Skip to main content

Stingless bees: uses and management by meliponiculturist women in the Chaco region of Bolivia



Stingless bees have a great value as main pollinators of wild flowering and cultivated plants, thus playing a fundamental role in the maintenance of biodiversity and food security in Latin America. Despite their importance, stingless bees face numerous threats causing alarming population declines. Moreover, stingless bees have a great cultural and traditional value, since most products from the hive are used for a wide variety of purposes. A growing number of initiatives are encouraging the breeding of these bees, through training courses and modern management techniques. This study documents the knowledge on stingless bees and their products that meliponiculturists from the Chaco region of Bolivia have, as well as the influence that meliponiculture initiatives have on the management and general knowledge of the bees.


Local richness and diversity of stingless bees was calculated using Hill numbers. Structured interviews were conducted with 59 meliponiculturists in order to characterize traditional and formal knowledge on stingless bees and meliponiculture. Generalized linear models were applied to assess the influence of training courses on the management of the bees. Also, a relative cultural importance index was calculated for each species.


Twelve Meliponini species were identified, and 15 local names were reported with morphological, defensiveness behavior, and nest description. There was no significant difference in the knowledge between different ethnical backgrounds or ages. A significant difference was observed in the use of supplementary feeding and assisted division, but none in the success in racking hives or in pest management, regarding the number or courses taken. The relative cultural importance index recorded 30 specific uses for bee products grouped in four categories, from which 29 were attributed (but not exclusively) to Tetragonisca angustula, making it the most versatile species.


The products of the hive, especially honey, are used for a wide variety of purposes, mostly in medicine. These uses are mostly attributed to just one species, T. angustula, in coincidence with what was taught in meliponiculture training courses by NGOs. The influence of formal knowledge is mostly positive, but it is recommended that other meliponini species are taken into account as well.


The importance of bees as the main pollinator of a great variety of wild flowering plants and almost 70% of all cultivated plants is worldwide recognized [1,2,3], but most people are unaware that more than 20,000 species of bees around the world are responsible for this ecosystemic service [4]. In the Neotropics, around 10% of the approximately 5,000 bee species described belong to the tribe Meliponini, commonly known as stingless bees on account of one of their main characteristics: a stunted sting [5,6,7]. Depending on the species, these eusocial bees normally live in permanent colonies with one queen and between 3000 and 100,000 workers [8]. Stingless bees are the most common and abundant bees in many areas of this region and represent approximately 70% of all eusocial bees [8, 9]. Hence, they play a fundamental role in the maintenance and perpetuity of biodiversity in many ecosystems; moreover, they are crucial for food security in Latin America as they are important pollinators of a vast number of cropping systems [8, 10, 11].

Despite their importance, bees and many other pollinators face numerous threats, including habitat loss due to deforestation, wildfires, changes in land use, excessive use of pesticides, and climate change, which are causing alarming population declines that will have severe consequences for the ecosystems and global human diet, health, and economies [2, 3, 12, 13]. For these reasons, efficient and long-term strategies for conservation of stingless bees (and other pollinators) is a pressing matter [14, 15]. Furthermore, there is a huge knowledge gap on these bees, since only about 6% of scientific publications deal with stingless bees compared to other eusocial bees such as honeybees and bumble bees [9].

Stingless bees also have a great cultural value for many indigenous and rural populations [16,17,18,19]. The breeding of stingless bees is known as meliponiculture and dates back to the pre-Columbian Maya civilization in Mesoamerica, as documented through ancient paintings [20,21,22]. These bees are bred mainly for their honey, which they stock in cerumen pots, making it relatively easy to harvest [23], and for other important resources obtained from the hives such as cerumen, propolis, and pollen [18, 24]. Hive products are used for a wide variety of religious, medical, nutritional, and economic purposes [16, 25, 26]. In Bolivia for example, the Yuqui, a Tupi–Guaraní-speaking folk from the Chapare region, use a mixture of cerumen and plant resin to manufacture arrows for hunting [27]; the Siriono, an indigenous population from the Amazonas, feed on larvae (actually the complete brood cells) and pollen, and use honey to prepare fermented drinks [28]; and the Ayoreos of Southern Bolivia have a particularly strong connection to bees and hive derivatives, consuming honey as a sweet and for religious purposes, and cerumen as a key material to make anything from instruments to cloths [16]. Likewise, many rural populations benefit from stingless bee products like honey, pollen, or propolis, either for self-consume as medicine to treat various diseases or as an additional income source by selling these products [20]. While meliponiculture is widely spread in many regions of Latin-American, in Bolivia meliponiculture is not very common; instead, bee products are most commonly harvested from wild hives, thus destroying them and endangering bee populations [16].

Despite their cultural importance, traditional uses of honey and other hive products have decreased over the last decades since it has become harder to find wild hives near villages due to over-harvesting and logging, which reduce their habitat and suitable nesting sites [29]. Hence, many people are starting to practice apiculture instead of meliponiculture because honeybees produce more honey [30]. On the other hand, in Bolivia and many other Latin-American countries, there has been a great number of government, NGOs, and private initiatives to enhance the development of meliponiculture in rural areas. For example, in Brazil and Colombia meliponiculture has developed very quickly, triplicating the number of bee boxes in 2005 and becoming important for the economy of many rural and Indigenous families [20]. This fast development is due to the advances in the knowledge and understanding of meliponine biology, which gave way to improvement in management techniques, especially in the division of the hive, processing of honey, and colony food supplementation, as well as to social and governmental projects which encourage meliponiculture and these new techniques [20, 31]. In Bolivia, government and NGOs’ social initiatives to promote meliponiculture are becoming increasingly popular especially among women in rural areas as a source of sustainable incomes and also as a way of empowerment. Although most of these initiatives tend to leave behind cultural aspects and are mainly focused on sustainably improving the economic situation of rural communities, by simply promoting meliponiculture they are also helping bees’ conservation [32].

