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Article

Making Timber Accessible to Forest Communities: A Study on Locally Adapted, Motor–Manual Forest Management Schemes in the Eastern Lowlands of Bolivia

by
Benno Pokorny
1,
Juan Carlos Montero Terrazas
2,
James Johnson
3,
Karen Mendoza Ortega
4,
Walter Cano Cardona
5 and
Wil de Jong
1,*
1
Chair of Silviculture, Faculty of Environment and Natural Resources, Freiburg University, 79085 Freiburg, Germany
2
GOPA Worldwide Consultants, 61348 Bad Homburg vor der Höhe, Germany
3
Canavalia Verde, Villa Brigada 0000, Bolivia
4
Instituto Boliviana de Investigacion Forestal, Santa Cruz de la Sierra 0000, Bolivia
5
World Commission on Protected Areas, Cochabamba 0000, Bolivia
*
Author to whom correspondence should be addressed.
Forests 2025, 16(3), 496; https://doi.org/10.3390/f16030496
Submission received: 31 January 2025 / Revised: 18 February 2025 / Accepted: 8 March 2025 / Published: 11 March 2025
(This article belongs to the Section Forest Economics, Policy, and Social Science)

Abstract

:
Forest communities around the world have great difficulties in utilizing the economic potential of their forests, especially timber, under current technical requirements and legal frameworks. The present study examines the feasibility of motor–manual timber management among indigenous Chiquitano communities in Bolivia’s Eastern Lowlands. It evaluates local practices, tests technical optimization options, and assesses their technical, financial, and environmental impacts. Findings reveal that traditional motor–manual timber production is scarcely profitable, exacerbated by burdensome legal frameworks and limited market access. However, motor–manual forest management remains an essential source of income for communities, and it constitutes an important option for rural development. Field tests demonstrate that, with the use of better equipment such as quality chainsaws, and improved maintenance and workflows, productivity and profitability of local logging can be enhanced. Despite a low environmental impact, optimized motor–manual timber management continues to be constrained by governance challenges, logistical limitations, and limited markets for locally produced timber. The study recommends optimizing these aspects, including targeted technical support, market development, simplified legal frameworks, and the setting up of robust local governance structures to replace ineffective centralized command and control approaches. These improvements would enable communities to sustainably use timber from their forests while addressing their socio-economic needs. The findings underscore the potential of logging by local communities as an alternative to large-scale mechanized logging, for Bolivia and in other tropical forest countries.

1. Introduction

Over the last three decades, communal natural resource dependencies have been recognized [1,2,3,4,5]. Large natural forest areas became subject to communal collective use rights [6]. For instance, in South America, 20% of the land is designated as protected areas, but populated by indigenous and traditional communities [7,8]. While community-based conservation has been promoted [9,10], the living conditions of forest communities have in many cases remained precarious. Communities still face social marginalization and remain vulnerable to external threats like climate change, deforestation, land dispossession, and resettlement [11,12]. In addition to the allocation of land rights, sustainable income opportunities are necessary for poverty alleviation and to create long-term prospects, especially for young people [13,14].
The 1992 Rio Summit identified the sustainable production of timber as an option to combat deforestation in the tropics, while generating income [15,16,17]. Timber production was understood as mechanized harvesting by timber companies [18]. Simultaneously, the importance of forest communities for forest conservation became recognized. Community forestry initiatives became prominent, financed by international donors, and implemented by NGOs, and it was included in the legislation of many countries, but often with restrictions. Bolivia’s forestry legislation [19], for example, emphasized that communities follow the technical and administrative requirements demanded of timber companies [18,20]. The legal, administrative, and technological challenges turned out to be unachievable and communities depended on timber companies or NGOs when trying to benefit from timber [21]. Not uncommonly, external support led to social conflicts [22,23] and the sustainable exploitation of timber is ignored in new bioeconomy strategies [24].
Some countries made an effort to better adapt forestry legislation to the realities of communities. Bolivia, for example, has legalized previously illegal local forest exploitation, like the harvesting of small volumes without the design of forest management plans. In practice, however, it remains very difficult for communities in Bolivia and elsewhere to capture the economic potential of their forests.
Motor–manual logging and processing, or chainsaw milling as it is referred to in other studies [25], has been analyzed in the academic literature [25,26,27,28]. Its role in tropical forest logging has increased [27], in some cases already reported since the 1980s and 1990s [29]. Wit and van Dam [25] compiled case studies on motor–manual logging and processing in 20 countries. Motor–manual logging and processing can be legal, e.g., in Guyana, as regulations accommodate the practice, but more commonly it is viewed with reservation by authorities, or is illegal [27,28]. In some countries, motor–manual logging and processing exceeds the volumes that are produced by formally operating forest companies, e.g., in in Ghana, Cameroon, Peru, and Liberia [25]. Demands for timber products in domestic markets are an important incentive for rural populations with access to timber resources to turn to motor–manual logging and processing, and increase household incomes [25,26,28]. The availability of affordable and easier to operate chainsaws is another important explanation for the proliferation of motor–manual logging and processing in recent decades (this paper).
Commentators mostly agree on the economic opportunities that motor–manual logging and processing offers to rural people with access to forest, and who have the means to obtain the necessary equipment. Negative impacts on health, and possible contributions to intra-communal conflicts have also been observed [25]. Opposing views are held on how motor–manual logging and processing impacts forest conditions. While the practice is generally recognized as having lower impacts on forests, it may contribute to the decline of timber species that are being targeted [25,27].
The majority of studies on motor–manual logging and processing recognize that forestry legislation and regulations are inadequate, even in countries where the practice is authorized. Where the practice is outside of the law, all studies suggest that this needs to be addressed, but how it is best done is a point of contention. Folefack et al. [30] suggest that legalizing motor–manual logging and processing increases profits, added value, and social welfare. Lescuyer et al. [26] argue that continued operation outside of governance institutions constrains its contribution to sustainable and equitable forest benefits, and that the ‘fine-tuned’ formalization of the practice is required. The conflict of unauthorized motor–manual logging and processing and FLEGT requirements is also observed by various authors [25,26,27]. Only regulatory changes, however, are considered insufficient, as the public administration performance would need to keep pace with such changes [26]. Little attention has been given to the actual operations of motor–manual logging and processing, as this paper aims to do.
The literature on the topic indicates that the sustainable use of timber from natural forests by communities requires exploitation options adapted to local capacities, needs, and interests ([25,26,27], this paper). This study analyses the feasibility of locally adapted low-input, motor–manual timber logging and processing among indigenous communities in the Bolivian Chiquitania, a highly diverse forest region in Eastern Bolivia. This study will (1) describe local timber extraction schemes, (2) test options to enhance motor–manual harvesting as the base for low-input forest management, and (3) assess the technical and financial performance and environmental impact of such management.

2. The Case Study

2.1. The Situation in Bolivia

Over the past two decades, Bolivia has experienced notable growth in forest areas managed by indigenous and peasant communities, and local social groups [31]. They managed 2.2 million ha in 2009, and 6.6 million ha in 2023, or 63% of the 10.6 million ha of natural forest under management. Forest companies managed 2.9 million ha, while private ownership accounted for 1.6 million ha. Bolivia’s forest legislation mandates reduced impact logging (RIL) with oversight and approval from the national government forestry agency ABT (Autoridad de Fiscalización y Control Social de Bosques y Tierras). Many efforts since Bolivia’s 1990s forestry reforms aimed at building the technical and managerial capacities of indigenous communities to follow forestry regulations. Only a few success stories can be reported [32] and the harvesting and marketing of timber from indigenous and other community lands is carried out by logging companies, or community members negotiate individually with chainsaw operators to extract timber [33]. The results are low prices, and the conversion of logged-over forests to agricultural land, or negative social, economic, and environmental consequences [34].
The Bolivian Constitution of 2009 creates the possibility for forest communities to define their own rules, management, and governance systems, which should be supported and validated by ABT [35]. This legal opportunity is known as the Integrated Forest and Land Management Plan, which should incorporate indigenous and local communities’ forest management traditions. In practice, however, when applied, such plans follow forest regulations defined for timber concessions managed by timber companies (Administrative Resolution ABT N° 250/2013). Several regulations allow small volumes of timber to be harvested on indigenous and local community lands in some Bolivian regions. These regulations increase decision-making power to communities but do not break dependence on other forestry actors for commercial timber extraction such as timber companies and non-local entrepreneurs [33,36].

