deploying surplus physical resources and social capital, and maintaining/ expanding the trial once it reached a state of economic beneﬁt/cost ratio of >1, and (2) accommodating the concerns of other stakeholders. They knew gregarious ﬂowering induced mass mortality of bamboo but reconciled it with high productivity.

People gave up their initial reservations on planting trees after learning from participatory discussions that: (1) scientiﬁc knowledge lacked tested methods of cultivation of medicinal herbs/understory bamboo, (2) some multipurpose trees valued by them were likely to facilitate them, (3) organic branding of walnut/ honey will fetch premium prices, (4) payments for carbon sequestration were quite likely in near future, and (5) availability of tree products close to dwellings would save time/labour spent on collection from distant forests and would unleash opportunities for raising crop yields by eliminating tree-crop interferences. Ultimately, the community decided to establish a mixed plantation of trees, viz. Aesculus indica (horse chestnut), Quercus leucotrichophora (oak) and Juglans regia (walnut), a short bamboo (Thamnocalamus spathiﬂorus), and medicinal herbs viz. Aconitum heterophyllum, Angelica glauca, Picrorhiza kurroa and Rheum australe in an eight- hectare plot and maintain/expand it once economic outputs exceeded input costs. Financial support was terminated 7 years after planting when economic beneﬁt/cost ratio crossed the mark of one (Rao et al. 1999), while participatory discussions and monitoring of the restored forest and competing land uses/economic activities continued.

2.3 Data Collection

Density of surviving plants, height/girth growth of trees/bamboo, biomass, soil carbon stocks and material inputs/outputs were measured after 1, 7, 10, and 20 years in the trial area and also in agricultural land, intact forests and degraded forests outside the trial area. All households were surveyed to assess changes in human/livestock population, land use-land cover, harvests and income. People’s perceptions about the present trial and conservation development policies were ascertained from open-ended discussions, and researchers’ deductions were informed in traditional open village assemblies in accordance with traditional norms (Rao et al. 1999; Maikhuri et al. 2000; Semwal et al. 2013).

3 Results

3.1 On-Site Outcomes and Impacts

3.1.1 Unanticipated Problems and Responses

Bamboo suffered gregarious ﬂowering-induced mass mortality in the tenth year (2 years after cessation of funding) when it was at peak growth (80% of above- ground biomass). Economic loss from bamboo was far less than the gain from walnut, which coincidently started fruiting in the same year. At this time, people also felt a threefold increase in crop/beehive damage from bears and porcupines. People viewed this problem as a combined outcome of the decline in traditional collective mechanisms for dispelling harmful wildlife, facilitation of wildlife movement by bridges constructed over rivers/streams with road expansion, the wildlife sink function of the restored forest, and the focus on charismatic top carnivores (leopards/tigers) and their preferred ungulate preys in protected area management. Further, they envisioned that factors increasing pressure on intact forest (population growth, lack of cost-effective alternatives to timber/wood used for warmth, and cultural obligations of sharing resources with neighbouring communities that have lost their forests due to common amenities like electricity/road) would outweigh the ones decreasing pressure (access to subsidised cooking gas, modern medicine, vermicompost, subsidised food grains, and wage employment) in the near future. Comprehending their ILK, people transplanted wild saplings of Alnus nepalensis (Nepalese alder) in gaps for its fast growth in exposed nutrient poor soils, negative association with wildlife and timber value. This species was excluded in the initial planting when wildlife intrusion was limited, insect pests thriving on it threatened crops that met local food needs in the absence of external food supply, and there was yet a lack of envisioning of timber scarcity in future.

3.1.2 Species Selection, Performance and Ecological Recovery

People’s selection of species was guided solely by direct economic beneﬁts in the initial treatment and by both direct and indirect beneﬁts in gap ﬁlling. Coincidently, species chosen for economic beneﬁts were diverged in respect to leaf dynamics, nutrient requirements, shade tolerance and rooting patterns. ILK about fast growth of bamboo and alder in open habitats turned out to be true, though it altogether lacked underlying biological mechanisms. Naturally regenerated species shared just six percent of above-ground biomass after 20 years.

The rate of economic returns from the 20-year-old restored forest was higher than both the intact forest and cropland. On the other hand, the intact forest had better structure (canopy density, vertical stratiﬁcation, and basal area) and higher regulating (carbon stock) and supporting (plant biodiversity) ecosystem services than the restored forest. Restoration over 20 years resulted in recovery of hardly 50% of ﬂowering plant species and carbon stock in the intact forest. Species of high conservation value, the transplanted medicinal herbs, were altogether absent in cropland and untreated degraded forest (Table 4.2).

