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Review

Lessons from Managing for the Extremes: A Case for Decentralized, Adaptive, Multipurpose Forest Management within an Ecological Framework

1
ForestAction Nepal, GPO Box, Lalitpur 12207, Nepal
2
The Forest School, Yale School of the Environment, New Haven, CT 06511, USA
3
School of Agriculture, Food and Wine, The University of Adelaide, Urrbrae, Adelaide, SA 5064, Australia
*
Author to whom correspondence should be addressed.
Forests 2022, 13(2), 333; https://doi.org/10.3390/f13020333
Received: 5 January 2022 / Revised: 9 February 2022 / Accepted: 14 February 2022 / Published: 18 February 2022
(This article belongs to the Section Forest Ecology and Management)

Abstract

:
Multipurpose and ecological forest management frameworks are being increasingly applied across the Global North on public lands. However, the discourse and practice of public forest management in much of the developing world are captured by extreme approaches of single-crop (usually timber) production and strict canopy-cover protection, as exemplified by the case of Nepal. We combine insights from field research with published documents and trace the consequences of prevalent management regimes on the ecology and silviculture of Nepal’s public forests. We find that managing for either extreme of timber production or forest protection can degrade forest ecosystems and affect their capacity to address the increasing number of demands placed on them. A history of narrow management outlooks has erased indigenous silvicultural practices and discouraged the development of novel silvicultural solutions to address today’s environmental concerns. Government initiatives advancing singular objectives, such as Nepal’s Scientific Forest Management program, often crumble under political resistance. Forest users in Nepal are widely interested in generating diverse benefits from their forests, including non-commercial products and services, suggesting a mandate for multipurpose management. We present a decentralized adaptive modality of multipurpose management featuring a silviculture that more closely matches the ecology of forests.

1. Introduction

Despite the widespread demand for a multitude of forest products and services [1,2,3,4], both the discourse and practice of public forest management, in modern history, have largely gravitated towards two problematic extreme positions. At one extreme is an approach that uses public forests to produce a single crop, usually timber. This outlook often animates conflicts over land uses [5,6] and can degrade a variety of attributes of the forest resource, regardless of whether it involves destructive resource use [7,8] or careful silvicultural planning to produce sustained yields [9,10]. At the other extreme lies a strict protection-oriented stance that excludes almost all human uses of public forests other than recreation, often to the detriment of a variety of ecological attributes dependent upon disturbance [11,12]. The blanket application of this approach disenfranchises forest-dependent communities and disregards their heritages of multifaceted indigenous silviculture [13,14]. This outlook often conflates all forms of tree-felling with forest degradation, negating the utility of active silvicultural treatments for restoration and regeneration [15,16].
Deviations from these extreme approaches began to appear as early as the beginnings of timber-centric scientific forestry [17] and protectionist environmentalism [18] in colonial times. Since at least the middle of the 20th century, high-income nations have had large-scale implementations of novel management approaches in their public lands [19,20,21]. These include ‘multipurpose management’ to address multiple socioeconomic objectives [21,22,23,24] as well as ‘ecosystem management’ [25] and, subsequently, ‘ecological forestry’ to actively engineer complex, resilient and productive ecosystems [15]. Yet, barring some exceptions [26], the discourse and practice of public forest management, in much of the Global South, still largely oscillates between the dichotomy of single-crop production and strict protection [27,28]. This has been the case despite the prominence of movements to decentralize management back to local communities that depend on forests for multiple resources [29,30].
Nepal, heralded for the implementation of community forestry across much of its public forests [31,32], provides an illustrative example of a nation confined to these antiquated extreme approaches. The discourse on public forest management in Nepal has been reenergized by the dissolution of ‘Scientific Forest Management (ScFM)’—a government project to increase domestic timber production. However, the narrowness of the current debate exposes the persistence of the historical tendency to dichotomize forest management into the extremes of timber production and passive forest protection. In this article, we chart the historical course of these extreme approaches to managing Nepal’s public forests, uncovering ecological consequences and impacts on the development of indigenous and professional silviculture. We then demonstrate a public mandate for multipurpose management in the managed forests of Nepal and elaborate on how its implementation in Nepal can avoid the short-comings of prior management regimes through effective decentralization, adaptive management and silviculture informed by the ecology of natural forests.

2. Methods

We synthesize together publications, policy documents and reports, with insights from field observations, household surveys and focused group discussions produced by the ‘Enhancing livelihoods from improved forest management in Nepal (EnLiFT)’ project. Since 2013, EnLiFT has been working with multiple community-forest user groups and local farmers to establish silvicultural demonstration harvests, to promote local agroforestry practices and forest-based enterprises and to institutionalize novel community-based forest planning and governance frameworks within the new local government system. We also present diagrams to help readers visualize the chronology of public forest management in Nepal (Figure 1) as well the described modality of multipurpose management at the levels of both the forest stand (Figure 2) and local landscape (Figure 3).

3. Decline of Indigenous Silviculture

Up till the mid-20th century, most forests in Nepal were managed by village communities [33,34,35] using iteratively refined indigenous silvicultural practices to regenerate, protect and utilize multiple forest resources, such as fuel, fodder, medicine, food and timber [36]. In formal terms, indigenous silviculture prominently featured swidden cultivation (alternatively: shifting agriculture; locally: khoriya-kheti) [37,38] and various silvipastoral [39,40] and coppice systems [36].
The Rana premiership gradually developed a centralized forest governance structure over the late 19th century, as Sal (Shorea robusta Gaertn.) timber became a lucrative commodity exported to British India [41]. Eventually, in the early 20th century, Nepal invited officers from the British Indian Forest Service to introduce technical forestry and to create a forest service to manage and sell timber resources [42,43,44]. Despite British India’s efforts to institutionalize forest governance and silvicultural planning, destructive logging practices continued to degrade much of the productive lowland forests of Nepal [45]. The Rana regime also encouraged forest clearance for agricultural expansion to increase its tax revenues, among other reasons [46].
Soon after the regime collapsed, the new state nationalized, at first, some, and eventually all of Nepal’s private and communal forests in the 1950s [41], citing the need to preserve dwindling resources [46]. The nationalization of forestlands alienated village communities from forest management and native governance structures and their associated silvicultural knowledge and practices deteriorated [45,47,48]. The state also actively suppressed indigenous silviculture after environmental experts from foreign-aid agencies attributed environmental degradation to peasant practices, such as swidden forestry [47,49] and rotational and migratory silvipastoralism [39,50]. Swidden forestry was virtually uprooted from Nepal [51] without much academic exploration of its silvicultural particularities and influence on forest composition and characteristics. Today, it is widely acknowledged as a complex form of locally adapted successional agri-silviculture featuring the optimal management of soil fertility and growing space [52]. Over the latter half of the 20th century, foreign experts also facilitated the creation of multiple strictly protected areas in which local inhabitants’ traditional access to forest resources was severely restricted, if they were not displaced entirely [53].

4. Prevalence of Protectionism

Unable to curb clandestine logging in the newly nationalized forests by itself and facing a new foreign-aid mandate to decentralize resource control [47], the state progressively brought local communities back into public forest management, starting in 1978 [54,55]. In the following decades, the government and foreign-aid agencies facilitated communities in establishing timber plantations, mostly of fast-growing native and exotic pines, in open landscapes [56] considered barren or degraded, even though some were actually productive pasture ecosystems [39,50]. Plantations and natural forests were then protected by communities through the regulation of wildlife hunting, forest fires, grazing and encroachment [57,58].
Conservation campaigns promoted a ‘passive’, ‘protection-oriented’ outlook that deprioritized timber management in favor of forest canopy cover expansion and retention, even in timber plantations [59,60]. For example, under activist and media pressure, the state instated recurring nation-wide bans on the felling of live trees [61] and regularly issued directives limiting timber extraction to dead and defective trees [62]. In certain cases, communities themselves avoided cutting live trees, in fear that the encouragement of timber harvesting could escalate degradation or result in total deforestation [63,64]. With harvests of canopy trees suppressed until the early 2000s, timber management remained limited to the non-commercial thinning of poles, pruning, singling of coppices, cleaning of undesirable regeneration, removal of deadwood and exclusion of fire and grazing [63,65,66]. As plantations became overstocked with merchantable timber, the availability of non-wood products declined [59] and communities heavily relied on natural forests to provide leaf litter, fodder, fruits and medicinal plant-parts [67,68,69]. Pine plantations also became associated with the desiccation of water springs [70], though no study conclusively isolated the actual causes.

5. Efforts for Active Management

The push-back against protectionist thinking in public forest management began as far back as the late 1970s. In the most extreme of approaches, the forest administration replaced vast swathes of natural state-managed lowland forests with timber plantations, often featuring exotic species [71,72]. Nonetheless, the government also tested multipurpose approaches in some community forests and state-managed lands (i) to demonstrate the use of natural regeneration-based timber harvests to convert pine plantations to broad-leaf forests [73], (ii) to study the establishment and growth of seedlings in natural forests following natural regeneration harvests [74] and (iii) to explore the potential to develop different silvicultural systems to produce fuelwood, fodder and timber [75,76,77,78]. Eventually, in 1996, with foreign-aid support, the government devised the ‘Operational Forest Management Plan’ program to produce timber in several lowland Sal forests using natural regeneration. However, this project was thwarted by resistant local communities and civil society networks, who were concerned by the program’s lack of local consultation, prohibitively technical prescriptions [79] and the involvement of a private foreign company [80].
A nation-wide shift towards active timber management finally occurred in the early 2000s, when community forests were required to produce inventory-based management plans. The mandated introduction of technical planning, overseen by government officials, marked the beginning of a long process of the recentralisation of community forestry. Management prescriptions were solely concerned with timber production until the late 2000s, when provisions for other forest products grew in popularity (though active canopy management for the production of non-timber resources was not encouraged) [60,81]. Prescriptions were often identical across forests, irrespective of prevalent dynamics and community objectives [81].
However, long-term silvicultural planning for forest resource production and regeneration remained absent from discourse and practice through the 2000s and early 2010s. Both indigenous practices and novel silvicultural innovations were precluded by the persistence of recurring moratoriums on the felling of healthy merchantable trees [82,83]. Further, technicians often arbitrarily restricted harvest allowance volumes to avoid attracting sensational media coverage and legal oversight [61,67,84,85,86]. Consequently, besides the removal of dead and defective trees [82,83], timber harvests were largely limited to light-handed thinnings, which did not even meet the intensity of the administration’s own guidelines [87].
Thinning operations reportedly increased forest productivity [88,89], structural complexity [87] and coverage [90] along with the diversity of the understory and regenerating vegetation [91]. However, where communities heavily favored only economically valuable timber species, thinnings resulted in the mono-dominance of a single species at the cost of excluding other sub-canopy and canopy species [57,59,87,90,92,93] and reducing the availability of non-timber resources [86]. Meanwhile, researchers and managers completely overlooked the consequences of repeatedly and pervasively removing dead and defective trees, despite their important role in the ecological functioning of native forests, and in silvicultural and conservation planning (see Appendix A for details) [94,95,96,97]. In the occasional harvests of mature well-formed trees, technicians either arbitrarily (ad hoc) chose few trees for harvesting [98] or selectively logged out some of the most merchantable trees [59,85,93,99]. Both of these low-intensity operations opened up small poorly-planned canopy gaps in the forest, which at first stimulated a range of plants to germinate and resprout [100] but eventually excluded the regeneration of shade-intolerant and drought-competitive species which require more light to grow after establishment [101] (see Appendix B for details).