2.2. Study Area

This study focuses on the Chiquitanía (Figure 1) in the eastern lowlands of Bolivia, an area covered largely by natural forest constituting a transition from dry seasonal lowland forest, the Chiquitano forest, in the South (55% coverage) to humid Amazonian forest in the north (21% coverage). The remaining area is covered by seasonally flooded marshlands and dry endemic shrublands locally called abayoy [37]. Chiquitanía is the source of 80% of Bolivia’s timber from indigenous territories and community land [31,38]. The Chiquitano forest is threatened by predatory timber harvesting deforestation from agricultural and cattle ranching, and forest fires [34]. Over the past two decades, the national government has increasingly attempted to settle farmers from upland areas of Bolivia in the Chiquitanía [39]. The older settlements are indigenous communities founded by Jesuits [40]. The principal indigenous nation in the region is the Chiquitano, of approximately 40,000 people, just under half of the region’s population. Over four million ha have been allocated under different rights of tenure to indigenous communities, logging concessionaires, private landholders, farmer communities (campesinos), and local social groups [31].
The study reported here was implemented in the Territorio Indígena Originario Campesino—TIOC (Indigenous Native Peasant Territory) of Lomerio. This TIOC covers an area of 259,189 ha and has 29 villages with a population of 6178 or around 1200 families (CICOL, personal information, 2019). The TIOC Lomerio is legally affiliated with the Organization of Indigenous Communities of Lomerio, CICOL (Central Indígena de las Comunidades Originarias de Lomerío), which aims to establish autonomy over indigenous territories.
The soil and terrain of the area are poorly suited for intensive farming. Traditionally, families cultivate less than one ha of swidden plots and collect fruits, nuts, medicinal plants, and wood from collectively owned forests. Beekeeping is gaining in importance. Many families, however, are switching to livestock farming. A recurring problem is forest fires caused by escaping fires when burning recently slashed agricultural fields or pastureland [34,41].
The communities of Monterito were selected in coordination with CICOL and community members for the analysis of informal timber harvesting schemes, The underlying goal was to identify options for the enhancement of local logging practices through improved motor–manual harvesting. Forest operators from Monterito, San Josecito del Sarí (Municipality of San Ignacio de Velasco), Villa Nueva—La Emboscada (Municipality of Concepción), and Puquio (Municipality of Lomerío) near Puquio joined the testing. These communities are affiliated with indigenous organizations responsible for the implementation of the forest management plans in their respective communities.

2.3. Experiences from Formal Timber Harvesting in the Study Area

In the 1990s, with support from NGOs, government agencies, and international cooperation, a General Forest Management Plan (GFMP) was developed for the TIOC Lomerio under the responsibility of CICOL. This included the purchase of a stationary band saw mill located in the community of Puquio. Individual communities or groups of communities were allowed to implement their annual operation plan (AOP). The AOP included the extraction of logs with machinery and their subsequent milling in the stationary sawmill in Puquio. The machinery was managed by a private company under the supervision of CICOL, with technical support provided by local NGOs. The sawmill was expected to generate financial returns that would initially cover CICOL’s operating expenses to then distribute any surplus to the communities.
Some communities benefited from temporary jobs as well as incomes from the timber harvested in their forests. Income from the sale of timber was used for school improvement, the purchase of medicines, and maintenance of a healthcare center. Challenges in generating expected cash flows arose, primarily due to the low productivity, high costs, and unfavorable market prices. Disagreements between the sawmill and local communities, particularly over delayed and perceived underpayments were frequent. Distant communities did not benefit from employment opportunities at the sawmill [42]. By 2000, significant losses led to the suspension of the GFMP under CICOL’s supervision, and the sale of the sawmill to a private company.
At this point, members of some of the communities took the initiative to use their chainsaws to fell and saw timber on their own, without prior communal endorsement. They began cutting trees in the most remote parts of the forest, especially where they had previously fought against intruders together with CICOL. The timber was sold informally for little money to local buyers, who transported the timber to Santa Cruz. Discontent with this practice soon grew within communities because the income remained in the hands of a few unauthorized loggers. This violated the GFMP, which covered the entire area managed by CICOL, jeopardizing the forest activities of all the 28 communities involved. As a result, the community of Monterito decided to organize its own logging and prepare a new AOP. After consultation, Monterito’s plans were authorized by CICOL and the other communities.
To overcome the lack of operating capital, Monterito requested the support of a timber company, which provided the financial resources to implement their new AOP for 280 ha. The company appointed a professional forester as a collaborator and hired community members as temporary staff to carry out a forest census. After being approved, AOP logging operations were carried out under the supervision of the forester. The company was eventually caught undertaking illegal activities and collaboration was terminated. All communities included in the CICOL’s GFMP were affected, and the plan was suspended for two years. Many communities as a result lost interest in collective forest management coordinated by CICOL. Informal logging operations, however, continued.

2.4. Data Gathering

Structured interviews were conducted with 28 of the 56 families living in the Monterito community to record details of informal timber harvesting and to find out whether and to what extent families were involved in these activities. Families were selected for their recognized involvement in timber extraction activities. The survey was carried out by locals who had previously received intensive training. The questionnaire and the survey process were tested to ensure the suitability and comprehensibility of its application. In each household both spouses were interviewed. The interviews focused on timber harvesting, i.e., activities, logistics, tree selection criteria, harvesting volumes, products, sales markets, actors involved, and governance arrangements. They also inquired about non-timber forest products harvested, the economic importance of the different products, and the forest and the land use dynamics. Questions were asked about the costs and benefits of timber harvesting and its environmental impact. Data were tabulated for subsequent analysis [43].
A group of community members, selected after discussions with village authorities, was brought together to verify and complement information from the surveys. The group drew maps of logging sites and discussed selection criteria. For each site, the group recalled how many trees had been logged and of which species. Opportunities and risks associated with informal timber harvesting were discussed, as well as possibilities for optimization. Information on timber quantities was provided in the customary Bolivian unit of measurement “pie tablar” (pt), which corresponds to a board foot of one inch × one foot × one foot or 2.54 cm × 30.48 cm × 30.48 cm. 424 board feet (bf) equals one cubic meter (m3). The prices were expressed in local currency Bolivianos (Bs). At the time of the study (2019), the exchange rate was Bs 6.96 for USD 1.
Three community members with experience in timber harvesting were asked to demonstrate how trees are selected, felled, processed, and transported off-site, to evaluate the technical, financial, and environmental performance of informal logging. The three members, each with one assistant felled a total of 16 trees, mainly cuchi (Astronium urundeuva), but also curupaú (Anadenanthera colubrina), and sirari (Copaifera chodatiana), with an average volume of 1.26 m3 per tree, as well as 3 tajibo (Handroanthis serratifolius) trees of significantly smaller dimensions (Table 1).
The group was given full autonomy in how to carry out the operations and was accompanied through all working steps. The following measurements were taken: work efficiency, yield of the timber processed, and damage to the remaining forest stand. The time the workers invested for each activity was measured, as were the volumes of the felled trees, sawn logs, and sawn products. To assess financial viability, both direct and indirect costs were considered. Direct costs include all input-related items such as equipment, materials, and services, including transportation costs and salaries, and were determined for each phase of work. The indirect costs, e.g., depreciation of equipment and materials, were estimated using standard values.
The damage caused by the felling and sawing was measured by classifying all trees with a diameter at breast height greater than 20 cm (dbh) into five classes of damage: 1. no damage; 2. damage to 25% of the crown but intact trunk; 3. damage to 50% of the crown and/or moderate damage to the trunk; 4. damage to 75% of the crown and/or severe damage to the trunk; and 5. the tree had severe damage or died. No surveys along the skid trails were conducted since no roads are needed to transport sawn timber products with heavy machinery and major damage was not expected.
The study of technical optimization options focused on two primary cost-relevant activities, i.e., the sawing of logs into locally marketed end products such as long logs, short logs, and poles, and the transportation of these products to the collection points for further distribution. All operators underwent training on the proper use and maintenance of the tested equipment which included instruction on equipment assembly, chain sharpening, and lubrication.
For milling, we considered three options: (1) the traditional technique, freehand sawing of the trunk with the chainsaw, but with quality equipment in terms of the chainsaw (STIHL MS661), the latest generation model with high performance, low weight, and reduced vibration thanks to an all-electric management system, a specific milling chain (Rapid Duro), and professional maintenance including periodic sharpening; (2) The use of a portable mill Bristol guide bar for single-person use consisting of a frame adjusted by a bolt system adjustable in all its sections and used for mounting on the saw blade. The Bristol unit used in the test was made in Brazil and weighs 7 kg; and, (3) the use of a portable attachment Logosol timberjig and guide rail (further referred to as Logosol equipment) consisting of three main parts: the timberjig used as a stand, two steel guide rail supports that can be adjusted at 90° angles in four exact positions, and a 2.75 m aluminum guide rail, adaptable for longer dimensions. The unit weighs 15 kg (5 kg excluding the rails) and can be used with blades up to 90 cm in length for sawing logs up to 80 cm in diameter. The Logosol equipment is manufactured in Sweden.
The three technologies were evaluated based on three parameters: (1) yield, understood as the ratio between the volume of the log to the volume of the sawn products; (2) time, understood as the description and qualitative and quantitative documentation of the flow of operations to calculate the total time, productive time, non-productive time and efficiency percentage of each technology; and (3) input, required for the operations (i.e., gasoline, spare parts, logistics, transportation). The study used two hardwood species, tajibo amarillo (Handroanthis serratifolius) and cuchi (Astronium urundeuva), and three semi-hardwood species with commercial value, tarara colorada (Platymiscium fragans), tarara amarilla (Centrolobium microchaete), and roble (Amburana cearensis), to balance out the effects of different wood densities and wood qualities.
Three options for transporting the sawn products from the processing site to the storage yard were compared: (1) Manual transportation on shoulders, which is common in the area. People between 30 and 50 years of age in good physical condition were selected for the study. The boards were transported by two people, the planks and poles by one person; (2) Transport on horseback, more specifically two experienced local people who handled two horses with their respective harnesses and accessories. The animals were used alternately to avoid excessive strain. And, (3) transport with a Chinese-made 250 cc three-wheeled cargo bike (Dayand-PUMA), very common in the area, with a trailer with a maximum load capacity of 300 kg.
For each option, times were measured for each step (i.e., loading and shipping, transporting, unloading and stacking, and packing), including preparing access routes for the horse and motorcycle. Non-productive times for refreshments, rest breaks, and equipment maintenance, as well as unforeseen events (mechanical breakdowns, rain, storms, etc.) were also recorded. The distance traveled on each trip was measured and, based on the measured volume, the total weight of the transported products was calculated. Necessary resources were recorded, including periodic feeding and watering of the horses.
For systematization and analysis, parameterized matrices were designed in Excel format to standardize the data recorded in the field. Based on the data collected on time and input, input costs (Table 2), and sales value of final products were entered. For all options, a net cash flow analysis was undertaken to calculate the net present values (NPVs) and internal rates of return (IRRs).
For the analysis, the sale price of the lumber from the forest road was assumed at 105 USD/m3, regardless of the product and species. Accordingly, the timber trader’s costs of 58 USD/m3 for transporting the timber over 100 km to Concepción, the nearest city, were not taken into account. The analysis also did not take into account the costs of technical training and support for local operators.