Time scale and accounting of biomass removals, below-ground organs and soil were signiﬁcant determinants of carbon sequestration rate (Table 4.3).

Table 4.2 Economic returns, vegetation structure, plant species richness and carbon stock in restored forests after 20 years, and other land uses (intact forest, degraded forest, cropland, and abandoned cropland) in the Khaljhuni socio-ecological production landscape

Table 4.3 Changes in carbon sequestration rates with progression of participatory forest restora tion trial in village Khaljhuni, Central Himalaya, India

3.2 Off-Site Impacts and Outcomes

There were two off-site impacts of the trial. First, three farmers started cultivating medicinal herbs on their private farms, which was boosted by ﬁnancial support from National Medicinal Plants Board set up in 2000. The majority attributed non-adoption of this innovation to their exclusion from the scheme and hurdles in marketing. Secondly, 23 families leased out abandoned farms to a pharmaceutical company in 2005 for an annual income of Rs. 5000 ha^-1 from the lease fee for 30 years. The company planted yew (Taxus baccata), which people used for preparing a health drink and for making the mainframes of houses. Extraction of the anti-carcinogenic drug paclitaxel (Taxol) by the company was outside the ILK domain. With the passage of time, people realised that the income from leasing was at the expense of land degradation (in the absence of manuring and weeding as yew was a stress tolerant species), their economic exploitation (rent being a fraction of the income to the company from Taxol), stagnation of ILK (exclusion of people from industrial processing), weakening of social bonding (the company negotiated with individuals) and illicit harvests from state forests at the company’s behest. This realisation, a spin-off beneﬁt from consistent monitoring, introspection, contemplation, social learning and adaptive responses learnt from the trial, led to a collective decision to defer new lease proposals. Further, conjecturing ILK as the foundation of Taxol discovery, people envisioned development of new commercial products from horse chestnut seeds and Prinsepia utilis/Neolitsea pallens seeds, used when crops failed as a staple food and an edible oil source, respectively, and from Juglans regia, used in healthcare/dyeing/pest control.

3.3 Khaljhuni Cultural Landscape Over the 1991–2011 Period

Abandonment of cropping initiated in 2000 covered 29% of farm area by 2011 due to: (1) failure of ILK-based alder planting in checking wildlife menace and inability of government agencies in developing solutions to the problem, (2) lack of policy for compensating crop/honey losses due to wildlife, (3) land holdings becoming too small (0.2 ha per capita in 2011) to secure livelihoods and (4) decline in cultural values prohibiting agricultural abandonment and fostering collective wildlife control due to access to subsidised food grains and acculturation to improved accessibility (distance to road reduced to 6 km in 2011, from 14 km in 1991). Forest recovery failed in abandoned farms as a result of the open-access status of unleased farms and stunted yew growth in leased/protected farms.

Government agencies planted conifers on seven hectares of degraded community forest between 2006–2007, engaging local people as wage labourers. The plantation suffered a 100% mortality within a year due to ﬁres set by the people themselves, who value herbaceous forage more than conifers. Administrative machinery was too weak to check illicit forest ﬁres and private farm leasing.

People listed many reasons behind the failed expansion of the trial: (1) it could not mitigate the new wildlife menace problems, decline in the demand for bamboo handicrafts and competition/uncertainties in walnut/medicinal herb markets; (2) it did not satisfy new aspirations viz., freedom to harvest and market all forest products, establishment of value-added facilities within the village and increase in quantum of government support for restoration; (3) technological stagnation created a mindset of looking down upon the traditional labour-intensive production system; and (4) it could not compete with new opportunities for income from caterpillar fungus (Cordyceps sinensis) and government-funded infrastructure development projects in the absence of protected markets for restoration products and commitments to payments for ecosystem services. Agricultural abandonment nulliﬁed restoration-mediated carbon sequestration.