6. Scientific Forest Management

6.1. Origins

Following decades of restricted felling and rudimentary harvest planning, both plantations and natural secondary forests suffered from intense canopy competition, which led to the stagnation of growth, wasted timber resources [64,65,92] and suppressed the establishment of an understory that could provide non-timber products [66,90,91]. The forest administration, forest users and academics increasingly came to the consensus that this passive management approach had failed to efficiently generate forest products and benefit communities [32,65,67,88,92,102,103,104,105] and the national economy [60,103,106,107].
In response, the government devised a new program, ‘Scientific Forest Management (ScFM)’, described as “an application of appropriate silviculture systems and forest management principles through design of systematic compartments of fixed rotation age” [108,109]. Following a pilot implementation in 2012 [108], a guideline was issued in 2014 [110] featuring instructions for a high-intensity ‘irregular shelterwood’ silviculture system, explicitly developed to regenerate lowland Sal forests for timber production. Regulatory procedures for harvest planning and implementation were cumbersome and demanded the intensive use of equipment and human resources (foresters and loggers) [108,111]. However, technicians took liberties that helped accelerate the expansion of ScFM. Management prescriptions were near identical to one another, irrespective of forest type, terrain and community objectives, because technicians only referred to the singular shelterwood guideline produced by ScFM [83,108]. There were legitimate concerns that the indiscriminate nation-wide application of intensive shelterwoods, whose regeneration studies revealed very low species diversity [112], would result in the loss of unique forest flora and the provisioning of non-timber products and ecosystem services, such as soil and water conservation [113,114,115]. However, during the actual implementation, technicians often arbitrarily deviated from the guideline, by halving the intensity of the prescribed harvest [116] or instructing communities to establish intensive plantations on harvested sites [117], sometimes replacing native natural regeneration with exotic species [118]. ScFM also inherited, from the prior management paradigm, the poor practice of dividing the forest into largely geometric blocks and compartments for management [116], instead of delineating forest stands on the basis of prevalent biophysical features and social circumstances [119].

6.2. Reception

The most prominent positive achievement of ScFM was its reintroduction of silviculture into Nepal’s discourse on public forest management, culminating in the first ever national workshop on silviculture [120]. The government also successfully demonstrated that high-intensity silvicultural harvests could establish natural Sal regeneration across the Terai lowlands [112,121,122], in spite of bureaucratic hesitancy to cut live trees and uninformed reporters and conservationists mischaracterizing the shelterwood regeneration method as deforestation [123]. Users of some Sal forests even welcomed and appreciated ScFM’s timber-centric agenda, since the large annual timber output of the shelterwoods [107,124,125] generated more income and employment opportunities compared to previous harvesting regimes [121,122,124,126].
However, the ScFM program was mired in irregularities that brought it under increasing state and public scrutiny, sparking years of protest by the Federation of Community Forest Users—Nepal (FECOFUN) [127] and local community resistance [113]. Allegations included the coercion of communities [123,127] and fabrication of consent through forged signatures [128], collusion among forest officials, the local elite and timber contractors [129,130] and a lack of meaningful local participation and access to timber-products [131] and income from timber-sales [111,121,125]. Eventually, the program faced unprecedented public exposure once reports surfaced that COVID-19 lockdowns were being used to illegally clear Sal forests at ScFM implementation sites [132]. The cabinet terminated ScFM in January 2021 [133] after multiple official investigations [134,135] (i) cited irregularities [123,129], (ii) criticized the program’s recentralizing tendency and redundancy [123] in light of existing legal provisions that already enabled silviculture-based management [136] and (iii) questioned its legal standing [130].

6.3. Discourse on Sustainability and Silviculture

Critics of ScFM reasonably argued that the program was unsustainable because it failed to consider ecological sensitivities, foster democratic dialogue among stakeholders and promote local participation and enterprises [137]. They associated ScFM’s socially and ecologically unconscious timber-centric approach with the global history of ‘scientific forestry’ programs, through which state bureaucracies still establish order and control over forestland, often alienating forest-dependent communities [138,139]. Many activists, protesting against ScFM, also vilified the entire concept of silviculture-based management as being colonial, extractive and unsustainable [123]. However, silviculture—the science and art of growing and tending to forests—is not exclusively the legacy of colonial and post-colonial ‘scientific forestry’. Indigenous silviculturists have engineered forests to produce fuelwood, fruits, gum and fodder in Nepal and around the world for thousands of years [140,141]. When ‘scientific forestry’ emerged in 18th century Germany, it formally codified a set of silvicultural practices to produce sustained yields of timber and address the depletion of timber and water resources [139], providing a founding narrative for the entire concept of ‘sustainable development’ of the United Nations in 1987 [142]. Today, silviculture has become a useful tool applied across different management scenarios, including urban forestry, the promotion of ecological complexity and the creation of wildlife habitats [119].
Some critics of ScFM even demanded a reversion to the ad hoc and selective logging regimes that they deemed sustainable for their modest harvest volumes [123]. However, pervasively implementing modest logging regimes may stifle desired forest regeneration and may not even protect biological diversity because high-severity canopy disturbances are required to promote early successional ecosystems [143,144,145,146]. The single-minded insistence on low-intensity regimes is often based on the idealization of an unmanaged wilderness with no human impact, which is in itself largely erroneous and antiquated, even if still globally popular [8,147]. Even the ‘wildest’ of forests, such as in the Amazon and Borneo, have had their diversity and structural complexity significantly enhanced by both intensive and subtle anthropogenic interventions, leading eminent foresters to reasonably argue that we are living in a world where people have been ‘managing the wild’ for thousands of years [148,149]. The concept of a true ‘wild’ is even more untenable in countries like Nepal, where hundreds of mobile ethnic groups have pursued diverse forest-based livelihoods for centuries [150] and play an outsized role in determining forest dynamics and composition [151].

7. Multipurpose Forest Management

Prior governance approaches promoting singular management objectives in Nepal not only had adverse ecological impacts and suppressed indigenous and professional silviculture but also misread or disregarded the actual interests of forest-dependent communities. Most often, community forest users are actually interested in fulfilling diverse non-commercial objectives and generating multiple outcomes from forest management, including the production of fuelwood, fodder, mulch, fruits and medicinal plants, besides timber [87,152]. In fact, in some areas, people’s reliance and engagement with communal forests have actually declined in recent years, since their diverse needs are not met by prevalent management regimes [152]. Communities are much more likely to assume responsible stewardship of forest resources if their multiple interests are addressed through a multipurpose forest management approach [152].
Multipurpose management, alternatively called multiple-use [153,154], multifunctional [24] and integrated forest management [155,156,157], refers to the management of forest land for more than one purpose, such as the production of wood, fruits, resin and medicine, water source protection, biodiversity promotion and human recreation. To some extent, native communities have persisted with multipurpose management for fuel, fodder, food and medicine, even if official management plans focus on singular objectives [87,141,158]. In the professional forestry world, formal multipurpose management frameworks have been implemented to complement industrial timber forestry with the generation of non-timber forest products, watershed management and the creation of therapeutic landscapes for stress relief [153,159].
Multipurpose management can be accomplished through the use of one or a combination of the following approaches [154]: (i) simultaneous production of various services and goods in a single forest stand (such as timber, fruit, fiber and medicine in Figure 2 (2.2.6)); (ii) rotational and successive production of different resources in the same stand (such as the gradual replacement of tuber and herb production in Figure 2 (2.1.3) by timber production and understory farming in Figure 2 (2.1.5)); and (iii) geographic segregation of uses across a mosaic of stands in the same landscape (such as exclusive fruit production in Figure 2 (2.1.4) and exclusive forage production in Figure 2 (2.2.8)).
Following the collapse of ScFM, new efforts are underway to create a national standard for sustainable forest management in managed public forests, which is expected to promote multipurpose management, local decision making and indigenous practices (field notes). Based on these developments, we introduce a modality of multipurpose management, designed to avoid the social and ecological consequences of prior regimes through (i) effective decentralization, (ii) adaptive management and (iii) silvicultural applications of the ecological principles of forest stand dynamics.

7.1. Effective Decentralisation

Community-based management in Nepal has been recentralized by technocratic control over harvest planning and the requirements for technical inventories and management plans which do not address the community’s varied interests [82,83,140,160]. Formal inventories are often redundant where many forest-dependent communities already spend a significant amount of time regularly learning about their forest’s condition and resource base [140]. Communities act on this local knowledge by adapting poorly designed technocratic prescriptions to sustainably produce multiple forest products [82,160]. These government requirements can be simplified and, in smaller forests with modest subsistence uses, even eliminated, allowing local forest users to determine the nature and intensity of land uses and silvicultural manipulation based on shared knowledge of site productivity, harvest regulation and ecology [87]. However, foresters, ecologists and project developers may have to help interested communities develop novel technologies for new pursuits, such as ecotourism (field notes), while inspiring and empowering communities with deteriorated native management frameworks [57] to reengage in forest management and pursue the greatest diversity of forest uses.

7.2. Adaptive Management

In a country like Nepal where natural forest stand dynamics are poorly understood and management interests vary widely, the pursuit of sustainable multipurpose management requires an ‘adaptive’ style of silvicultural design and implementation [161]. Adaptive silviculture and management acknowledge that “the understanding of forest dynamics and the development of silvicultural systems should be continually evolving processes” [161] as opposed to the rigid adherence to technical guidelines. The forest manager must continually analyze the “details of tree structure and physiology, soils, climate, natural disturbances, and human use” of their particular forest, instead of relying on broad ecological generalities [161]. This involves three steps: (i) applying silviculture treatments using current knowledge and monitoring effects on the forest; (ii) updating assumptions and adapting silvicultural planning based on new knowledge obtained from monitoring; and (iii) documenting the planning, implementation and results of a prescription. Managers can then devise and continuously adapt the harvest pattern and volume calculations required to guide the forest to a deliberatively planned condition [162]. Since adaptive management demands intimacy with the particular forest to be managed, it favors the devolution of decision-making power to forest-dependent local communities and encourages the incorporation of their ethnoecological knowledge and practices into silvicultural planning [163].