3. Results

3.1. Local Timber Harvesting Practices

Three-quarters of the households surveyed had actively participated in logging in the past year. Tree felling locations were generally easily accessible but outside the area of the AOP. According to the municipality’s land use plan, the selected areas were designated for agriculture or grazing land. In some communities, logging happens with the permission of local authorities while in others it does not, which may lead to conflicts within the community, with other communities, and with CICOL. In Monterito, only one person logged without permission, while 14 people obtained permits from the community head (cacique) and another nine from the community assembly. Two people had the approval of both the head and the assembly.
Households harvested an average of 13.5 trees the previous year. Two persons harvested more than 30 trees each. Households harvested trees for their consumption, particularly for the construction of fences, suggesting a close link between local forest use and the expansion of livestock farming. Others engaged in commercial logging. The timber was sold to third parties and a smaller proportion within the community. Tree species were selected that have durable wood, adequate dimensions, and a reasonably straight trunk. Within the two main categories, construction materials and fencing, seven products were locally manufactured using chainsaws (Table 3). All the products are sold in standard dimensions corresponding to volumes expressed in board feet. The volume of one piece varies between 0.0075 m3 for one strut, and up to 0.045 m3 for a cross beam. Prices vary from USD 244/m3 for roof beams to 169 USD/m3 for fence posts.
Nine tree species were named that were harvested last year. Cuchi (Astronium urundeuva) accounted for more than half of the harvested volume (57%). Cuchi wood is known for its durability, and accounted for 85% of fence posts production, but is also used as corner posts for houses. In the second place, although in significantly lower volumes, tajibo is used locally, including two species: Tabebuia sp. and Handroanthis serratifolius. Both are among the most commercially valuable species in the region and are used for furniture, house construction, and crafts. In addition to these species, some cases of harvesting of cedro (Cedrela fissilis) and roble (Amburana cearensis) were mentioned, both with great commercial importance in the region 20 years ago. Their reduced utilization suggests a decrease in availability because of past exploitation. Similarly, the lack of mention of Bolivian rosewood (Machaerium scleroxylon, morado) indicates a rapid decrease in availability. Interviews confirmed that households in the region also use a variety of non-timber forest products (NTFPs) such as nuts, medicinal plants, fibers, forest seeds, wild fruits, and honey. The sale of baru nuts (Dipteryx alata) and honey in particular can generate considerable income. In addition, families engage in hunting and fishing, often in combination with logging. Overall, forest uses play a key role in household subsistence and are an important element of cultural identity.
Chainsaws without any special accessories are the preferred equipment for felling trees and for sawing. All chainsaw operators in the community are self-taught. Experienced operators offer their services for a daily rate. There were 21 such operators in the community. All of them use Stihl chainsaws; 16 own their chainsaws, while 5 operators rent chainsaws for the equivalent of USD 7.20 per day. Most of the chainsaws were more than five years old, many even more than 10 years old. Only two chainsaws were purchased in the last two years.
Logs are usually processed directly at the felling site as there is no equipment available to move them in one piece. Sawn products are transported manually on shoulders if they are not too heavy and the distance is not too large, usually less than 200 m. Eight of the interviewees stated that they shouldered products over a distance of up to 1 km, and three even mentioned distances of more than 1 km. For heavier products, horses and sometimes cargo bikes are used. More than a third of respondents stated that they work almost exclusively manually, but combine manual transportation with the use of horses and cargo bikes. More than 80% of the operators do not market the timber products they produce. One-third used the products for their purposes, such as building houses and fencing pastures. One-tenth supplied their community for community projects or to meet a specific demand. A single operator supplies its products to another community.
Less than 20% of the people engaged in logging sold their sawn products—almost exclusively tajibo and, less frequently, cedro, roble, and curupaú. The prices obtained for the products fluctuated widely: In Lomerio, between USD 2.90 per post and USD 17.25 per straining or corner post. Eight households were more intensively engaged in external marketing. In one year, they produced a total of 1895 posts (46.46 m3). One businessperson reported having sold 15.51 m3 of tajibo as flitches to Santa Cruz. A few people have specialized in these more lucrative urban markets, although selling without the required permit is risky.

3.2. Technical and Financial Assessment

3.2.1. Technical Aspects

Felling and processing of the 16 trees selected by the teams that were requested to test low-input, motor–manual timber harvesting required an average of 6.5 h per tree, (Figure 2). Of these 6.5 h, about 35% was dedicated to productive work, and 19% to logistics. Almost half of the time, (46%) was recorded as waiting time, which included waiting, hunting, and resting. It took a total of one hour to get to and from the forest each day. Half an hour was spent searching for trees. The felling, including preparations, took less than 20 min while the sawing of the felled tree took about one hour and a half. Less than one hour was spent on sharpening the chain, troubleshooting the chainsaw and other interruptions, and 30 min on a lunch break.
A total of 5.5 m3 of final products were obtained from the 16 trees (Table 4). Almost 60% of this volume consisted of fence posts and 30% of roof beams for housing construction.
Around 30% of the log volume was transformed into products (Table 5). Posts showed yields of over 30%, but also the yields for construction timber reached almost 30%, both yields being lower than expected as trees with low-quality stems were sawn. The differences in yields per species were as follows: sirari (33.4%), cuchi (32.0%), and curupaú (30.3%). Cuchi and curupaú trunks were on average longer than those of the other species and varied between 28 cm and 78 cm in diameter. Tajibo trunks had smaller diameters and were of poorer quality, compared to those of the other species.
The time required for processing varied greatly depending on factors like the species (wood density), type of product, dimension, quality of the log, the condition of the chainsaw and chain, and the skill of the operator and the assistant. Processing of cuchi was more difficult than that of lower-density species such as sirari. Rough-sawn fence posts were produced more quickly than higher-quality products such as roof beams. Processing logs with depressions or other natural physical defects also took longer, especially if a good quality of the final product was to be achieved.
As for the transport distance of the sawn products, we measured an average distance of 160 m that operators carried on their shoulders. Typically, the operator carried two posts per trip corresponding to 0.034 m3 or 34 kg. Consequently, 30 trips with 60 posts were needed to transport 1 m3 of cuchi fence posts, corresponding to approximately 2.35 h of working time.