4 Discussion

4.1 Socio-Ecological Diversity

Subjective carving of community forests resulted in enormous variation in their extents, accessibility and ecological status. It is common to observe communities conserve intact forests and restore selectively logged forests vast enough to secure their essential needs by deploying their ILK and social capital centred around passive restoration. Because of cultural restraints on the timber trade, the intact community forests of Khaljhuni were more efﬁcient in storing carbon (Buffum et al. 2008; Sharma et al. 2010; Pandey et al. 2014) and harbouring species of high conservation (Maikhuri et al. 2000; Adnan and Hölscher 2011) and ecological values (Bhadauria et al. 2012) than the ones managed by the communities free from such restraints. On the other hand, intact forest patches lacking religious value and too small to meet subsistence needs, recharge potable water sources, mitigate ﬂoods and to stabilise slopes, suffered from illicit logging by outsiders and then encroachment by local people (Semwal et al. 2004; Wakeel et al. 2005). Due to increasing integration into the mainstream, Khaljhuni people aspired for a quantum leap rather than an incremental rise in income, feasible only by active restoration lacking in ILK. Divergent from people’s expectations, conventional restoration targeted forest area expansion to cover two-thirds the area of mountains and one-third the area of the country at the time of trial initiation in the early 1990s.

4.2 Environment-Knowledge-Culture-Policy Interlinkages

The initial demand for growing marketable herbs/short bamboo was a combined reﬂection of the people’s aspirations for early and high income and their ignorance of scientiﬁc knowledge (Guariguata et al. 2010; Ashton et al. 2014) and the expectations of other stakeholders. Participatory discussions enriched ILK and motivated people to minimise trade-offs between immediate economic and long-term ecological beneﬁts from restoration (Yami et al. 2013; Andrews and Borgerhoff Mulder 2018). Attention to non-material beneﬁts and people’s priorities, which were excluded in top-down restoration, enabled people to (1) conceive new ideas viz., alder planting in gaps in the restored plot and medicinal herb cultivation in private farms, and visualisation of ILK-based new commercial products, (2) revise/rectify based on new learnings reﬂected from inclusion of tree planting, deferring of new lease proposals and abandonment of cultural values forbidding income even from over-mature/dead/diseased trees, and (3) offer in-kind contributions which reduced treatment establishment (Rao et al. 1999) and monitoring costs (Evans et al. 2018). ILK has been increasingly recognised as an under-exploited resource and community participation as a means of cost-effective forest management and inclusive development worldwide after 1980.Yet, forest restoration planning, monitoring and ﬁnancial management remains the state monopoly. Top-down restoration pro- jects continue to thrive as a result of projection of their success based on achievement of planting targets rather than the magnitude of ecological recovery (Le et al. 2012; Dudley et al. 2018). These projects serve the vested interests of a few ofﬁcials and elected representatives more than community well-being (Barr and Sayer 2012; Baynes et al. 2015). Likewise, bioprospecting remains the monopoly of mega- industries in the absence of strict enforcement of free, prior and informed consent procedures and ambiguous beneﬁt-sharing provisions (Maikhuri et al. 2004).

Unlike conventional projects treating people solely as beneﬁciaries, this project involved them as responsible stakeholders owning all decisions, collecting scientiﬁc data and maintaining expenditure accounts jointly with the researchers. Following the traditional norms, ﬁnal decisions were made by consensus in an open assembly steered by the community leaders and facilitated by the researchers (Rao et al. 1999). Whole-hearted community participation thus derived from researchers appreciating and enriching ILK and cultural heritage, recognising people’s needs/aspirations, living with them, establishing a transparent expenditure accounting system and earnestly following the principles of co-management (Berkes 2009). Voluntary maintenance from the eighth year onwards testiﬁes that people tend to honour their informal commitments and take collective action when they encounter anticipated shocks like bamboo ﬂowering. Nonetheless, the trial succeeded in securing investment in restoration, but not in its voluntary expansion or upgradation. A quantum rise in effectiveness and efﬁciency of current forest restoration approaches is the key transformative change needed to arrest/reverse global deforestation and forest degradation. The present study unveils that this change is feasible from a set of concomitant policy changes for (1) harnessing and enriching ILK and cultural heritage, (2) motivating people to contribute surplus physical resources, (3) making people a formal party in designing and monitoring treatments and ﬁnancial management, (4) rescuing people from unanticipated problems like excessive wildlife intrusions and economic exploitation by industries and traders whose mitigation is beyond their knowledge and capacity, and (5) nesting restoration in long-term and adaptive landscape management-cum-livelihood enhancement plans.