7.3. Ecological Principles of Forest Stand Dynamics: Stand- and Landscape-Level Practices

In community forests in Nepal, the pursuit of multiple objectives together, such as environmental protection and the generation of a range of forest products, can be complementary to one another [102]. Since such forests feature the simultaneous or successive growth of multiple plant species, they also tend to display greater species diversity [93]. Elsewhere, forests managed for multiple values also had greater diversity of species traits (functional diversity) [164] and were structurally more complex [165], potentially because all vertical strata were put into productive use. The promotion of ecological complexity, through an increase in taxonomic, functional and structural diversity, can increase ecosystem function and make forests more adaptive and resilient to catastrophes and chronic disturbances [119,166,167,168], including global changes [169]. Nonetheless, in the absence of a proper orientation, there is always a risk that multipurpose management may devolve into extractive multi-crop production and potentially lead to a decline in complexity, health and resilience. This concern can be addressed by closer silvicultural adherence to a variety of ecological principles under the sub-discipline of forest stand dynamics. In North America, some academics and practitioners have coined the term ‘ecological forestry’ [170]. They preach the practice of ‘ecological silviculture’ and define their management recommendations and practices as emulating a range of functions, processes, dynamics, compositions and structures, observed in complex natural ecosystems, that represent all stages of forest succession [15]. This framework has been largely associated with relatively remote, expansive native public forests managed primarily for timber by federal and state-level bureaucracies but with little demand for high resource production [19]. Nonetheless, even the partial adoption of ecological forestry can potentially increase the vitality and integrity of relatively more intensively managed multipurpose production forests [171].
Ecological principles that can be used to more closely emulate native forest stand dynamics when practicing silviculture include: (i) allowing the accumulated structure, function and biotic community of a forest to continue persisting after a regeneration harvest through the retention of live old trees, productive seed sources, snags (standing dead trees), trees with large cavities and coarse woody debris (Figure 2 (2.1.2) and Figure 2 (2.2.6)); (ii) sustaining and promoting compositional and structural complexity, biological diversity and spatiotemporal heterogeneity at the scale of the individual stand (Figure 2 (2.2.6)) as well as the entire forest by maintaining the whole array of cover-types and successional stages (Figure 3); (iii) applying treatments at ecologically appropriate timescales which allow the development of the structural, compositional and functional complexity in forests; and (iv) managing forests in the context of objectives and land uses prevalent at the larger spatial scale of the landscape [15,170,171,172].
To elaborate on the last principle, landscape-level ecological planning of forests often includes two different concepts. The first is ‘functional zoning’, which reconciles ecological and socioeconomic goals by adopting the multipurpose forestry approach of spatially segregating a forest landscape into zones that produce different sets of goods and services (i.e., functions) [173]. An example of functional zoning, useful to large community-managed forest landscapes, is the ‘landscape triad’ approach featuring a mosaic of three land-use designations: (i) areas allocated towards intensive commodity production, (ii) a connected network of protected ecological reserves of rare old-growth forests, sacred groves and hydrological structures, such as streams and swamps (Figure 3), and (iii) areas managed for both ecological complexity and modest resource production [173]. Functional zoning can increase the resilience of a landscape to withstand disturbances, such as insect outbreaks or climatic shifts, while ensuring the sustainable long-term production of desired goods and services [174].
The other concept, ‘integrated landscape management’, refers to the identification and utilization of hydro-ecological linkages and synergies among forest ecosystems, agroecosystems, pastoral ecosystems and aquatic ecosystems, nested in the same landscape (Figure 3) [175]. This concept has only recently gained traction among professional circles [176] because modern chemical-based agriculture has significantly divorced agricultural planning from other land uses [177]. However, many rural communities in Nepal, for centuries, have been synergizing matrixes of farms and forests with patches of settlements, wetlands, shrubland and open meadows, and corridors of riparian forests, streams and roads (Figure 3) (field notes). Nonetheless, forest-level and landscape-level elements of ecological silviculture may be impracticable when community forests face intensive socioeconomic demands or are small and embedded in landscapes that communities do not entirely control. There is an opportunity to manage landscapes through cooperation, such as by allocating state-managed lands, adjacent to intensively managed community forests, as the ecological reserves in the landscape. However, formal landscape-level planning in Nepal, in particular watershed management, has been marred by a lack of meaningful dialogue and engagement among concerned stakeholders [178].

8. Challenges Ahead

8.1. Research on Silviculture and Forest Stand Dynamics

Scholarly advancements in the understanding of forest stand dynamics have facilitated the development of silviculture in natural mixed-species stands in many high-income nations [161]. Academics and forest-managers, in developing nations, such as Nepal, must also invest an unprecedented effort in training silviculturists and studying diverse natural forests in order to gain localized understanding of forest dynamics. Such studies would include longitudinal observations and analysis of vegetation responses to disturbances in chronosequences [179,180], experimental canopy openings [181] and harvests [182], as well as tracing the ontogenetic history of forest trees by conducting stem and crown analyses [183] and learning from ethnoecological traditions [141]. The demonstration of the utility of silvicultural harvests, by successfully producing desired forest conditions and multiple resources via experimentation, would also publicly dispel the stigma around cutting live trees.
One approach to developing appropriate technologies required to establish multipurpose management, featuring both indigenous practices and modern silvicultural innovations, is through the aforementioned ‘EnLiFT’ project’s approach of iterative ‘collaborative action research’ involving forest users and professional foresters [87,104]. Instead of promoting a particular silvicultural regime, it has brought together forest users, professional foresters and researchers to jointly develop and implement silvicultural systems that respond to the needs and capacities of the forest users through Active and Equitable Forest Management (AEFM). It is ‘active’ in that forest dynamics are consciously directed towards specific ecological states as opposed to a ‘reactive’ ad hoc management guided by prevailing commercial and regulatory constraints. It is ‘equitable’ in that all stakeholders, from all groups within the local community through to various layers of government, are recognized as deserving access to forest resources. Both active and equitable drivers inevitably create multipurpose forests.

8.2. Complexities Introduced by Carbon and Climate Mitigation

The fate of the embryonic global movement of multipurpose management will be undoubtedly influenced by its interaction with the United Nation’s ongoing supranational environmental governance scheme, known as REDD+, which plays a leading role in the current discourse and practice of public forest management [184,185]. REDD+’s focus on protecting and increasing forest carbon could either promote or stifle the establishment of multipurpose management, depending on governance approaches, site conditions and local management objectives [186]. In Nepal, the forest administration has planned to impose a protectionist approach to carbon sequestration and forest emission reduction through the restriction of forest grazing and fuelwood harvesting by local communities [187]. As Nepal has already committed to sell its forest carbon through the REDD+ program [188], there is a concern that the pendulum of public forest management may swing from ScFM’s timber-centric focus back to strict protectionism, instead of landing on multipurpose management.

9. Conclusions

Public forest management may perpetually swing between extremes unless it is challenged by the widespread communication and collaborative demonstration of the socioecological benefits of multipurpose management. A radical transformation in forest planning and management to a multipurpose modality calls for advocacy, training and long-term experimental demonstrations on multipurpose silvicultural systems and governance approaches, as well as collaborative research into natural forest dynamics. These experimental models can serve as references for policy makers, technicians and forest users to construct appropriate institutional networks and design their own set of silvicultural treatments. In order to avoid multipurpose management from derailing into multi-crop production and degrading forest ecosystems, professionals and rights networks will also have to promote adaptive management and silviculture within an ecological framework, while encouraging the revival of sustainable ethnoecological practices.

Author Contributions

Conceptualization, S.T., N.S.P., L.N.S., M.S.A., B.H.P., I.K.N., E.C., S.B.B. and S.B.; methodology, S.T., L.N.S. and N.S.P.; writing—original draft preparation, S.T.; writing—review and editing, S.T., M.S.A., L.N.S., N.S.P., B.H.P., I.K.N., E.C. and S.B.; visualization, S.T. and S.B.B.; supervision, N.S.P.; project administration, N.S.P. and I.K.N. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Acknowledgments

The authors acknowledge the generosity and hospitality of the Deupokhari forest user group in Sindhupalchowk and the Hijejaljale-ka forest user group in Kavrepalanchowk. We are also grateful for the support and helpful comments received from our colleagues: Rahul Karki, Madan Basyal, Sakar Jha, Lakhsman Kunwar and Shyam Bhandari at ForestAction Nepal, Hemant R. Ojha at the University of Canberra and Avash Bhandari at the University of Illinois, Chicago.

Conflicts of Interest

Four authors (S.T., N.S.P., S.B. and I.K.N.) are project members in EnLiFT2.

Appendix A. Retention of Dead, Decaying and Deformed Wood

Thinning out deformed and dying trees that are slowing the growth of competitive trees can increase forest productivity [119], while removing diseased trees can sanitize forests plagued by infectious diseases and pests [119]. However, the partial retention of coarse woody debris from fallen and dying trees as well standing dead and decaying wood is important for the ecological functioning of native forests, particularly those growing on marginal soils, as well as for silvicultural and conservation planning [94,95,96]. In fact, their presence is commonly used as an indicator of forest health and resilience [97]. The mid- and ground-stories of forests are often mostly composed of deformed unmerchantable trees, and some rare upper canopy species may also be locally represented only by deformed and decaying trees. A harvest regime focused on removing these trees can reduce species diversity [9] and structural complexity, affecting the movement of seed-dispersing animals and eliminating habitat for wildlife that depend on the cover of lower-strata trees [189]. Similarly, fallen decaying logs may be crucial for regeneration management, as they are often the only microsites in which some tree species can competitively establish and grow [190,191,192]. Dead and dying wood also provide growing substrates for vines, fungi, lichen and bryophytes [193,194]; predatory birds nest and perch on standing defoliated trees; and cavities in decaying trees and logs sustain and shelter small birds and seed-dispersing mammals [195]. In some instances, astutely retaining dying, deformed or decaying trees can actually protect the vigor and quality of neighboring healthy trees. For example, the retention of overtopped deformed trees prevents the boles of adjacent well-formed canopy trees from being exposed to sunlight after canopy harvest operations, discouraging the sprouting of epicormic branches that can decrease timber quality [196].

Appendix B. Ad hoc Harvesting and Selective Logging

Some technicians and academics erroneously referred to both arbitrary (ad hoc) and low-intensity selective logging as ‘selection-felling’ [84] because they removed light volumes of timber and created cool partially shaded canopy gaps like those in single-tree selection silviculture. However, these harvests were neither planned to maintain an even distribution of all age classes of trees in the forest nor to deliberatively target the regeneration of shade-tolerant species, as is typical in actual single-tree selection silviculture [119]. Though selective logging is a globally common practice in which trees larger than a certain diameter are cut [197,198], it has little basis in forest dynamics and regeneration ecology, unlike actual silvicultural treatments. ‘Selective logging’ is actually criticized by professional silviculturists as an ecologically and often economically detrimental practice [119] that degrades a forest’s resource base by singularly focusing on the immediate extraction of the largest and most valuable timber trees [7]. Outside Nepal, recurring episodes of selective logging have left forest canopies with only depauperate trees likely to produce fewer seedlings lacking in genetic diversity [199,200] and have inadvertently shifted the canopy to a more shade-tolerant tree composition [201]. The isolated effects of ‘ad hoc’ harvesting and selective logging within Nepal are not well-known because observational studies often clump their effects with each other and with those of lopping, weeding and livestock grazing [90,202,203,204,205]. In the worst cases, the creations of these gaps, in the absence of regeneration management, may have encouraged invasion by undesired shrubs and vines, such as the fire-tolerant invasives Chromolaena odorata (L.) R.M.King & H.Rob. and Mikania micrantha Kunth [206,207,208], that arrest forest succession by usurping the growing space of the ground story.