3.2.2. Costs of Operations

Based on the time estimates, equipment used, and material costs described above, the cost of producing posts and boards and placing them at the roadside was estimated. According to this, the average cost of producing a fence post from cuchi was USD 2.86 per post, or USD 168.53 per m3. The production costs for sawn timber from tajibo amounted to USD 246.04 per m3. Figure 3 shows the breakdown by cost category. Almost 60% of the total costs were labor costs, together with the costs of transporting the operator and assistants to and from the forest, personal costs accounted for more than two-thirds of the total costs. A further 16% was accounted for by the chainsaw, which was rented daily. The costs for the transportation of wood and products, and for fuel and lubricants accounted for around 7%–8% each. Other costs were negligible. In actual logging operations by community members, payments may have to be made to officials to avoid the confiscation of timber when no valid transportation permit was obtained. Neither the costs for legalization nor compensation payments to the community for the use of communal forests were taken into account.
If the products were to be sold following required legal procedures, the costs would increase significantly (Table 6). Many of the fees are fixed payments that disregard the low production volumes. However, there are also costs involved in organizing these payments, for example for filling out forms, for obtaining advice and information, for trips to the city, and for long waiting times at government offices.

3.2.3. Financial Return

There are four possible sale locations for Monterito timber products: Lomerío itself (Monterito, Puquio, or San Antonio), the small town of San Ramón (71 km), the district capital of Concepción (77 km), and the department capital Santa Cruz de la Sierra (268 km). The prices (as of May 2022) for a fence post ranged from USD 2.87/post in Lomerio to USD 3.59/post in Santa Cruz. The price difference for sawn timber was even greater at USD 243.68/m3 in Lomerio and USD 487.36/m3 in Santa Cruz. These prices were paid by traders. Although end users usually pay 10%–15% more, communities tend to sell to traders to avoid having to find customers and rent storage facilities. When selling to traders, communities usually deduct the costs of transport, loading, and unloading, from the above prices. In response, traders offer to take over all forest work, including the risk of being caught for a lack of permits, in exchange for lower prices paid for the products.

3.3. Environmental Impact

The damage of the logging operations described above was limited to the area around the felled trees. No tracks, skid trails, or stacking areas were created in the forest. A total of 18 trees were damaged during the felling and processing of the 16 trees. Almost 61% of the damage occurred to trees with a dbh less than 30 cm, but there were also three trees with a dbh greater than 60 cm that were damaged. In two-thirds of the cases, the damage was minor and mainly affected the crown. Six trees were severely damaged.
An additional environmental impact is the possible link to forest fires. Tree felling and processing with chainsaws leave wood residues and flammable material on the ground. In combination with the possible construction and use of trails, this creates favorable conditions for the spread of forest fires, especially in the dry season. However, forest fire risk is much lower when using motor–manual logging and processing than in the case of mechanized large-scale timber logging, which leaves a much higher fuel load. In addition, as forests close to villages are prioritized for chainsaw logging, firewood collection will reduce the fuel load in the harvested area.
Excellent natural regeneration, especially of cuchi, was observed during fieldwork in the areas where chainsaws were used. The natural regeneration of trees also occurred in adjacent meadows and former agricultural areas. This indicates the considerable regenerative capacity of forests after motor–manual logging and processing. Unfortunately, however, it was also found that many families intended to use the harvested areas as pastureland afterward.

4. Options for Technical Optimization

4.1. Processing

To test the three sawing techniques used, i.e., free hand, using a guide bar, and using the Logosol equipment, a total volume of 47.68 m3 of logs was processed into 7.62 m3 of short wood and 13.09 m3 of long wood. The total yield was 43.53%. For all three options, the yields were better than 40%, which meets the legally established minimum requirement [28], but there were clear differences in efficiency between the three technologies tested (Table 7).
The use of Logosol equipment achieved the highest overall yield of more than 45%, followed by the guide bar (44%) and freehand use of the chainsaw (41%). These differences between the techniques were even more pronounced in the case of semi-hardwood timber. Logosol equipment use achieved a yield of nearly 46.94%, while freehand milling only produced a yield of 38.8%. However, if one looks only at hardwood species, which are the most commonly harvested in the region, freehand milling achieved the highest yield of 43.9%, followed by Logosol equipment (42.77%) and the guide bar (40.94%). The subjective quality assessment indicated that Logosol equipment achieves visibly better results than the other two techniques in terms of product surface smoothness and angular precision.
In terms of production times, it took an average of 4.4 productive hours to process one cubic meter of wood. However, at 5 h per cubic meter, Logosol equipment and the guide bar required significantly more time than the 4 h of free-hand milling due to additional time requirements for transport, assembly, and disassembly. In all three technologies, sawing required more than 70% of the total time, followed by positioning (8%–10%), de-logging (2%–17%), and rounding (2%–5%). In addition, time was spent on operational control activities. Working with Logosol equipment and the guide bar consumed more time per cubic meter compared to freehand milling, mainly due to the need to check the pusher rail, adjust the timberjig and square, necessary to correctly size the log, and ensure the quality of the cut. If productive and non-productive activities are considered together, the differences between the technologies are even greater, from Logosol equipment (6:38 h per m3), the guide bar (6:05 h per m3), and freehand milling with less than 5 h per m3 (4:63 h). These differences are also reflected in the productivity levels, with Logosol equipment at 0.16 m3/h, the guide bar at 0.17 m3/h, and freehand milling at 0.22 m3/h.
Differences were also observed in the consumption of the chainsaw’s fuel mixture (approx. 95% gasoline and 5% engine oil). Freehand sawing consumed 6.22 L per m3 of sawn timber, while Logosol equipment 6.79 L/m3 and the guide bar 7.80 L per m3, respectively.

4.2. Transport

The three tested transport options (human power, by horse, with cargo bike) differed significantly in terms of productivity (Table 8).
Based on the measured transport distances of 379 to 689 m, the cargo bike took 1.10 h to transport one cubic meter of timber, while the horse took 2 h per m3. Shoulder transportation took much longer, almost 9 h per m3.

4.3. Financial Assessment

The financial results vary considerably for the three sawing technologies when the same transportation means are considered (Table 9). Because of the equipment costs, the costs for the Logosol equipment variant are much higher, while the additional investment for the guide bar is moderate.
All three variants were cost-effective, with a positive net present value (NPV) and a benefit–cost ratio greater than 1. However, the benefit-cost ratio of 6.68 for freehand processing in combination with cargo bike transport was significantly higher than for the guide bar (4.24) or even for the Logosol equipment option (2.81).
All three techniques tested gave a positive net financial result above the local selling price of the standing trees of 15.09 USD/m3. However, due to the differences in productivity, inputs, investments, and operating costs, the financial results of the tested technologies were very different. The use of Logosol equipment yielded a net result of 28.02 USD/m3, the use of the guide bar resulted in 30.32 USD/m3, but the freehand processing of the logs in combination with the use of a cargo bike for transport generated a net income of 37.93 USD/m3.