Policies have changed, but are far from the expectations of people and initiatives in other countries (Berkes 2009; Liu et al. 2016). Lack of holistic and integrated landscape management approaches advocated since the 1980s manifested in decline in competitiveness of forest restoration. With increasing education and awareness, people are becoming disgusted with policy elements lacking scientiﬁc and/or socio- economic rationale: (1) transfer of only 18% of forest area taken over from them in the nineteenth century and community empowerment just to regulate subsistence uses in an era of economic globalisation, (2) meager ﬁnancial support for ILK-based treatments (Derak et al. 2018) and persistence of cultural heritage favouring equity, community solidarity and environmental sustainability (Maikhuri et al. 2000), (3) elongation of restoration project duration without raising the quantum of ﬁnancial support, (4) arbitrary selection of households for availing government incentives, and (5) lack of commitments on community share in UN-REDD+ and other mechanisms of payments for ecosystem ILK on medicinal plants and new demand for them in national and overseas markets prompted policy uptake, but budget support was too low to induce any transformative change. Further, policy support was largely conﬁned to cultivation in private farms, anticipating that wild populations would be restored. This was unsuccessful due to loopholes in the existing mechanisms of checking illicit harvests and their marketing (Rao et al. 2015). Failure of policy uptake for long-term support for participatory-adaptive restoration and for synergising forest conservation, forest restoration, agricultural development and socio-economic upliftment underscores a need for effective inter- actions among stakeholders: people, researchers, industrialists, traders and government ofﬁcials. This failure seems to be the root cause of the lack of competitiveness of current forest restoration pathways, nulliﬁcation of restoration-mediated carbon sequestration by agricultural abandonment-mediated emissions, and people’s perceptions about the unfair sharing of beneﬁts from new products.

Voluntary maintenance of the trial area despite poor survival of medicinal herbs and the ineffectiveness of alder in checking wildlife intrusions suggest that people value whole-hearted efforts more than their outcomes (Andrews and Borgerhoff Mulder 2018). Voluntary maintenance of the trial from the eighth year onwards was a sort of reciprocation for external support to the satisfaction of the people. Participation merely as wage earners resulted in unproductive investment in top-down restoration planting in the absence of a sense of ownership, responsibility and accountability among people and law enforcement (Schultz et al. 2012; Lyver et al. 2019; Reyes-Garcia et al. 2019). Discontentment among people due to neglect of their genuine concerns may turn into mass movements, like the ones in the 1920s forcing government to create community forests, in 1970s to ban logging even by its agencies in natural forests and to restore ecotourism, for example, in the Nanda Devi Biosphere Reserve (Maikhuri et al. 2000; Rao et al. 2015).

Assuming persistence of a net above-ground accumulation rate of 0.75 Mg C ha^-1 year^-1 observed at the end of the 20th year, it will take 210 years to restore C stock in the temperate intact Himalayan forest compared to 50–100 years in tropical forests (Marin-Spiotta et al. 2007; Wheeler et al. 2016; Lewis et al. 2019). Recovery in species richness was faster than carbon stock due to planting of a large number of species and minimal weeding. Active restoration is more expensive than passive restoration but a necessity in a biodiversity hotspot like Himalaya with intense limitations of propagule dispersal, viable soil seed banks and safe sites in shallow-gravelly soils on steep slopes. This study also underscores a need for treating cultural landscapes (Takeuchi et al. 2014; Reed et al. 2016) rather than just forests (Vanderhaegen et al. 2015) as spatial units, and for clarity on accounting of below-ground and harvested biomass carbon pools, and for time scale in deter- mining payments for ecosystem services.

5 Conclusions

The present long-term location-speciﬁc study shows that nature and outcomes of participation of local people in forest restoration would vary in space and time depending on the socio-ecological conditions. Our ﬁeld visits during the 2011–2019 period after systematically analysing the landscape for 20 years suggest the persistence of agricultural abandonment, restoration failure beyond the trial area, conservation of intact forest and the mindset of higher social status of urban liveli- hoods. The present study unveils the following practices for transformative change to achieve national or global targets:

Nesting restoration in participatory long-term adaptive and integrated landscape and livelihood enhancement programmes;
Coupling commodity production with bioprospecting, manufacturing and marketing;
Formally involving communities in planning, monitoring and ﬁnancial management;
Assuring funding until restoration becomes an additional source of material/ income beneﬁts to people;
Limiting funding to inputs unaffordable by people with a condition of people- researcher joint monitoring after cessation of funding;
Stimulating the inquisitive minds of people by informing them of the scientiﬁc implications of their ILK, as well as that evolved by other communities;
Convincing policymakers to provide scientiﬁc foundations for stands/actions in open domain, and necessary support for the development of a network of “model restoration landscapes” co-managed by local people, researchers, traders and industrialists, and to commit a fair share to communities in payments for ecosystem services;
Promoting condition/performance-based incentives/subsidies/rewards/compensation at multiple spatial (household, village, and village cluster) and temporal (short, medium, and long-term)

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