References

  1. FAO (Food and Agriculture Organisation of the United Nations). Asia-Pacific Forestry Towards 2010: Report of the Asia-Pacific Forestry Sector Outlook Study; Food and Agriculture Organisation of the United Nations: Rome, Italy, 1998. [Google Scholar]
  2. Favero, A.; Daigneault, A.; Sohngen, B. Forests: Carbon Sequestration, Biomass Energy, or Both? Sci. Adv. 2020, 6, eaay6792. [Google Scholar] [CrossRef] [PubMed][Green Version]
  3. Shields, D.J.; Martin, I.M.; Martin, W.E.; Haefele, M.A. Survey Results of the American Public’s Values, Objectives, Beliefs, and Attitudes Regarding Forests and Grasslands: A Technical Document Supporting the 2000 USDA Forest Service RPA Assessment; Gen. Tech. Rep. RMRS-GTR-95; U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: Fort Collins, CO, USA, 2002; Volume 95, 111p.
  4. Vogt, K.; Gara, R.; Honea, J.; Vogt, D.; Patel-Weynand, T.; Roads, P.; Fanzeres, A.; Sigurdardottir, R. Historical Perceptions and Uses of Forests. In Forests and Society: Sustainability and Life Cycles of Forests in Human Landscapes. CABI: Compton, CA, USA, 2006; pp. 1–29. [Google Scholar]
  5. Erdle, T.A. The Conflict in Managing New Brunswick’s Forests for Timber and Other Values. For. Chron. 1999, 75, 945–954. [Google Scholar] [CrossRef][Green Version]
  6. Widmark, C. Forestry and Reindeer Husbandry in Northern Sweden–the Development of a Land Use Conflict. Rangifer 2006, 26, 43–54. [Google Scholar] [CrossRef]
  7. Kelty, M.J.; D’Amato, A.W. Historical Perspective on Diameter-Limit Cutting in Northeastern Forests. U.S. Department of Agriculture, Forest Service, Northeastern Research Station: Broomall, PA, USA, 2006; Volume 342. [Google Scholar]
  8. Perley, C.J. Resourcism and Preservationism in New Zealand Forestry: An End to the Dichotomy. N. Z. J. For. 2003, 11–17. [Google Scholar]
  9. Finkeldey, R.; Ziehe, M. Genetic Implications of Silvicultural Regimes. For. Ecol. Manag. 2004, 197, 231–244. [Google Scholar] [CrossRef]
  10. Langston, N. When Sound Science Is Not Enough: Regulating the Blues. J. For. 2000, 98, 31–35. [Google Scholar]
  11. Elliott, C. Paradigms of Forest Conservation. UNASYLVA-FAO 1996, 47, 3–9. [Google Scholar]
  12. Oravec, C. John Muir, Yosemite, and the Sublime Response: A Study in the Rhetoric of Preservationism. Q. J. Speech 1981, 67, 245–258. [Google Scholar] [CrossRef]
  13. Bloom, R.; Deur, D. “Through a Forest Wilderness”: Native American Environmental Management at Yosemite and Contested Conservation Values in America’s National Parks. In Public Lands in the Western US: Place and Politics in the Clash between Public and Private; Sullivan, K.M., McDonald, J.H., Eds.; Lexington Books: Lanham, MD, USA, 2020. [Google Scholar]
  14. Vilgiate, T. Forestry and the “World on Paper”: Ideas of Science and Resistance to Forest Reservation on the Gold Coast in the Early Twentieth Century. Ghana Stud. 2020, 23, 3–27. [Google Scholar] [CrossRef]
  15. Palik, B.J.; D’Amato, A.W.; Franklin, J.F.; Johnson, K.N. Ecological Silviculture: Foundations and Applications. Waveland Press: Long Grove, IL, USA, 2020; ISBN 1-4786-4523-7. [Google Scholar]
  16. Pesklevits, A.; Duinker, P.N.; Bush, P.G. Old-Growth Forests: Anatomy of a Wicked Problem. Forests 2011, 2, 343–356. [Google Scholar] [CrossRef][Green Version]
  17. Saldanha, I.M. Colonialism and Professionalism: A German Forester in India. Environ. Hist. 1996, 2, 195–219. [Google Scholar] [CrossRef]
  18. Barton, G. Empire Forestry and the Origins of Environmentalism. J. Hist. Geogr. 2001, 27, 529–552. [Google Scholar] [CrossRef][Green Version]
  19. D’Amato, A.W.; Palik, B.J.; Franklin, J.F.; Foster, D.R. Exploring the Origins of Ecological Forestry in North America. J. For. 2017, 115, 126–127. [Google Scholar] [CrossRef]
  20. Puettmann, K.J.; Wilson, S.M.; Baker, S.C.; Donoso, P.J.; Drössler, L.; Amente, G.; Harvey, B.D.; Knoke, T.; Lu, Y.; Nocentini, S. Silvicultural Alternatives to Conventional Even-Aged Forest Management—What Limits Global Adoption? For. Ecosyst. 2015, 2, 8. [Google Scholar] [CrossRef][Green Version]
  21. Meacham, G.P. The Multiple Use-Sustained Yield Act: A Decade of Consideration. Ida. Law Rev. 1973, 10, 105. [Google Scholar]
  22. Tognetti, R.; Mugnozza, G.S.; Hofer, T. Mountain Watersheds and Ecosystem Services: Balancing Multiple Demands of Forest Management in Head-Watersheds; European Forest Institute: Joensuu, Finland, 2017. [Google Scholar]
  23. Vize, S.; Killin, D.; Sexton, G. The Community Rainforest Reforestation Program and Other Farm Forestry Programs Based around the Utilisation of Rainforest and Tropical Species; Erskine, P.D., Lamb, D., Bristow, M., Eds.; Rural Industries Research and Development Corporation: Canberra, Australia, 2005; pp. 7–22. [Google Scholar]
  24. Wiersum, K.F.; Elands, B.H. The Integrated Multifor. RD Research Approach. In The Changing Role of Forestry in Europe: Perspectives for Rural Development. Forest and Nature Conservation Policy Group. Proceedings; Forest and Nature Conservation Policy Group, Wageningen University: Wageningen, The Netherlands, 2002; pp. 1–24. [Google Scholar]
  25. Christensen, N.L.; Bartuska, A.M.; Brown, J.H.; Carpenter, S.; D’Antonio, C.; Francis, R.; Franklin, J.F.; MacMahon, J.A.; Noss, R.F.; Parsons, D.J. The Report of the Ecological Society of America Committee on the Scientific Basis for Ecosystem Management. Ecol. Appl. 1996, 6, 665–691. [Google Scholar] [CrossRef][Green Version]
  26. Altrell, D. Multipurpose National Forest Inventory in Mongolia, 2014-2017-A Tool to Support Sustainable Forest Management. Geogr. Environ. Sustain. 2019, 12, 167–183. [Google Scholar] [CrossRef][Green Version]
  27. Mgaya, E. Forest and Forestry in Tanzania: Changes and Continuities in Policies and Practices from Colonial Times to the Present. J. Geogr. Assoc. Tanzan. 2016, 36, 45–58. [Google Scholar]
  28. Vandergeest, P.; Peluso, N.L. Political Forests. In The International Handbook of Political Ecology; Edward Elgar Publishing: Cheltenham, UK, 2015. [Google Scholar]
  29. Shackleton, S.; Campbell, B.; Wollenberg, E.; Edmunds, D. Devolution and Community-Based Natural Resource Management: Creating Space for Local People to Participate and Benefit. Nat. Resour. Perspect. 2002, 76. [Google Scholar]
  30. Tole, L. Reforms from the Ground up: A Review of Community-Based Forest Management in Tropical Developing Countries. Environ. Manag. 2010, 45, 1312–1331. [Google Scholar] [CrossRef]
  31. Ojha, H.; Persha, L.; Chhatre, A. Community Forestry in Nepal: A Policy Innovation for Local Livelihoods; International Food Policy Research Institute: Washington, DC, USA, 2009; Volume 913. [Google Scholar]
  32. Springate-Baginski, O.; Dev, O.P.; Yadav, N.P.; Soussan, J. Community Forest Management in the Middle Hills of Nepal: The Changing Context. J. For. Livelihood 2003, 3, 5–20. [Google Scholar]
  33. Bartlett, A.G.; Malla, Y.B. Local Forest Management and Forest Policy in Nepal. J. World For. Resour. Manag. 1992, 6, 99. [Google Scholar]
  34. Fisher, R.J. Indigenous Systems of Common Property Forest Management in Nepal; Environment and Policy Institute, East-West Center: Honolulu, HI USA, 1989. [Google Scholar]
  35. von Fürer-Haimendorf, C. The Sherpas of Nepal: Buddhist Highlanders. University of California Press: Berkeley, CA, USA, 1964; ISBN 0-7195-1464-9. [Google Scholar]
  36. Gilmour, D.A. Forest Resources and Indigenous Management in Nepal. Environment and Policy Institute, East-West Center: Honolulu, HI, USA, 1989. [Google Scholar]
  37. Aryal, K.P.; Kerkhoff, E.E. The Right to Practice Shifting Cultivation as a Traditional Occupation in Nepal: A Case Study to Apply ILO Conventions Nos. 111 (Employment and Occupation) and 169 (Indigenous and Tribal Peoples); International Labour Organization: Kathmandu, Nepal, 2008; ISBN 978-92-2-121452-6. [Google Scholar]
  38. Messerschmidt, D.A. Ecological Change and Adaptation among the Gurungs of the Nepal Himalaya. Hum. Ecol. 1976, 4, 167–185. [Google Scholar] [CrossRef]
  39. Banjade, M.R.; Paudel, N.S. Mobile Pastoralism in Crisis: Challenges, Conflicts and Status of Pasture Tenure in Nepal Mountains. J. For. Livelihood 2008, 7, 49–57. [Google Scholar]
  40. Dong, S.; Wen, L.; Zhu, L.; Lassoie, J.; Yan, Z.; Shrestha, K.; Pariya, D.; Sharma, E. Indigenous Yak and Yak-Cattle Crossbreed Management in High Altitude Areas of Northern Nepal: A Case Study from Rasuwa District. Afr. J. Agric. Res. 2009, 4, 957–967. [Google Scholar]
  41. Regmi, M.C.R. An Economic History of Nepal, 1846–1901; Nath Publishing House: Varanasi, India, 1988. [Google Scholar]
  42. Mr. EA Smythies लाई केही समयको लागी नेपालमा आमन्त्रणा गरिएको विषयको कागजात (Document about Mr. EA Smythies Being Invited to Nepal for a Period of Time); Serial No. 218, Poka Number 168/4; Foreign Ministry Archives Kathmandu: Kathmandu, Nepal.
  43. Mr. EA Smythies नेपाल आएपछि वहाँले गर्ने कामको विषय उल्लेख भएका कागजपत्रहरु (Documents about the Tasks to Be Conducted by Mr. EA Smythies Upon Arriving at Nepal); Serial No. 218, Poka No. 168/5; Foreign Ministry Archives Kathmandu: Kathmandu, Nepal.
  44. Landon, P. Nepal; Constable and Company Limited: London, UK, 1928; Volume 2. [Google Scholar]
  45. Bajracharya, D. Deforestation in the Food/Fuel Context: Historical and Political Perspectives from Nepal. Mt. Res. Dev. 1983, 3, 227–240. [Google Scholar] [CrossRef]
  46. Mahat, T.B.S.; Griffin, D.M.; Shepherd, K.R. Human Impact on Some Forests of the Middle Hills of Nepal 1. Forestry in the Context of the Traditional Resources of the State. Mt. Res. Dev. 1986, 6, 223–232. [Google Scholar] [CrossRef]