5. Discussion

Motor–manual logging and processing of timber is a common practice, among poor rural residents living in or near tropical or subtropical forests, and even among a category of forest users in temperate zones [44]. The practice has proliferated in the southern hemispheres for three main reasons. An important one is the availability of affordable and relatively easy to use chainsaws in recent decades [44]. Motor–manual logging and processing became an option for local operators to satisfy a demand in their own, or nearby villages and urban centers where demand was poorly met by traditional timber supply chains, or where the formal wood and timber supply chains have collapsed in recent years, for instance, in Peru [45]. Local operators saw motor–manual logging and processing as an opportunity to meet livelihood needs. With relatively little investment in equipment and some minimal training [44], operators can engage in motor–manual logging and processing and obtain incomes. In some instances, effective supply chains have developed starting with motor–manually produced timber, which is traded into several neighboring countries [46].
In the case of Bolivia, as the findings suggest, an important reason why Chiquitania residents turned to motor–manual logging and processing was that previous efforts to promote communal logging under a formal regime failed (Section 2.3, this paper). NGOs and government agencies attempted with financial support from international donors to get forest communities to use their forests sustainably following reduced-impact logging principles, but with little success. Most initiatives were abandoned by communities after external support was withdrawn because of high costs, erroneous bureaucracy, and uncertain markets [8]. As a result, the Chiquitania resident turned to individual motor–manual logging and processing nowadays to benefit from timber in their forests, to obtain material for domestic uses and to generate income. However, as in so many other locations in the world [26], they operate largely outside of the law.
The literature is ambiguous about the actual benefits from motor–manual milling. Profit margins reportedly vary from 15% to 50 % [25]. In some instances, producing timber is an important option to benefit from forests for forest dwelling rural people [47]. This study corroborates that motor–manual logging and processing is an attractive way for local communities in Chiquitania to use the wood from their forests. It remains one of only a few opportunities to generate cash income in the region. As a result, over 75% of the surveyed families reported that they were involved in this type of harvesting. It makes sense for many families as it is simple and flexible, does not require large investments, and avoids erroneous bureaucracy, however, because existing regulations are not abided by. Motor–manual logging and processing can be combined with hunting and gathering forest products, and products are made for personal use that could not otherwise be purchased, like for in-stance fence posts to expand livestock farming. The modest profit margins that are observed in Chiquitania (Section 4) relate to the overall economic realities of Bolivia. While USD 15 daily wages are modest, which is the equivalent against which profits are measured, it is higher than in areas where rural populations capture incomes just above poverty line levels, a reality in many locations where motor–manual logging and processing is practiced [48,49,50].
While motor–manual logging and processing is thus widely reported as a complimentary or substitutionary income opportunity, its impact on communities where such practices become adopted is similarly ambiguous. The literature reports on how income from motor–manual logging and processing is used for communal investments [25]. However, such non-traditional new opportunities for income may, in other locations, contribute to a decline in the social cohesion of previously self-contained communities [50]. In the case of Chiquitania, for instance, communities where local loggers operate do not capture any payments for the use of collectively held forests, resulting in a diminishing respect for common property resources, which has been the backbone of many indigenous or other customary rural communities in the America and elsewhere.
Virtually all publications on motor–manual logging and processing indicate its constraints with forest sector institutionality [25,26,27]. A legal and regulatory frame that accommodates motor–manual logging and processing is the exception, rather than the rule. In a very few cases, adequate regulations exist to accommodate the practice. While almost all analyses of motor–manual logging and processing recommend the formalization of the practice, few specific recommendations are provided on how that actually should happen. Its challenge is also demonstrated in Bolivia. Bolivia, in 2020, modified its forest regulations, which until then strictly prohibited motor–manual logging and processing, and a Decreto Supremo (supreme decree) was enacted, permitting the practice from thereon. However, despite this change, an acceptable income can only be obtained by avoiding the costs of permits and taxes (Section 4), which are required for any timber processing and trade. This is a conundrum that is recognized, but few specific solutions have been forwarded [26].
In tropical countries, sustainable forest management is often perceived as requiring centralized state control. Authorities, however, typically struggle to effectively monitor large forest concessions and economic activities that convert forests into other land uses. A more viable solution would involve local communities organizing to manage their forests through agreements and clearly defined mechanisms with established responsibilities. If local forest management, including sustainable exploitation and concurring effective governance, was successfully established, the state’s role could shift to support these efforts. Motor–manual logging and processing is an important option to make forests profitable for local communities, which would become a key incentive for communities to pursue effective forest governance.
While the above is the case, in Bolivia, as elsewhere in the world, motor–manual logging and processing, is in practice constrained by a lack of the technical skills necessary to operate and maintain chainsaws properly and a lack of means of traveling people and equipment to logging locations. This is one of the many attributes of motor–manual logging and processing that need to be addressed. In Bolivia, the greater the distance of exploitable forests, the lower the financial viability due to the related transportation costs. The exploitation of more remote forest areas inevitably requires investment in road infrastructure which in turn increases the complexity and costs of operations, as well as secondary deforestation effects. For this reason, harvesting will at least initially be limited to the easily accessible parts of the forest, until communities have established effective local governance systems and aggregate capital to undertake investments in roads. This contributes to the limits to make motor–manual logging and processing an alternative to industrial logging and protect larger natural forest areas from logging damage. Moreover, income from the accessible forest parts is already very relevant for the communities and there might be limited interest or need for them to use the timber from more remote areas.
Studies on motor–manual logging and processing indicate the technological and capacity challenges with the practice [25]. Almost all studies on these practices recommend training practitioners. Surprisingly little attention is given to appropriate equipment and how it is used, which would make local timber processing easier, more effective and efficient. In this respect, this study does add an important contribution to the literature, but it also highlights a direction where improvements can and need to be made. The testing of milling and skidding variants demonstrated that the financial attractiveness of the customary system could be improved by simple means. The use of suitable chainsaws and chains, training in their operation and maintenance, and better organization of the work process significantly increase productivity and financial results.
The test of three technologies for sawing and skidding showed that the freehand use of a chainsaw is financially more attractive than the use of Logosol equipment or a guide bar. This goes against recommendations to use the two latter options, as they are considered to result in less waste [51]. However, in the Bolivia case, this study finds that the slightly higher yield and product quality of Logosol equipment or guide bar does not justify the significantly higher investment and operating costs. While this is the case, alternative options include the use of the equipment of a cargo bike to transport sawn products to a collection point where truck transportation is possible.
Some methodological shortcomings of the study should be considered. The study to describe customary practices and the one on optimization options were carried out with different actors from different municipalities. The originally planned coherent sequence of the two studies could not be carried out due to the COVID-19 pandemic and obtaining the necessary authorizations. In addition, there were differences in the methods used in the two aspects of the study. As a result, the estimates of productivity and financial results are not fully comparable. The limited sample size of motor–manual logging and processing reduces the accuracy of the reported values. Some parameters of relevance for the calculations could only be approximated, but not systematically measured, like, for instance, the quality of the sawn timber or its marketing options. Due to the sensitive nature of the informal wood-use system described, it can also be assumed that not all of the information provided in the interviews is entirely accurate. Nevertheless, it can be assumed that even if not all data and information are equally reliable, the results provide a plausible overall impression of realities and potentials, also because a large number of local people and experts were interviewed.

6. Conclusions

Motor–manual logging and processing is hampered in Bolivia, as in many other locations in the world, by requirements developed for large, commercial operators. Where it is possible, motor–manual logging and processing is a viable and affordable option for forest communities to benefit from timber in their forests. It can realize the ambitious objective from UNCED 1992 to achieve sustainable forest management in its truest sense. It would contribute to forest conservation and foster the livelihood improvement of forest communities. At least in Bolivia, when local motor–manual logging and processing comply with regulations and the prescribed administrative procedures, the costs would now render this type of logging unprofitable. On the other hand, legalizing wood products from motor–manual logging and processing would make them much more compatible in domestic and even international markets.
A significant challenge lies in developing attractive and stable markets for locally produced wood. Important local customers include wood processors such as carpenters and builders, as well as farmers, who use fence posts. There is potential for tapping into the markets of larger urban centers. Public procurement programs, which represent a significant market in the case of Bolivia, could also play a crucial role, particularly if local products are explicitly prioritized. Independent export market development seems feasible only for niche markets in the medium term due to the high formal requirements and high costs, despite higher prices that can be derived in those markets.
To make local motor–manual logging and processing much wider available, three viable measures in particular should be taken: 1. Government agencies, NGOs, and other support organizations must develop expertise to engage rural, especially indigenous, communities effectively. This expertise should include knowledge of community dynamics, and methods for meaningful interaction, as well as technical skills such as chainsaw operation, silvicultural practices, timber harvesting, transport techniques, and support for local governance arrangements. 2. Sufficient resources must be allocated to procure essential equipment—in the case of Chiquitania, chainsaws, saw chains, cargo bikes, and spare parts. 3. Where it is promoted, external support is needed, including long-term, trust-based collaborations, which require sustained financial and human resources to support organizations effectively and optimize available resources.
It is imperative to adapt the legal framework to facilitate local motor–manual logging and processing. This adaptation can be in the form of self-regulation at the communal level, which may also increase the contribution of communities to forest monitoring, assisting state agencies in their activities. A shift away from centralized control toward empowering local governance systems is crucial to fostering sustainable and inclusive forest management practices, including authorized motor–manual logging and processing.

Author Contributions

B.P.: design of the study, supervising research, drafting and revising paper. J.C.M.T.: design of the study reviewing and revising paper draft. J.J.: contribution to field research, writing research report, reviewing and revising draft paper. K.M.O.: design of the study, supervising research, reviewing and revising draft. W.C.C.: reviewing and revising paper. W.d.J.: reviewing and revising paper. All authors have read and agreed to the published version of the manuscript.

Funding

The project was generously supported by the STIHL company. Hiller S.A., a private company representing STIHL in Bolivia, provided technical backstopping, donated chainsaws and accessories, supported on-site training, and oriented the selection and organization of materials and equipment tested in the field.