  47. Guthman, J. Representing Crisis: The Theory of Himalayan Environmental Degradation and the Project of Development in Post-Rana Nepal. Dev. Change 1997, 28, 45–69. [Google Scholar] [CrossRef]
  48. Hobley, M.; Malla, Y.B. From Forest to Forestry—The Three Ages of Forestry in Nepal: Privatisation, Nationalisation, and Populism. In Participatory Forestry: The process of Change in India and Nepal; Overseas Development Institute: London, UK, 1996. [Google Scholar]
  49. Ives, J.D. The Theory of Himalayan Environmental Degradation: Its Validity and Application Challenged by Recent Research. Mt. Res. Dev. 1987, 7, 189–199. [Google Scholar] [CrossRef]
  50. Saxer, M. Between China and Nepal: Trans-Himalayan Trade and the Second Life of Development in Upper Humla. Cross-Curr. East Asian Hist. Cult. Rev. 2013, 2, 424–446. [Google Scholar] [CrossRef]
  51. Mukul, S.A.; Byg, A. What Determines Indigenous Chepang Farmers’ Swidden Land-Use Decisions in the Central Hill Districts of Nepal? Sustainability 2020, 12, 5326. [Google Scholar] [CrossRef]
  52. Dove, M.R. Theories of Swidden Agriculture, and the Political Economy of Ignorance. Agrofor. Syst. 1983, 1, 85–99. [Google Scholar] [CrossRef]
  53. Bhattarai, B.R.; Wright, W.; Poudel, B.S.; Aryal, A.; Yadav, B.P.; Wagle, R. Shifting Paradigms for Nepal’s Protected Areas: History, Challenges and Relationships. J. Mt. Sci. 2017, 14, 964–979. [Google Scholar] [CrossRef]
  54. Gilmour, D.A.; King, G.C.; Hobley, M. Management of Forests for Local Use in the Hills of Nepal-I: Changing Forest Management Paradigms. J. World For. Resour. Manag. 1989, 4, 93–110. [Google Scholar]
  55. HMGN, (His Majesty’s Government of Nepal). Master Plan for Forestry Sector; Ministry of Forest: Kathmandu, Nepal, 1988. [Google Scholar]
  56. Griffin, D.M. Innocents Abroad in the Forests of Nepal: An Account of Australian Aid to Nepalese Forestry; Anutech: Canberra, Australia, 1988; ISBN 0-86420-001-3. [Google Scholar]
  57. Shrestha, U.B.; Shrestha, B.B.; Shrestha, S. Biodiversity Conservation in Community Forests of Nepal: Rhetoric and Reality. Int. J. Biodivers. Conserv. 2010, 2, 98–104. [Google Scholar]
  58. Niraula, R.R.; Gilani, H.; Pokharel, B.K.; Qamer, F.M. Measuring Impacts of Community Forestry Program through Repeat Photography and Satellite Remote Sensing in the Dolakha District of Nepal. J. Environ. Manag. 2013, 126, 20–29. [Google Scholar] [CrossRef]
  59. Acharya, K.P. Does Community Forests Management Supports Biodiversity Conservation? Evidences from Two Community Forests from the Mid Hills of Nepal. J. For. Livelihood 2004, 4, 44–54. [Google Scholar]
  60. Yadav, N.P.; Yadav, K.P.; Yadav, K.K.; Thapa, N. Facilitating the Transition from Passive to Active Community Forest Management: Lessons from Rapti Zone, Nepal. J. For. Livelihood 2009, 8, 51–66. [Google Scholar] [CrossRef][Green Version]
  61. Banjade, M.R. Discourse and Discursive Practices over Timber in Nepal. J. For. Livelihood 2012, 10, 58–73. [Google Scholar] [CrossRef][Green Version]
  62. Sharma, B.P.; Lawry, S.; Paudel, N.S.; McLain, R.; Adhikary, A.; Banjade, M.R. Operationalizing a Framework for Assessing the Enabling Environment for Community Forest Enterprises: A Case Study from Nepal. Small-Scale For. 2020, 19, 83–106. [Google Scholar] [CrossRef][Green Version]
  63. Ojha, H.R. Silviculture in Community Forestry: Conceptual and Practical Issues Emerging from the Middle Hills of Nepal. Banko Janakari 2001, 11, 20–23. [Google Scholar] [CrossRef][Green Version]
  64. Pokharel, R. Assessing Community Forests’ Condition Using Variables Recommended by Local People: A Case of Kaski District, Nepal. Banko Janakari 2005, 15, 40–48. [Google Scholar] [CrossRef][Green Version]
  65. Hunt, S.; Dangal, S.; Shrestha, S. Minimizing the Cost of Overstocking, towards a Thinning Regime for Community-Managed Pine Plantations in the Central Hills of Nepal. J. For. Livelihood 2001, 11–13. [Google Scholar]
  66. Webb, E.L.; Gautam, A.P. Effects of Community Forest Management on the Structure and Diversity of a Successional Broadleaf Forest in Nepal. Int. For. Rev. 2001, 3, 146–157. [Google Scholar]
  67. Acharya, K.P. Twenty-Four Years of Community Forestry in Nepal. Int. For. Rev. 2002, 4, 149–156. [Google Scholar] [CrossRef]
  68. Kanel, K.R.; Dahal, G.R. Community Forestry Policy and Its Economic Implications: An Experience from Nepal. Int. J. Soc. For. 2008, 1, 50–60. [Google Scholar]
  69. Pokharel, B.K.; Branney, P.; Nurse, M.; Malla, Y.B. Community Forestry: Conserving Forests, Sustaining Livelihoods and Strengthening Democracy. J. For. Livelihood 2007, 6, 8–19. [Google Scholar]
  70. Sharma, B.; Nepal, S.; Gyawali, D.; Pokharel, G.S.; Wahid, S.; Mukherji, A.; Acharya, S.; Shrestha, A.B. Springs, Storage Towers, and Water Conservation in the Midhills of Nepal; International Centre for Integrated Mountain Development: Lalitpur, Nepal, 2016; ISBN 92-9115-395-8. [Google Scholar]
  71. Gopali, B.; Nepali, D.B. अवैज्ञानिक छ वैज्ञानिक वन व्यवस्थापन (Scientific Forest Management Is Unscientific). Naya Patrika. 2021. Available online: https://www.nayapatrikadaily.com/news-details/70197/2021-09-05 (accessed on 13 February 2022).
  72. White, K.J. Organisation and Management Practices for the Sagarnath Project of Central Nepal. Man.-Sagarnath For. Dev. Proj. Minist. For. Nepal 1986. [Google Scholar]
  73. Gilmour, D.; King, G.; Applegate, G.; Mohns, B. Silviculture of Plantation Forest in Central Nepal to Maximise Community Benefits. For. Ecol. Manag. 1990, 32, 173–186. [Google Scholar] [CrossRef]
  74. Rautiainen, O.; Suoheimo, J. Natural Regeneration Potential and Early Development of Shorea Robusta Gaertn. f. Forest after Regeneration Felling in the Bhabar-Terai Zone in Nepal. For. Ecol. Manag. 1997, 92, 243–251. [Google Scholar] [CrossRef]
  75. Tamrakar, P.; Danbury, D. Silviculture by Rural People in the Middle Hills of Nepal. Banko Janakari 1997, 7, 9–16. [Google Scholar] [CrossRef][Green Version]
  76. Ojha, S.; Acharya, K.; Acharya, B.; Regmi, R. Simple Coppice Management Options for the Sal (Shorea Robusta Gaertn. f.) Forests in the Terai of Nepal. Banko Janakari 2008, 18, 32–41. [Google Scholar] [CrossRef][Green Version]
  77. Acharya, B.; Acharya, K. A Preliminary Result on Simple Coppice Management of Sal (Shorea Robusta) Forests of Nepal. Banko Janakari 2004, 14, 51–53. [Google Scholar] [CrossRef][Green Version]
  78. Acharya, K.; Tamrakar, P.; Gautam, G.; Regmi, R.; Adhikari, A.; Acharya, B. Managing Tropical Sal Forests (Shorea Robusta) in Nepal in Short Rotations: Findings of a 12-Year Long Research. Banko Janakari 2002, 12, 71–75. [Google Scholar] [CrossRef][Green Version]
  79. Laudari, H.K.; Aryal, K.; Maraseni, T. A Postmortem of Forest Policy Dynamics of Nepal. Land Use Policy 2020, 91, 104338. [Google Scholar] [CrossRef]
  80. Paudel, N.S.; Ojha, H.; Shrestha, K.; Cedamon, E.; Karki, R.; Paudel, G.; Basyal, M.; Nuberg, I.; Dangal, S. Towards Active Utilisation of Community Forestry: Silvo-Institutional Model for Sustainable Forest Management in Nepal. Banko Janakari 2018, 4, 120–129. [Google Scholar] [CrossRef]
  81. Baral, S.; Hansen, C.P.; Chhetri, B.B.K. Forest Management Plans in Nepal’s Community Forests: Does One Size Fit All? Small-Scale For. 2020, 19, 483–504. [Google Scholar] [CrossRef]
  82. Baral, S.; Meilby, H.; Chhetri, B. The Contested Role of Management Plans in Improving Forest Conditions in Nepal’s Community Forests. Int. For. Rev. 2019, 21, 37–50. [Google Scholar] [CrossRef]
  83. Baral, S.G.; Vacik, H.; Chhetri, B.B.K.; Gauli, K. The Pertinent Role of Forest Inventory in Making Choice of Silvicultural Operations in Community Forests of Nepal. Banko Janakari 2018, 27, 65–75. [Google Scholar] [CrossRef]
  84. Baral, S.; Meilby, H.; Chettri, B.B.K.; Basnyat, B.; Rayamajhi, S.; Awale, S. Politics of Getting the Numbers Right: Community Forest Inventory of Nepal. For. Policy Econ. 2018, 91, 19–26. [Google Scholar] [CrossRef]
  85. Baral, S.; Vacik, H. What Governs Tree Harvesting in Community Forestry—Regulatory Instruments or Forest Bureaucrats’ Discretion? Forests 2018, 9, 649. [Google Scholar] [CrossRef][Green Version]
  86. Kanel, K.R.; Kandel, B.R. Community Forestry in Nepal: Achievements and Challenges. J. For. Livelihood 2004, 4, 55–63. [Google Scholar]
  87. Cedamon, E.; Nuberg, I.; Paudel, G.; Basyal, M.; Shrestha, K.; Paudel, N. Rapid Silviculture Appraisal to Characterise Stand and Determine Silviculture Priorities of Community Forests in Nepal. Small-Scale For. 2017, 16, 195–218. [Google Scholar] [CrossRef]
  88. Gurung, A.; Bista, R.; Karki, R.; Shrestha, S.; Uprety, D.; Oh, S.-E. Community-Based Forest Management and Its Role in Improving Forest Conditions in Nepal. Small-Scale For. 2013, 12, 377–388. [Google Scholar] [CrossRef]
  89. KC, A.; Manandhar, R.; Paudel, R.; Ghimire, S. Increase of Forest Carbon Biomass Due to Community Forestry Management in Nepal. J. For. Res. 2018, 29, 429–438. [Google Scholar]
  90. Paudel, S.; Sah, J.P. Effects of Different Management Practices on Stand Composition and Species Diversity in Subtropical Forests in Nepal: Implications of Community Participation in Biodiversity Conservation. J. Sustain. For. 2015, 34, 738–760. [Google Scholar] [CrossRef]
  91. Poudyal, B.H.; Maraseni, T.; Cockfield, G. Impacts of Forest Management on Tree Species Richness and Composition: Assessment of Forest Management Regimes in Tarai Landscape Nepal. Appl. Geogr. 2019, 111, 102078. [Google Scholar] [CrossRef]
  92. Baral, S.; Gautam, A.P.; Vacik, H. Ecological and Economical Sustainability Assessment of Community Forest Management in Nepal: A Reality Check. J. Sustain. For. 2018, 37, 820–841. [Google Scholar] [CrossRef]
  93. Pandey, S.S.; Maraseni, T.N.; Cockfield, G.; Gerhard, K. Tree Species Diversity in Community Managed and National Park Forests in the Mid-Hills of Central Nepal. J. Sustain. For. 2014, 33, 796–813. [Google Scholar] [CrossRef]
  94. Radu, S. The Ecological Role of Deadwood in Natural Forests. In Nature Conservation; Springer: Berlin/Heidelberg, Germany, 2006; pp. 137–141. [Google Scholar]
  95. Franklin, J.F.; Shugart, H.H.; Harmon, M.E. Tree Death as an Ecological Process. BioScience 1987, 37, 550–556. [Google Scholar] [CrossRef]
  96. Hagan, J.M.; Grove, S.L. Coarse Woody Debris: Humans and Nature Competing for Trees. J. For. 1999, 97, 6–11. [Google Scholar] [CrossRef]
  97. Jia-bing, W.; De-xin, G.; Shi-jie, H.; Mi, Z.; Chang-jie, J. Ecological Functions of Coarse Woody Debris in Forest Ecosystem. J. For. Res. 2005, 16, 247–252. [Google Scholar] [CrossRef]
  98. Cedamon, E.; Paudel, G.; Basyal, M.; Nuberg, I.; Shrestha, K. Applications of Single-Tree Selection Guideline Following a DBq Approach on Nepal’s Community Forests. Banko Janakari 2018, 27, 104–112. [Google Scholar] [CrossRef]
  99. Poudyal, B.H.; Maraseni, T.; Cockfield, G. An Assessment of the Policies and Practices of Selective Logging and Timber Utilisation: A Case Study from Natural Forests of Tarai Nepal and Queensland Australia. Land Use Policy 2020, 91, 104422. [Google Scholar] [CrossRef]
  100. Sapkota, I.P.; Tigabu, M.; Odén, P.C. Species Diversity and Regeneration of Old-Growth Seasonally Dry Shorea Robusta Forests Following Gap Formation. J. For. Res. 2009, 20, 7–14. [Google Scholar] [CrossRef]
  101. Acharya, K. Unfavourable Structure of Forests in the Terai Needs Immediate Management. Banko Janakari 2000, 10, 25–28. [Google Scholar] [CrossRef]
  102. Chand, N.; Kerr, G.N.; Bigsby, H. Production Efficiency of Community Forest Management in Nepal. For. Policy Econ. 2015, 50, 172–179. [Google Scholar] [CrossRef]
  103. Paudel, G.; Paudel, N.S.; Khatri, D.B. Revenue and Employment Opportunities from Timber Management in Nepal’s Community Forests. In Report of the Sixth National Community Forest Seminar; Available online: https://www.researchgate.net/publication/313163112_Revenue_and_employment_opportunities_from_timber_management_in_Nepal's_community_forests (accessed on 13 February 2022)2017.
  104. Puri, L.; Nuberg, I.; Ostendorf, B.; Cedamon, E. Locally Perceived Social and Biophysical Factors Shaping the Effective Implementation of Community Forest Management Operations in Nepal. Small-Scale For. 2020, 19, 291–317. [Google Scholar] [CrossRef]
  105. Rai, R.; Neupane, P.; Dhakal, A. Is the Contribution of Community Forest Users Financially Efficient? A Household Level Benefit-Cost Analysis of Community Forest Management in Nepal. Int. J. Commons 2016, 10, 142–157. [Google Scholar]
  106. Joshi, O.; Parajuli, R.; Kharel, G.; Poudyal, N.C.; Taylor, E. Stakeholder Opinions on Scientific Forest Management Policy Implementation in Nepal. PLoS ONE 2018, 13, e0203106. [Google Scholar] [CrossRef]
  107. Poudyal, B.H.; Maraseni, T.; Cockfield, G. Scientific Forest Management Practice in Nepal: Critical Reflections from Stakeholders’ Perspectives. Forests 2020, 11, 27. [Google Scholar] [CrossRef][Green Version]
  108. Jayasawal, D.; Bishwokarma, D. Scientific Forest Management Initiatives in Nepal; Multi Stakeholder Forestry Program: Kathmandu, Nepal, 2016. [Google Scholar]
  109. Media Journal. दिगो वन व्यावस्थापनका लागि वैज्ञानिक वन व्यावस्थापन Scientific Forest Management (Documentary). 2020. Available online: https://www.youtube.com/watch?v=NM0_Wrct7Ec (accessed on 13 February 2022).
  110. MoFSC, (Ministry of Forests and Soil Conservation). वैज्ञानिक वन व्यवस्थापन कार्यविधि, २०७१ (Scientifc Forest Management Guideline, 2014); 2014. [Google Scholar]
  111. Bhattarai, B.P.; Poudyal, B.H.; Acharya, R.P.; Maraseni, T. Policy and Governance Issues in Timber Harvesting: A Case Study of Collaborative Forest in Nepal. In Proceedings of the Wild Harvests, Governance, and Livelihoods in Asia, Kathmandu, Nepal, 30 November–2 December 2017; p. 186. [Google Scholar]
  112. Awasthi, N.; Aryal, K.; Chhetri, B.B.K.; Bhandari, S.K.; Khanal, Y.; Gotame, P.; Baral, K. Reflecting on Species Diversity and Regeneration Dynamics of Scientific Forest Management Practices in Nepal. For. Ecol. Manag. 2020, 474, 118378. [Google Scholar] [CrossRef]
  113. Bhandari, B. वैज्ञानिक वन व्यवस्थापनले सुके पानीका स्रोत (Water Springs Dry After Scientific Forest Management). Ekantipur 2019. [Google Scholar]
  114. Poudyal, B.H.; Khatri, D.B. (अ)वैज्ञानिक वन व्यवस्थापनले गुम्दैछ समुदायको अधिकार (Communities Are Losing Their Rights Because of (Un)Scientific Forest Management). Himal Khabar, 2020. Available online: https://www.himalkhabar.com/news/118717?fbclid=IwAR0zYh7QGLp9zKReT-D2V7wzO4WR733aGhzN5fisZpF7T0QQWGZlVzC4oR0 (accessed on 13 February 2022).
  115. Sharma, L.N.; Paudel, N.S. वैज्ञानिक वन व्यवस्थापनमा जैविक विविधताका केही सवालहरु (Some Questions Regarding Biodiversity in Scientific Forest Management). Setopati 2020. [Google Scholar]
  116. Basnyat, B.; Treue, T.; Pokharel, R. Silvicultural Madness: A Case from the “Scientific Forestry” Initiative in the Community Forests of Nepal. Banko Janakari 2018, 27, 54–64. [Google Scholar] [CrossRef]
  117. Bhandari, B. वैज्ञानिक वन व्यवस्थापन: पुराना झिक्दै, नयाँ रोप्दै (Scientific Forest Management: Taking out Old Trees, Planting New Ones). Ekantipur, 2020. Available online: https://ekantipur.com/pradesh-1/2020/01/28/15801830910935831.html (accessed on 2 December 2021).
  118. Bhandari, T. वन व्यवस्थापनमा सामुदायिक वन उपभोक्ता महासंघ, नेपालको धारणा (FECOFUN’s (Federation of Community Forest Users, Nepal) Statement of Opinion on Forest Management). In Proceedings of the First National Silviculture Workshop, Kathmandu, Nepal, 19–21 February 2017; pp. 498–501. [Google Scholar]
  119. Ashton, M.S.; Kelty, M.J. The Practice of Silviculture: Applied Forest Ecology; John Wiley & Sons: Hoboken, NJ, USA, 2018; ISBN 1-119-27095-2. [Google Scholar]
  120. DoF, (Department of Forests). DoF, (Department of Forests). Silviculture for Forest Management. In Proceedings of the First National Silviculture Workshop, Kathmandu, Nepal, 19–21 February 2017. [Google Scholar]
  121. Baral, K.; Subedi, K.; Ghimire, K. Scientific Forest Management: Experience of Kaski District, Nepal. In Proceedings of the First National Silviculture Workshop, Kathmandu, Nepal, 19–21 February 2017; pp. 123–131. [Google Scholar]
  122. Khanal, Y.; Adhikari, S. Regeneration Promotion and Income Generation through Scientific Forest Management in Community Forestry: A Case Study from Rupandehi District, Nepal. Banko Janakari 2018, 27, 45–53. [Google Scholar] [CrossRef]
  123. Timsina, N.P.; Shah, R.; Karna, A.L.; Rajbhandari, K.; Dhungana, S.P. नीतिगत, कानुनी र संस्थागत सुधार बारे सिफारिस: राष्ट्रिय वन क्षेत्रमा अनुचित रुपमा साल लगायतका विभिन्न रुखहरु कटान, मुछान, संकलन तथा ओसारपसार गरी वन विनास भएको भन्ने सम्बन्धमा छानविन गर्न नेपाल सरकार (मन्त्रिपरिषद्)बाट गठित उच्चस्तरीय समितिको प्रतिवेदन (Recommendations for Policy, Legal and Institutional Improvement: A Report by the High-Level Committee Formed by the Cabinet of the Government of Nepal to Investigate the Deforestation Attributed to Undue Logging, Bucking, Collection and Transportation of Various Tree Species, Including Sal, in National Forest Areas); 2020. [Google Scholar]
  124. Modak, N.; Poudyal, A.S. Potentials and Challenges of Scientific Forest Management in Community Forest in Nawalparasi District, Nepal. In Proceedings of the Wild Harvests, Governance, and Livelihoods in Asia, Kathmandu, Nepal, 30 November–2 December 2017; p. 61. [Google Scholar]
  125. Bhusal, P.; Awasthi, K.R.; Kimengsi, J.N. User’s Opinion in Scientific Forest Management Implementation in Nepal–a Case Study from Nawalparasi District. Cogent Environ. Sci. 2020, 6, 1778987. [Google Scholar] [CrossRef]
  126. Paudel, G.; Bhusal, P.; Kimengsi, J.N. Determining the Costs and Benefits of Scientific Forest Management in Nepal. For. Policy Econ. 2021, 126, 102426. [Google Scholar] [CrossRef]
  127. Onlinekhabar. वैज्ञानिक वन तस्करको धन भयो,५० औं अर्ब रुपैया खोइ ?भारती पाठक, अध्यक्ष सामुदायिक वन उपभोक्ता महासंघ (Scientific Forest Management Has Become a Source of Wealth for Smugglers, Where Are the Billions of Rupees? Bharati Pathak, President, Federation of Community Forest Users, Nepal). 2020. Available online: https://www.himalkhabar.com/news/12526 (accessed on 13 February 2022).
  128. Bhatta, S. वैज्ञानिक वनमा नक्कली उपभोक्ता (Fake Consumers in Scientific Forests). Annapurna Post. Available online: http://annapurnapost.com/news/161178 (accessed on 13 February 2022).
  129. Kantipur. “वैज्ञानिक वन नीति सही, कार्यान्वयनमा केही बदमासी देखियो” (‘Scientific Forest Management Policy is Good, but there are Irregularities in Implementation’). 2020. Available online: https://ekantipur.com/news/2020/09/24/16009399190726545.html?author=1 (accessed on 13 February 2022).
  130. Kantipur. वैज्ञानिक वन व्यवस्थापन कार्यविधि खारेज गर्न सिफारिस (Recommendation to dissolve Scientific Forest Management); Kantipur; 2020. Available online: https://ekantipur.com/news/2020/09/24/16009399190726545.html (accessed on 13 February 2022).
  131. Basnyat, B. Commodifying the Community Forestry: A Case from Scientific Forestry Practices in Western Hills of Nepal. J. For. Res. 2020, 25, 69–75. [Google Scholar] [CrossRef]
  132. Kantipur. वैज्ञानिक वन व्यवस्थापनका नाममा कार्यविधि विपरीत फडानी गरेको भन्दै छानबिन गर्न संसदीय उपसमिति गठन (Parliamentary Sub-Committee Formed to Investigate Forest Clearance in the Name of Scientific Forest Management, Contrary to the Guidlines). 2020. Available online: https://ekantipur.com/news/2020/06/19/15925637072709211.html (accessed on 13 February 2022).