Data Availability Statement

The data used for this paper are available in the report: Montero, J.C., Mendoza, K., Pokorny, B., Ascarrunz, N., Johnson, J. 2020. Factibilidad técnica y financiera del aserrío móvil por productores forestales indígenas chiquitanos: en búsqueda de nuevas alternativas para reactivar el sector forestal en Bolivia. Instituto Boliviano de Investigación Forestal, Santa Cruz de la Sierra, Bolivia (https://ibifbolivia.org.bo/wp-content/uploads/2022/09/2021-Montero-et-al-Factibilidad-tecnica-y-fnanciera-del-aserrio-movil.pdf accessed on 30 January 2025) and James Johnson, Olvis Camacho and Roy Vélez. Estudio de línea de base del aprovechamiento forestal con tecnología local: Un estudio de caso de la Comunidad Chiquitana de Monterito, Lomerío, Bolivia (available upon request).

Acknowledgments

The study was implemented by a consortium of public, private, and community-based partner organizations coordinated by the non-governmental forest research organization Instituto Boliviano de Investigación Forestal (IBIF). We would especially like to thank Nataly Lorena Ascarrunz Austin, the director, and Juan Carlos Licona Vasquez, responsible for the project. We would also like to thank Olvis Camacho who was responsible for studying traditional harvesting schemes. IBIF was technically and organizationally supported by the Albert-Ludwigs University Freiburg. The national regulatory body, Autoridad de Fiscalización y Control Social de Bosques y Tierra (ABT), and the National Forestry Directorate (DGGDF) partnered with the study and took advantage of the research findings, resulting in a change in National Forest Law 1700 (1996) article 75, which previously prohibited the use of chainsaws for the commercial milling of timber. The Central Indígena de Comunidades Originarias de Lomerío (CICOL) representing the Indigenous communities in Lomerio constituted the competent local partner for all decisions of relevance to the communities. A special thanks needs to go to all the people who participated in the study and their families. We also thank Tropenbos International, the Society for the Promotion of Forestry and Wood Industry Research (Gesellschaft zur Förderung der forst- und holzwirtschaftlichen Forschung) at the University of Freiburg im Breisgau, and the German Cooperation through the Deutsche Gesellschaft für Internationale Zusammenarbeit (GIZ) GmbH and its Integrated Forest Management for Reducing Deforestation Project—PROBOSQUE.

Conflicts of Interest

Juan Carlos Montero Terrazas is employed by GOPA Worldwide Consultants, and James Johnson is CEO of Canavalia Verde. The two companies were not involved in this study, and there is no relevance between this research and their company. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript; or in the decision to publish the results. The authors declare that this study received funding from STIHL company. The funder was not involved in the study design, collection, analysis, interpretation of data, the writing of this article or the decision to submit it for publication.