  133. GoN, (Government of Nepal). In Decisions Made by the Cabinet Meeting on 2077 B.S. Magh 11 (2021 January 24); 24 January 2021.
  134. Mahara, J. वैज्ञानिक वन छानबिनको प्रतिस्पर्धा र विवादमा दुई संसदीय समिति (Two Parliamentary Committees in Debate and Competition over Investigating Scientific Forest Management); Kantipur; 2020.
  135. Miyan, A. वैज्ञानिक वन: छानबिनमाथि छानबिन (Multiple Investigations into Scientific Forest Management). Kantipur, 2020. Available online: https://ekantipur.com/news/2020/07/27/159585302418499511.html (accessed on 13 February 2022).
  136. MoFSC, (Ministry of Forests and Soil Conservation). वन नियामवली (Forest Regulation); 1995. [Google Scholar]
  137. Pathak, B. वैज्ञानिक वन व्यवस्थापनका चुनौती (Challenges Associated with Scientific Forest Management). Annapurna Post, 2019. Available online: https://setikalinews.com/news-details/752/2020-06-03 (accessed on 13 February 2022).
  138. Hansen, C.P.; Lund, J.F. Imagined Forestry: The History of the Scientific Management of Ghana’s High Forest Zone. Environ. Hist. 2017, 23, 3–38. [Google Scholar] [CrossRef]
  139. Hölzl, R. Historicizing Sustainability: German Scientific Forestry in the Eighteenth and Nineteenth Centuries. Sci. Cult. 2010, 19, 431–460. [Google Scholar] [CrossRef]
  140. Gilmour, D. Silviculture and Community Forestry: Looking Backwards, Looking Forwards. Banko Janakari 2018, 27, 6–14. [Google Scholar] [CrossRef]
  141. Martinez, D. Traditional Ecological Knowledge, Traditional Resource Management and Silviculture in Ecocultural Restoration of Temperate Forests. In Genetic Considerations in Ecosystem Restoration Using Native Tree Species; Food and Agriculture Organization of the United Nations: Rome, Italy, 2014; p. 109. [Google Scholar]
  142. Worster, D. The Wealth of Nature: Environmental History and the Ecological Imagination. Oxford University Press: New York, NY, USA, 1993; ISBN 0-19-509264-3. [Google Scholar]
  143. Fredericksen, T.S. Limitations of Low-Intensity Selection and Selective Logging for Sustainable Tropical Forestry. Commonw. For. Rev. 1998, 77, 262–266. [Google Scholar]
  144. O’Hara, K.L. The Historical Development of Uneven-aged Silviculture in North America. Forestry 2002, 75, 339–346. [Google Scholar] [CrossRef]
  145. Swanson, M.E.; Franklin, J.F.; Beschta, R.L.; Crisafulli, C.M.; DellaSala, D.A.; Hutto, R.L.; Lindenmayer, D.B.; Swanson, F.J. The Forgotten Stage of Forest Succession: Early-successional Ecosystems on Forest Sites. Front. Ecol. Environ. 2011, 9, 117–125. [Google Scholar] [CrossRef][Green Version]
  146. Lindenmayer, D.B.; Westgate, M.J.; Scheele, B.C.; Foster, C.N.; Blair, D.P. Key Perspectives on Early Successional Forests Subject to Stand-Replacing Disturbances. For. Ecol. Manag. 2019, 454, 117656. [Google Scholar] [CrossRef]
  147. Keye, W.W. My Chance: The Relentless Spread of Forest Protectionism. J. For. 1992, 90, 56. [Google Scholar]
  148. Erickson, C.L. Amazonia: The Historical Ecology of a Domesticated Landscape. In The handbook of South American archaeology; Springer: Berlin/Heidelberg, Germany, 2008; pp. 157–183. [Google Scholar]
  149. Peters, C.M. Managing the Wild: Stories of People and Plants and Tropical Forests; Yale University Press: New Haven, CT, USA; London, UK, 2018; ISBN 0-300-23552-6. [Google Scholar]
  150. Miehe, G.; Pendry, C.; Chaudhary, R. Nepal: An Introduction to the Natural History, Ecology and Human Environment of the Himalayas. A Companion to the Flora of Nepal; Royal Botanic Garden Edinburgh: Edinburgh, UK, 2017. [Google Scholar]
  151. Sapkota, I. Species Diversity, Regeneration and Early Growth of Sal Forests in Nepal; Swedish University of Agricultural Sciences: Alnarp, Sweden, 2009; ISBN 91-576-7438-8. [Google Scholar]
  152. Cedamon, E.; Bardsley, D.; Nuberg, I. Changing Forestry Interests in Nepal Midhills: Implications for Silviculture Policy and Practice. 2022; In Writing. [Google Scholar]
  153. Başkent, E. A Review of the Development of the Multiple Use Forest Management Planning Concept. Int. For. Rev. 2018, 20, 296–313. [Google Scholar] [CrossRef]
  154. Sabogal, C.; Guariguata, M.; Broadhead, J.; Lescuyer, G.; Savilaakso, S.; Essoungou, J.N.; Sist, P. Multiple-Use Forest Management in the Humid Tropics: Opportunities and Challenges for Sustainable Forest Management; FAO Forestry Paper No. 173; Food and Agriculture Organization of the United Nations: Rome, Italy, 2013. [Google Scholar]
  155. Bonsu, N.O.; Dhubháin, Á.N.; O’connor, D. Evaluating the Use of an Integrated Forest Land-Use Planning Approach in Addressing Forest Ecosystem Services Conflicting Demands: Experience within an Irish Forest Landscape. Futures 2017, 86, 1–17. [Google Scholar] [CrossRef]
  156. Cairns, M.A.; Meganck, R.A. Carbon Sequestration, Biological Diversity, and Sustainable Development: Integrated Forest Management. Environ. Manag. 1994, 18, 13–22. [Google Scholar] [CrossRef]
  157. Maier, C.; Winkel, G. Implementing Nature Conservation through Integrated Forest Management: A Street-Level Bureaucracy Perspective on the German Public Forest Sector. For. Policy Econ. 2017, 82, 14–29. [Google Scholar] [CrossRef]
  158. Peters, C.M. Precolumbian Silviculture and Indigenous Management of Neotropical Forests. In Imperfect Balance; Columbia University Press: New York, NY, USA, 2000; pp. 203–224. ISBN 0-231-50551-5. [Google Scholar]
  159. Emery, M.R.; Zasada, J. Silviculture and Nontimber Forest Products: Extending the Benefits of Forest Management. In The Timberline; Northern Research Station: Madison, WI, USA, 2001; pp. 10–13. [Google Scholar]
  160. Rutt, R.L.; Chhetri, B.B.K.; Pokharel, R.; Rayamajhi, S.; Tiwari, K.; Treue, T. The Scientific Framing of Forestry Decentralization in Nepal. For. Policy Econ. 2015, 60, 50–61. [Google Scholar] [CrossRef]
  161. Kelty, M.J.; Larson, B.C.; Oliver, C.D. The Ecology and Silviculture of Mixed-Species Forests: A Festschrift for David M. Smith; Springer Science+Business Media: Dordrecht, Netherlands, 1992; ISBN 978-90-481-4135-7. [Google Scholar]
  162. Vanclay, J.K. Growth Modelling and Yield Prediction for Sustainable Forest Management. Malays. For. 2003, 66, 58–69. [Google Scholar]
  163. Klooster, D.J. Toward Adaptive Community Forest Management: Integrating Local Forest Knowledge with Scientific Forestry. Econ. Geogr. 2002, 78, 43–70. [Google Scholar] [CrossRef]
  164. Okubo, S.; Tomatsu, A.; Muhamad, D.; Harashina, K.; Takeuchi, K. Leaf Functional Traits and Functional Diversity of Multistoried Agroforests in West Java, Indonesia. Agric. Ecosyst. Environ. 2012, 149, 91–99. [Google Scholar] [CrossRef]
  165. Salek, L.; Sivacioğlu, A. Forests for Future–Multifunctional Forests. Int. J. Plant Soil Sci. 2018, 24. [Google Scholar] [CrossRef]
  166. Haas, S.E.; Hall Cushman, J.; Dillon, W.W.; Rank, N.E.; Rizzo, D.M.; Meentemeyer, R.K. Effects of Individual, Community, and Landscape Drivers on the Dynamics of a Wildland Forest Epidemic. Ecology 2016, 97, 649–660. [Google Scholar] [CrossRef]
  167. Thompson, I. Biodiversity, Ecosystem Thresholds, Resilience and Forest Degradation. Unasylva 2011, 238, 25–30. [Google Scholar]
  168. Huang, X.; Su, J.; Li, S.; Liu, W.; Lang, X. Functional Diversity Drives Ecosystem Multifunctionality in a Pinus Yunnanensis Natural Secondary Forest. Sci. Rep. 2019, 9, 6979. [Google Scholar] [CrossRef][Green Version]
  169. Messier, C.; Bauhus, J.; Doyon, F.; Maure, F.; Sousa-Silva, R.; Nolet, P.; Mina, M.; Aquilué, N.; Fortin, M.-J.; Puettmann, K. The Functional Complex Network Approach to Foster Forest Resilience to Global Changes. For. Ecosyst. 2019, 6, 21. [Google Scholar] [CrossRef][Green Version]
  170. Seymour, R.S.; Hunter, M.L., Jr. Principles of Ecological Forestry. In Maintaining Biodiversity in Forest Ecosystems; Cambridge University Press: Cambridge, UK, 1999; pp. 22–64. [Google Scholar]
  171. Palik, B.J.; D’Amato, A.W. Ecological Forestry: Much More than Retention Harvesting. J. For. 2017, 115, 51–53. [Google Scholar] [CrossRef]
  172. Franklin, J.F.; Mitchell, R.J.; Palik, B.J. Natural Disturbance and Stand Development Principles for Ecological Forestry; Gen. Tech. Rep. NRS-19; U.S. Department of Agriculture, Forest Service, Northern Research Station: Newtown Square, PA, USA, 2007; Volume 19, 44p.
  173. Seymour, R.S.; Hunter, M.L. New Forestry in Eastern Spruce-Fir Forests: Principles and Applications to Maine; College of Forest Resources, University of Maine: Orono, ME, USA, 1992; Volume 716. [Google Scholar]
  174. Royer-Tardif, S.; Bauhus, J.; Doyon, F.; Nolet, P.; Thiffault, N.; Aubin, I. Revisiting the Functional Zoning Concept under Climate Change to Expand the Portfolio of Adaptation Options. Forests 2021, 12, 273. [Google Scholar] [CrossRef]
  175. Leitao, A.B.; Ahern, J. Applying Landscape Ecological Concepts and Metrics in Sustainable Landscape Planning. Landsc. Urban Plan. 2002, 59, 65–93. [Google Scholar] [CrossRef]
  176. Nielsen, T.D. From REDD+ Forests to Green Landscapes? Analyzing the Emerging Integrated Landscape Approach Discourse in the UNFCCC. For. Policy Econ. 2016, 73, 177–184. [Google Scholar] [CrossRef]
  177. Paul, E.A.; Robertson, G.P. Ecology and the Agricultural Sciences: A False Dichotomy? Ecology 1989, 70, 1594–1597. [Google Scholar] [CrossRef]
  178. Pandit, B.H.; Wagley, M.P.; Neupane, R.P.; Adhikary, B.R. Watershed Management and Livelihoods: Lessons from Nepal. J. For. Livelihood 2007, 6, 67–75. [Google Scholar]
  179. Awada, T.; Henebry, G.M.; Redmann, R.E.; Sulistiyowati, H. Picea Glauca Dynamics and Spatial Pattern of Seedlings Regeneration along a Chronosequence in the Mixedwood Section of the Boreal Forest. Ann. For. Sci. 2004, 61, 789–794. [Google Scholar] [CrossRef][Green Version]
  180. Saldarriaga, J.G.; West, D.C.; Tharp, M.; Uhl, C. Long-Term Chronosequence of Forest Succession in the Upper Rio Negro of Colombia and Venezuela. J. Ecol. 1988, 76, 938–958. [Google Scholar] [CrossRef]
  181. Martin, M.; Woodbury, D.; Glogower, Y.; Duguid, M.; Frey, B.; Ashton, M. Within-Gap Position Shapes Fifty Years of Forest Dynamics in a Temperate Hardwood Forest in Connecticut, USA. For. Ecol. Manag. 2021, 494, 119311. [Google Scholar] [CrossRef]
  182. Wikle, J.; Duguid, M.; Ashton, M.S. Legacy Forest Structures in Irregular Shelterwoods Differentially Affect Regeneration in a Temperate Hardwood Forest. For. Ecol. Manag. 2019, 454, 117650. [Google Scholar] [CrossRef]
  183. Pretzsch, H. Forest Dynamics, Growth, and Yield. In Forest Dynamics, Growth and Yield; Springer: Berlin/Heidelberg, Germany, 2009; pp. 1–39. [Google Scholar]
  184. Bastakoti, R.R.; Davidsen, C. Framing REDD+ at National Level: Actors and Discourse around Nepal’s Policy Debate. Forests 2017, 8, 57. [Google Scholar] [CrossRef][Green Version]
  185. Den Besten, J.W.; Arts, B.; Verkooijen, P. The Evolution of REDD+: An Analysis of Discursive-Institutional Dynamics. Environ. Sci. Policy 2014, 35, 40–48. [Google Scholar] [CrossRef]
  186. Poudel, M.; Thwaites, R.; Race, D.; Dahal, G.R. REDD+ and Community Forestry: Implications for Local Communities and Forest Management-a Case Study from Nepal. Int. For. Rev. 2014, 16, 39–54. [Google Scholar] [CrossRef][Green Version]
  187. Laudari, H.K.; Pant, B.; Timalsina, N.; Dhungana, S.P.; Poudel, M.; Karky, B.S. Decentralising REDD+: Lessons Learned from REDD+ Himalaya Project of Nepal. J. For. Livelihood 2018, 17, 1. [Google Scholar]
  188. Miyan, A. कार्बन बेचेर ४ वर्षमै ३६ अर्ब ल्याउने सम्झौता (Agreement to Sell Carbon and Receive 36 Billion Rupees within Four Years). Kantipur. 2021. Available online: https://ekantipur.com/news/2021/11/04/163598897646965776.html (accessed on 13 February 2022).
  189. Marzluff, J.M.; Millspaugh, J.J.; Ceder, K.R.; Oliver, C.D.; Withey, J.; McCarter, J.B.; Mason, C.; Comnick, J. Modeling Changes in Wildlife Habitat and Timber Revenues in Response to Forest Management. For. Sci. 2002, 48, 191–202. [Google Scholar]
  190. Motta, R.; Berretti, R.; Lingua, E.; Piussi, P. Coarse Woody Debris, Forest Structure and Regeneration in the Valbona Forest Reserve, Paneveggio, Italian Alps. For. Ecol. Manag. 2006, 235, 155–163. [Google Scholar] [CrossRef]
  191. Heinemann, K.; Kitzberger, T. Effects of Position, Understorey Vegetation and Coarse Woody Debris on Tree Regeneration in Two Environmentally Contrasting Forests of North-western Patagonia: A Manipulative Approach. J. Biogeogr. 2006, 33, 1357–1367. [Google Scholar] [CrossRef]
  192. Bolton, N.W.; D’Amato, A.W. Regeneration Responses to Gap Size and Coarse Woody Debris within Natural Disturbance-Based Silvicultural Systems in Northeastern Minnesota, USA. For. Ecol. Manag. 2011, 262, 1215–1222. [Google Scholar] [CrossRef]
  193. Fritz, Ö.; Gustafsson, L.; Larsson, K. Does Forest Continuity Matter in Conservation?–A Study of Epiphytic Lichens and Bryophytes in Beech Forests of Southern Sweden. Biol. Conserv. 2008, 141, 655–668. [Google Scholar] [CrossRef]
  194. Hottola, J.; Ovaskainen, O.; Hanski, I. A Unified Measure of the Number, Volume and Diversity of Dead Trees and the Response of Fungal Communities. J. Ecol. 2009, 97, 1320–1328. [Google Scholar] [CrossRef]
  195. Santiago, M.J.; Rodewald, A.D. Dead Trees as Resources for Forest Wildlife. Extension Fact Sheet; Ohio State University Extension: Columbus, OH, USA; 15.
  196. Meadows, J.S. Epicormic Branches and Lumber Grade of Bottomland Oak. In Proceedings of the Twenty-Third Annual Hardwood Symposium: Advances in Hardwood Utilization: Following Profitability from the Woods through Rough Dimension, Cashiers, NC, USA, 17–20 May 1995; Lowery, G., Meyer, D., Eds.; National Hardwood Lumber Association: Memphis, TN, USA, 1995; pp. 19–25.
  197. Asner, G.P.; Knapp, D.E.; Broadbent, E.N.; Oliveira, P.J.; Keller, M.; Silva, J.N. Selective Logging in the Brazilian Amazon. Science 2005, 310, 480–482. [Google Scholar] [CrossRef]
  198. Hardiansyah, G.; Hardjanto, T.; Mulyana, M. A Brief Note on TPTJ (Tebang Pilih Dan Tanam Jalur), a Modified Indonesia Selective Cutting System, from Experience of PT Sari Bumi Kusuma Timber Concessionaire. In Permanent Sample Slots; Center for International Forestry Research: Bogor, Indonesia, 2006; p. 23. [Google Scholar]
  199. Ng, K.K.S.; Lee, S.L.; Ueno, S. Impact of Selective Logging on Genetic Diversity of Two Tropical Tree Species with Contrasting Breeding Systems Using Direct Comparison and Simulation Methods. For. Ecol. Manag. 2009, 257, 107–116. [Google Scholar] [CrossRef]
  200. Sebbenn, A.M.; Degen, B.; Azevedo, V.C.; Silva, M.B.; de Lacerda, A.E.; Ciampi, A.Y.; Kanashiro, M.; da Carneiro, F.S.; Thompson, I.; Loveless, M.D. Modelling the Long-Term Impacts of Selective Logging on Genetic Diversity and Demographic Structure of Four Tropical Tree Species in the Amazon Forest. For. Ecol. Manag. 2008, 254, 335–349. [Google Scholar] [CrossRef][Green Version]
  201. Hall, J.S.; Harris, D.J.; Medjibe, V.; Ashton, P.M.S. The Effects of Selective Logging on Forest Structure and Tree Species Composition in a Central African Forest: Implications for Management of Conservation Areas. For. Ecol. Manag. 2003, 183, 249–264. [Google Scholar] [CrossRef]
  202. Dahal, B.R.; McAlpine, C.A.; Maron, M. Impacts of Extractive Forest Uses on Bird Assemblages Vary with Landscape Context in Lowland Nepal. Biol. Conserv. 2015, 186, 167–175. [Google Scholar] [CrossRef]
  203. Gautam, T.P.; Mandal, T.N. Effect of Disturbance on Biomass, Production and Carbon Dynamics in Moist Tropical Forest of Eastern Nepal. For. Ecosyst. 2016, 3. [Google Scholar] [CrossRef][Green Version]
  204. Oli, B.N.; Subedi, M.R. Effects of Management Activities on Vegetation Diversity, Dispersion Pattern and Stand Structure of Community-Managed Forest (Shorea Robusta) in Nepal. Int. J. Biodivers. Sci. Ecosyst. Serv. Manag. 2015, 11, 96–105. [Google Scholar] [CrossRef]
  205. Timilsina, N.; Ross, M.S.; Heinen, J.T. A Community Analysis of Sal (Shorea Robusta) Forests in the Western Terai of Nepal. For. Ecol. Manag. 2007, 241, 223–234. [Google Scholar] [CrossRef]
  206. Sapkota, L. Ecology and Management Issues of Mikania Micrantha in Chitwan Naitonal Park, Nepal. Banko Janakari 2007, 17, 27–39. [Google Scholar] [CrossRef][Green Version]
  207. Joshi, C. Mapping Cryptic Invaders and Invaisability of Tropical Forest Ecosystems: Chromolaena Odorata in Nepal; International Institute for Geo-information Science & Earth Observation: Enschede, The Netherlands, 2006; ISBN 90-8504-470-7. [Google Scholar]
  208. Khaniya, L.; Shrestha, B.B. Forest Regrowth Reduces Richness and Abundance of Invasive Alien Plant Species in Community Managed Shorea Robusta Forests of Central Nepal. J. Ecol. Environ. 2020, 44. [Google Scholar] [CrossRef]
Figure 1. A historical timeline depicting the major events and outlooks prevalent in public forest management in Nepal. The width of the bars shows the relative spatial area across which an activity or approach was implemented.
Figure 1. A historical timeline depicting the major events and outlooks prevalent in public forest management in Nepal. The width of the bars shows the relative spatial area across which an activity or approach was implemented.
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Figure 2. Pathways to convert pine plantations to natural broadleaf forests and agroforestry systems managed for multiple purposes. Silvicultural treatments and species mentioned are based on field work in mid-hill pine plantations adjacent to natural Schima-Castanopsis forests in Kavrepalanchowk and Sindhupalchwok districts.
Figure 2. Pathways to convert pine plantations to natural broadleaf forests and agroforestry systems managed for multiple purposes. Silvicultural treatments and species mentioned are based on field work in mid-hill pine plantations adjacent to natural Schima-Castanopsis forests in Kavrepalanchowk and Sindhupalchwok districts.
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Figure 3. A schematic diagram of multipurpose management in an agrarian landscape in hilly Nepal, incorporating indigenous and local knowledge with ecological principles of land use.
Figure 3. A schematic diagram of multipurpose management in an agrarian landscape in hilly Nepal, incorporating indigenous and local knowledge with ecological principles of land use.
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Timsina, S.; Sharma, L.N.; Ashton, M.S.; Poudyal, B.H.; Nuberg, I.K.; Baral, S.; Cedamon, E.; Bajracharya, S.B.; Paudel, N.S. Lessons from Managing for the Extremes: A Case for Decentralized, Adaptive, Multipurpose Forest Management within an Ecological Framework. Forests 2022, 13, 333. https://doi.org/10.3390/f13020333

AMA Style

Timsina S, Sharma LN, Ashton MS, Poudyal BH, Nuberg IK, Baral S, Cedamon E, Bajracharya SB, Paudel NS. Lessons from Managing for the Extremes: A Case for Decentralized, Adaptive, Multipurpose Forest Management within an Ecological Framework. Forests. 2022; 13(2):333. https://doi.org/10.3390/f13020333

Chicago/Turabian Style

Timsina, Shrabya, Lila Nath Sharma, Mark S. Ashton, Bishnu Hari Poudyal, Ian K. Nuberg, Srijana Baral, Edwin Cedamon, Sanjeeb Bir Bajracharya, and Naya Sharma Paudel. 2022. "Lessons from Managing for the Extremes: A Case for Decentralized, Adaptive, Multipurpose Forest Management within an Ecological Framework" Forests 13, no. 2: 333. https://doi.org/10.3390/f13020333

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