References

  1. USAID. Community Land and Natural Resource Tenure Recognition: Review of Country Experiences; USAID: Washington, DC, USA, 2016. [Google Scholar]
  2. Riester, J.; Fischermann, B. En Busca de la Loma Santa; Los Amigos del Libro: Santa Cruz de la Sierra, Bolivia, 1976. [Google Scholar]
  3. Almeida, F. Evaluating Formal Recognition of Forest Rights of Indigenous Peoples and Local Communities. In Tropical Forestry Handbook; Pancel, L., Köhl, M., Eds.; Springer: Berlin/Heidelberg, Germany, 2015. [Google Scholar] [CrossRef]
  4. Almeida, F. Legal Recognition of Forest Rights of Indigenous Peoples and Local Communities. In Tropical Forestry Handbook; Pancel, L., Köhl, M., Eds.; Springer: Berlin/Heidelberg, Germany, 2016. [Google Scholar] [CrossRef]
  5. Larson, A.M.; Barry, D.; Dahal, G.R.; Colfer, C.J.P. Bosques y Derechos Comunitarios: Las Reformas en la Tenencia Forestal; CIFOR: Bogor, Indonesia, 2010. [Google Scholar]
  6. UNCED. Forest Principles—Report of the United Nations Conference on Environment and Development (UNCED); UNCED: Rio de Janeiro, Brazil, 1992; Available online: https://digitallibrary.un.org/record/170821?ln=en (accessed on 4 January 2025).
  7. Borrini-Feyerabend, G.; Kothari, A.; Oviedo, G. Indigenous and Local Communities and Protected Area: Towards Equity and Enhanced Conservation. Guidance on Policy and Practice for Co-Managed Protected Areas and Community Conserved Areas; IUCN: Cambridge, UK, 2004; Volume XVIII, 111p, ISBN 2-8317-0675-0. [Google Scholar]
  8. RAISG (Red Amazónica de Información Socioambiental Georreferenciada). Amazon Under Pressure; RAISG: São Paulo, Brazil; ISBN 978-65-88037-07-2. Available online: https://www.raisg.org/en/publication/amazonia-under-pressure-2020/ (accessed on 6 February 2025).
  9. Dawson, N.M.; Coolsaet, B.; Sterling, E.J.; Loveridge, R.; Gross-Camp, N.D.; Wongbusarakum, S.; Sangha, K.K.; Scherl, L.M.; Phan, H.P.; Zafra-Calvo, N.; et al. The Role of Indigenous Peoples and Local Communities in Effective and Equitable Conservation. Ecol. Soc. 2021, 26, 19. [Google Scholar] [CrossRef]
  10. Mamo, D. (Ed.) The Indigenous World 2020; The International Work Group for Indigenous Affairs (IWGIA): Copenhagen, Denmark, 2020; 784p. [Google Scholar]
  11. Ford, J.D.; King, N.; Galappaththi, E.K.; Pearce, T.; McDowell, G.; Harper, S.L. The Resilience of Indigenous Peoples to Environmental Change. One Earth 2020, 2, 532–543. [Google Scholar] [CrossRef]
  12. Masaquiza, M. Challenges and Opportunities for Indigenous Peoples’ Sustainability; United Nations; Policy Brief No 101; Department of Economic and Social Affairs: New York, NY, USA, 2021. [Google Scholar] [CrossRef]
  13. The Rights and Resources (RRI). Who Owns the World’s Land? Global State of Indigenous, Afro-Descendant, and Local Community Land Rights Recognition from 2015–2020; Rights and Resources Initiative: Washington, DC, USA, 2023. [Google Scholar]
  14. Kusters, K.; de Graaf, M. Formalizing Community Rights to Forests: Expectations, Outcomes and Conditions for Success; Tropenbos International: Wageningen, The Netherlands, 2019. [Google Scholar]
  15. The Rights and Resources Initiative (RRI). Securing Community Land Rights: Priorities and Opportunities to Advance Climate and Sustainable Development Goals; Rights and Resources Initiative: Washington, DC, USA, 2017. [Google Scholar]
  16. American Forests. Principles for Sustainable Management of Global Forests. In Proceedings of the United Nations Conference on Environment and Development (UNCED), Rio de Janeiro, Brazil, 14 June 1992. [Google Scholar]
  17. Convention on Biological Diversity (CBD); United Nations Convention to Combat Desertification (UNCCD); United Nations Framework Convention on Climate Change (UNFCCC). The Rio Conventions: Action on Forests; CBD Secretariat: Monteral, QC, Canada, 2012. [Google Scholar]
  18. Pokorny, B.; Sabogal, C.; de Jong, W.; Stoian, D.; Louman, B.; Pacheco, P.; Porro, N. Experiencias y Retos del Manejo Forestal Comunitario en América Tropical. Recur. Nat. Y Ambiente/no.i 2008, 54, 81–98. [Google Scholar]
  19. Bolivia. Ley 1700 Nueva Ley Forestal de Bolivia; Bolivia, 1996. Available online: https://www.tribunalagroambiental.bo/wp-content/uploads/2021/01/ley_1700gaceta.pdf (accessed on 9 March 2025).
  20. Medina, G.; Pokorny, B.; Campbell, B. Favoreciendo el Desarrollo Local en la Amazonia: Lecciones de las Iniciativas de Manejo Forestal Comunitario; Forest Livelihood Briefs No 8; CIFOR: Bogor, Indonesia, 2008. [Google Scholar]
  21. Benneker, C. Dealing with the State, the Market and NGOs: The Impact of Institutions on the Constitution and Performance of Community Forest Enterprises (CFE) in the Lowlands of Bolivia. Ph.D. Thesis, Wageningen University and Research, Wageningen, The Netherlands, 2008. [Google Scholar]
  22. Pacheco, P. Smallholders and Communities in Timber Markets: Conditions Shaping Diverse Forms of Engagement in Tropical Latin America. Conserv. Soc. 2012, 10, 114–123. [Google Scholar] [CrossRef]
  23. Albornoz, M.; Cronkleton, P.; Toro, M. Estudio Regional Guarayos: Historia de la Configuración de un Territorio en Conflicto; Center for Labor and Agrarian Development, Center for International Forestry Research (CIFOR): Santa Cruz, Bolivia, 2008. [Google Scholar]
  24. van Dam, C. La Tenencia de la Tierra en América Latina: El Estado del Arte de la Discusión en la Región; IUCN Regional Office for South America: Quito, Ecuador, 1999. [Google Scholar] [CrossRef]
  25. Wit, M.; van Dam, J. (Eds.) Chainsaw Milling: Supplier to Local Markets; Tropenbos International: Wageningen, The Netherlands, 2010; Volume XXII, 226p. [Google Scholar]
  26. Lescuyer, G.; Cerutti, P.O.; Robiglio, V. Artisanal Chainsaw Milling to Support Decentralized Management of Timber in Central Africa? An Analysis Through the Theory of Access. For. Policy Econ. 2013, 32, 68–77. [Google Scholar] [CrossRef]
  27. Lescuyer, G.; Cerutti, P.O.; Tshimpanga, P.; Biloko, F.; Adebu-Abdala, B.; Tsanga, R.; Yembe-Yembe, R.I.; Essiane-Mendoula, E. The Domestic Market for Small-Scale Chainsaw Milling in the Democratic Republic of Congo: Present Situation, Opportunities and Challenges; Occasional Paper 112; CIFOR: Bogor, Indonesia, 2014; ISBN 978-602-1504-43-7. [Google Scholar]
  28. Mejia, E.; Pacheco, P.; Muzo, A.; Torres, B. Smallholders and Timber Extraction in the Ecuadorian Amazon: Amidst Market Opportunities and Regulatory Constraints. Int. For. Rev. 2015, 17, 38–50. [Google Scholar] [CrossRef]
  29. Quartey, J.D. Chainsaw Milling in Ghana: Assessing its Economic Impact. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  30. Folefack, A.J.; Darr, D. Implications of Legalizing Artisanal Chainsaw Milling on Social Welfare, Income Distribution and the Economic Performance of Sawyers in Cameroon. Int. For. Rev. 2022, 24, 534–559. [Google Scholar] [CrossRef]
  31. ABT. Informe Anual de Resultados: Gestión 2022–2023; ABT: Santa Cruz de la Sierra, Bolivia, 2023. Available online: https://abt.gob.bo/images/Revista_audiencia_o15_abril_compressed.pdf (accessed on 9 March 2025).
  32. Kusters, K.; Benneker, C.; Danga, S.; de Graaf, M.; Faure, N.; Greijmans, M.; Livingstone, J.; Louman, B.; Maindo, A.; Mpoyi, C.; et al. NGOs Facilitating Internal Governance Processes in Community Forestry Initiatives. Trop. Conserv. Sci. 2022, 15, 1–4. [Google Scholar] [CrossRef]
  33. De Jong, W.; Cano, W.; Zenteno, M.; Soriano, M. The Legally Allowable versus the Informally Practicable in Bolivia’s Domestic Timber Market. For. Policy Econ. 2014, 48, 46–54. [Google Scholar] [CrossRef]
  34. Müller, R.; Montero, J.C.; Mariaca, G. Causas, Actores y Dinámicas de la Deforestación en Bolivia 2010–2022; CEDLA: La Paz, Bolivia, 2024. [Google Scholar]
  35. Pacheco, P. Los Dilemas de las Políticas y el Manejo Forestal Comunitario: Algunas Reflexiones Desde el Caso Boliviano. In Proceedings of the IV Reunión sobre Investigación Forestal “Hacia un Modelo de Manejo Forestal Comunitario”, Cobija, Bolivia, 3–5 September 2008; Available online: https://www2.cifor.org/tenure-reform/data/files/bolivia/conference_papers/cp_bolivia2.pdf (accessed on 9 March 2025).
  36. Cano, W.; Van de Rijt, A.; De Jong, W.; Pacheco, P. Public Innovation and Changes in Communal Access to Timber in the Northern Bolivian Amazon. Int. For. Rev. 2019, 21, 4. [Google Scholar] [CrossRef]
  37. Navarro, G. Clasificación de la Vegetación de Bolivia; Centro de Ecología Difusión Simón I. Patiño: Santa Cruz de la Sierra, Bolivia, 2011. [Google Scholar]
  38. CFB. En Bolivia el 80% de la Producción de Madera es de Operaciones Comunitarias; Camera Forestal Bolivia: Santa Cruz de la Sierra, Bolivia, 2024; Available online: https://www.cfb.org.bo/noticias/comercial/en-bolivia-el-80-de-la-produccion-de-madera-es-de-operaciones-comunitarias (accessed on 9 March 2025).
  39. de la Vega-Leinert, A.C. Too Small to Count? Making Land Use Transformations in Chiquitano Communities of San Ignacio de Velasco, East Bolivia, Visible. J. Land. Use Sci. 2020, 15, 172–202. [Google Scholar] [CrossRef]
  40. Riester, J. Aspectos Fundamentales de la Cultura Intangible y Social de la Nación Chiquitana en la Obra; Biblioteca del Bicentenario de Bolivia-BBB: La Paz, Bolivia, 2021. [Google Scholar]
  41. CEJIS. Incendios en Territorios Indígenas de las Tierras Bajas de Bolivia: Análisis del Periodo 2010–2020; CEJIS: Santa Cruz, Bolivia, 2021. [Google Scholar]
  42. Markopoulos, M.D. The Impacts of Certification on Community Forest Enterprises: A Case Study of the Lomerío Community Forest Management Project, Bolivia; Oxford Forestry Institute: Oxford, UK, 1998; Available online: https://www.iied.org/7544iied (accessed on 25 January 2025).
  43. Montero, J.C.; Mendoza, K.; Pokorny, B.; Ascarrunz, N.; Johnson, J. Factibilidad Técnica y Financiera del Aserrío Móvil por Productores Forestales Indígenas Chiquitanos: En Búsqueda de Nuevas Alternativas para Reactivar el Sector Forestal en Bolivia; Instituto Boliviano de Investigación Forestal (IBIF): Santa Cruz de la Sierra, Bolivia, 2021; ISBN 978-99974-848-1-9. [Google Scholar]
  44. Pasiecznik, N. Sawmilling with Chainsaws: A Technical Overview. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  45. Brotto, L. The Impact of REDD+ Projects on Chainsaw Milling in Peru. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  46. Langbour, P.; Roda, J.M.; Koffi, Y.A. The Chainsaw Supply Chain in Cameroon: The Northern Trail. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  47. Muthike, G.M.; Shitanda, D.; Kanali, C.L.; Muisu, F.N. Chainsaw milling in Kenya. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  48. Marfo, E. Chainsaw milling in Ghana: Context, drivers and impacts. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  49. Keenan, R.J.; Grigoriou, J.; Yosi, C. Financial analysis of small-scale harvesting in Papua New Guinea. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  50. Roda, J.M.; Langbour, P.; Shantiko, B. The chainsaw economy in Tanimbar Archipelago, Indonesia. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
  51. Eckelmann, C.M.; Gallion, A.; Simon, A.; Mahabir, B.; Prosper, A.; Morgan, A. Chainsaw milling in the Caribbean. In Chainsaw Milling: Supplier to Local Markets; Marieke, W., van Dam, J., Eds.; Tropenbos International: Wageningen, The Netherlands, 2010. [Google Scholar]
Figure 1. Map of the TIOC Lomeria in the Chiquitanía region in Bolivia.
Figure 1. Map of the TIOC Lomeria in the Chiquitanía region in Bolivia.
Forests 16 00496 g001
Figure 2. Average times to harvest and process a tree with the chainsaw per activity (N = 16).
Figure 2. Average times to harvest and process a tree with the chainsaw per activity (N = 16).
Forests 16 00496 g002
Figure 3. Proportion of cost categories for the processing of timber using low-input motor–manual harvesting.
Figure 3. Proportion of cost categories for the processing of timber using low-input motor–manual harvesting.
Forests 16 00496 g003
Table 1. Measurements of the 16 trees felled for the study.
Table 1. Measurements of the 16 trees felled for the study.
SpeciesNAverage
dbh (cm)Commercial Height (m)Volume
(m3)
Total Height (m)
Cuchi (Astronium urundeuva)956.17.881.2620.33
Curupaú (Anadenanthera colubrina)262.58.501.2716.00
Sirari (Copaifera chodatiana)273.55.801.2521.00
Tajibo (Tabebuia sp)348.35.900.5117.33
Total1657.67.331.1219.31
Table 2. Prices for relevant items used for calculation for the year 2019.
Table 2. Prices for relevant items used for calculation for the year 2019.
ItemPrice
Chainsaw STIHL MS 661USD 1015.00
Attachment Big Mill Basic (Logosol)USD 1506.00
Portable Mill Bristol Guide Bar (Marco guía)USD 330.00
Cargo Bike Dayand-PUMA (Motochata)USD 1250.00
Depreciation15% per year
Materials and minor toolsUSD 93.50 per person
OilUSD 7.03 per liter
FuelUSD 0.54 per liter
Maintenance (cleaning the devices, replacing worn parts, skid trail maintenance)2.96 USD per m3
Daily rate for a worker14.40 USD per day
Personal protective equipment109.00 USD per person
First aid kit40.00 USD per person
Food6.45 USD per person
Average price of boards and planks produced (as in the district capital Concepción)5.52 USD per m3
Table 3. Principle products obtained by local chainsaw milling.
Table 3. Principle products obtained by local chainsaw milling.
ProductDescriptionStandard DimensionVolumePrice *
m3USD/UnitUSD/m3
Triangular fence postsForests 16 00496 i001A longitudinal portion of wood triangular shape, with a base typically of 13 cm and a height of 12 cm. The length is 2.20 m used for fence posts or for dividing paddocks in livestock activities.10 cm × 10 cm × 12 cm × 220 cm0.0172.87169
Straining or corner postsForests 16 00496 i002Rectangular or round posts range from 4″ to 8″ and up to 3 m long used in cattle corrals.20 cm diameter × 250 cm width0.07917.24218
LintelForests 16 00496 i003A wide solid structure, used to support the weight of a roof or concrete over doors or windows of a dwelling. The lintel is less than the length of the gables and its dimensions fit 4″ high × 8″ wide × 2 m long.15 cm × 15 cm × 300 cm0.06717.24257
StrutsForests 16 00496 i004Rectangular piece to aid in securing corrugated iron or tiles used for roofing. Dimensions vary according to need but are typically 2″ × 2″ inches.5 cm × 5 cm × 300 cm0.012.16216
Roof beamForests 16 00496 i005The rectangular wood is utilized for constructing roof supports, which are shaped as either triangles or rectangles. The dimensions of the wood are 4″ in width and 2″ in height for use with zinc roofing, or 6″ in width and 2″ in height for shingles. The length of the wood ranges from 2 m to 5 m, depending on the required roof size.5 cm × 15 cm × 400 cm0.037.33244
Cross beamForests 16 00496 i006Rafters are also rectangular timbers used for roof supports, but, unlike the scissors, they are self-supporting structures. When a roof is assembled, the rafters are placed parallel and perpendicular to the battens. Their most common dimensions are between 5″–7″ wide and 2″ high. The longer the better, but from 15′ and up are acceptable, unless for smaller constructions.15 cm × 10 cm × 300 cm0.0459.63214
PlanksForests 16 00496 i007Planks are wider than other products and are used for different purposes, ranging from the manufacture of furniture to the production of flooring or wooden utensils. The width is variable but the thickness is generally between 1″ and 2″. The board is considered short if it is less than 8′, and long, if greater than 8′.10 cm × 2.5 cm × 300 cm0.00751.58211
* Average prices in Lomerio in May 2022.
Table 4. Total production volume of the 16 sample trees by product category.
Table 4. Total production volume of the 16 sample trees by product category.
CategoryVolume (m3)Proportion (%)
Triangular fence posts3.18257.7
Roof beams1.58428.7
Straining pots0.4187.6
Beams0.1462.6
Lintel0.0831.5
Planks0.0581.1
Struts0.0480.9
Total5.520100.0
Table 5. Yields per product category.
Table 5. Yields per product category.
Sub CategoryProduct CategoryPrinciple SpeciesLog Volume
(m3)
Product Volume (m3)Yield (%)
Struts, roof beams, lintels, and cross beamsConstructionTajibo8.452.2826.95
Simple milled planksBoardsTajibo1.490.063.91
Triangular fence posts and straining postsPostsCuchi, Sirarí, Curupaú9.453.1833.68
Total 17.905.52
Average 1.120.3429.34
Table 6. Cost related to the legality of forest production in Bolivia.
Table 6. Cost related to the legality of forest production in Bolivia.
ItemExplanationCost Estimates (USD)
TaxesFlat-rate taxation of 8% on the final pricee.g., 13.52 USD/m3 (posts) and 19.52 USD/m3 (boards)
Forestry engineer (provided and charged by the responsible governmental agency)Sign and endorse both the information and documentation coming from the communityeither 720 USD per month or 1–5 USD/m3 in the case of larger volumes
Forestry regulation feeCalculated on a daily updated index (35 Housing Development Units (Unidad de Fomento de la Vivienda-UFV) per ha)12.95 USD/ha
Forestry patentFixed value to be paid to the governmental forest authority to realize the yearly management plan1 USD/ha
Yearly harvesting plan (POAF)Mapping of trees for traceability and monitoring purposes20 USD/ha
Registration of the processing centerwhether fixed or mobile.~120 USD per year
Transport permits (certificate of origin–CFO)To be presented to the forestry authority for transport of the harvest regardless of volume5.10 USD/20 m3
Table 7. Comparative performance of technologies by board size.
Table 7. Comparative performance of technologies by board size.
LogProduct CategoryYields
N(m3)Short (m3)Long (m3)Total (m3)Short (%)Long (%)Total (%)
Free hand4615.331.454.856.309.4931.6241.11
Guide bar3612.723.701.845.5429.0714.4443.88
Logosol5319.632.476.408.8712.6032.5945.20
Total13547.687.6213.0920.71
Table 8. Performance of the three tested transport options.
Table 8. Performance of the three tested transport options.
Cargo BikeHorseHuman Power
Time (h)%h/m3Time (h)%h/m3Time (h)%h/m3
Loading and Dispatch2.70160.262.50190.500.501.00.10
Transport4.60270.455.90441.1840.5081.78.32
Unloading and Stacking2.45150.241.50110.301.202.40.25
Cubing1.5590.150.5040.100.901.80.18
Total productive time11.30671.1010.40782.0843.1086.98.85
Non-productive time5.50330.542.90220.586.5013.11.33
Total Time16.801001.6413.301002.6649.60100.010.18
Table 9. Financial results of the three processing options combined with Cargo Bike transport.
Table 9. Financial results of the three processing options combined with Cargo Bike transport.
Initial Investment *
(USD)
Internal Rate of Return (%)Net Present ValueBenefits/CostNet Financial Result (USD/m3)
Logosol equipment377174.59322.2912.8128.02
Guide bar2595118.62404.6234.2830.32
Freehand2265188.31667.3486.6837.93
* for details, see [43].
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Pokorny, B.; Montero Terrazas, J.C.; Johnson, J.; Mendoza Ortega, K.; Cano Cardona, W.; de Jong, W. Making Timber Accessible to Forest Communities: A Study on Locally Adapted, Motor–Manual Forest Management Schemes in the Eastern Lowlands of Bolivia. Forests 2025, 16, 496. https://doi.org/10.3390/f16030496

AMA Style

Pokorny B, Montero Terrazas JC, Johnson J, Mendoza Ortega K, Cano Cardona W, de Jong W. Making Timber Accessible to Forest Communities: A Study on Locally Adapted, Motor–Manual Forest Management Schemes in the Eastern Lowlands of Bolivia. Forests. 2025; 16(3):496. https://doi.org/10.3390/f16030496

Chicago/Turabian Style

Pokorny, Benno, Juan Carlos Montero Terrazas, James Johnson, Karen Mendoza Ortega, Walter Cano Cardona, and Wil de Jong. 2025. "Making Timber Accessible to Forest Communities: A Study on Locally Adapted, Motor–Manual Forest Management Schemes in the Eastern Lowlands of Bolivia" Forests 16, no. 3: 496. https://doi.org/10.3390/f16030496

APA Style

Pokorny, B., Montero Terrazas, J. C., Johnson, J., Mendoza Ortega, K., Cano Cardona, W., & de Jong, W. (2025). Making Timber Accessible to Forest Communities: A Study on Locally Adapted, Motor–Manual Forest Management Schemes in the Eastern Lowlands of Bolivia. Forests, 16(3), 496. https://doi.org/10.3390/f16030496

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