In the Boliviano-Tucumano forest of Chuquisaca in southern Bolivia, in the municipalities of Villa Vaca Guzmán and Monteagudo, a large-scale meliponiculture initiative from a local Foundation (PASOS) has taken place since 2015, where more than 200 women from different communities and ethnical backgrounds have been trained in meliponiculture. PASOS is financed by the German Agency for International Cooperation GmbH (GIZ for their initials in German—Deutsche Gesellschaft für Internationale Zusammenarbeit GmbH) and aims to increase women's own income in the Chaco region of Chuquisaca through the ecological business development of the production of stingless bees’ honey. To train such a large number of producers, PASOS focuses on training representatives from each community who later replicate what they learn with the other women of the communities. Additionally, communal meliponaries (also called field schools) have been installed in some regions so that practical training can be carried out locally.

In the Chaco region in Chuquisaca, the main economic activities are agriculture and raising livestock. Most of the products are used for self-consumption, although some are also commercialized. The main products are peanuts, chili peppers, corn, beans, and citrus fruits; meliponiculture and apiculture have also become important, leading to small-scale production consumed mainly by the producing families. The Villa Vaca Guzmán and Monteagudo municipalitys are multiethnic, mainly from Guarani, Quechua, and Spanish stock [33, 34]. Both municipalities reported a high percentage of the population living in poverty due to Unsatisfied Basic Needs criteria (Monteagudo 74.4%, Villa Vaca Guzmán 82.1%), higher than the national average (70.9%) [35].

In order to improve conservation and management strategies in the Chaco region, it is important to document the current state of knowledge that women have about stingless bees’ management and meliponiculture practices. In this study, the resulting knowledge from training activities is referred to as formal knowledge, while previous knowledge, even though it is not ancestral, is referred to as traditional. The present study documents, characterizes, and analyzes structured interviews of women from rural communities in the Chaco-Chuquisaqueño region, in order to better understand traditional and formal knowledge of stingless bees and practices in meliponiculture performed by them. It is also documented how traditional practices have changed or evolved after having formal education on meliponiculture through NGOs acting in the region. Additionally, bee surveys and identification were conducted to assess stingless bee diversity of the region, and thus explore its relationship with cultural importance and to evaluate its conservation status.


Study area

The study was carried out in the municipalities of Villa Vaca Guzmán, best known as Muyupampa (19°54′ S, 63° 43′ W, 600–2800 m.a.s.l.) and of Monteagudo (19° 30′ S, 63° 45′ W, 2000 m.a.s.l.), both located in the southeastern region of the Chuquisaca department, Bolivia. The northern region of both municipalities, where the study took place, belongs to the biogeographic region of the Boliviano-Tucumano forest, characterized by a mesotropical subhumid pluviseasonal bioclimate. This region presents high montane ecological floors with an altitude of 2700–3800 m above sea level [36, 37], where some of the main tree species are “palo Barroso” (Blepharocalyx salicifolius), “mato” (Myrcianthes pseudomato), “laurel” (Cinnamonum porphyria), “cedro” (Cedrela lilloi), “pino negro” (Podocarpus parlatorei), “yuruma” (Myrsine coriaceae), among others [38]. In general terms, this area is well conserved, since a large proportion of it lies within the limits of the National Park “Serranía del Iñao” (Fig. 1).

Fig. 1
figure 1

Map of study area. The red dot indicates where the bee surveys were taken, within the communities of Ticucha and La Tapera, at Villa Vaca Guzmán municipality in Chuquisaca–Bolivia

Stingless bee survey and identification

Bee surveys to determine local bee diversity were conducted during the end of the 2022 rainy season (February 11–16, March 16–24, and May 6–8) in the surroundings of the communities of La Tapera (19° 40′ 42.75′′ S, 63° 48′ 58.4′′ W) and Ticucha (19° 37′ 23.01′′ S, 63° 49′ 29.9′′ W), approximately 20 km northeast from Monteagudo. Seven transects (200 m long) were established at a range of no further than 2 km from the communities (4 in La Tapera, 2 in Ticucha and 1 in La Angostura). Sites were chosen based on high accessibility and low human traffic (Fig. 1). A group of three pan traps of different colors (white, blue, and yellow) were placed every 20 m along the transects, so that every transect had 33 pan traps in total [39]. Although previous studies had shown that the minimum distance between color traps should be 5 m [40], it was decided to place them every 20 m to cover a larger area. Also, three air white traps were hung approx. 3 m above ground along the same transects, one every 100 m. All traps were filled two-thirds with soapy water (to break the surface tension of the water), which was prepared by mixing a few drops of unscented liquid dishwashing detergent per liter of tap water. Traps were deployed for approx. 9 h, being set up early in the morning and collected in the evening, just one time in each transect. Additionally, targeted netting surveys were conducted along the transects and around the communities. Netting time varied between 1 and 3 h, during 7 says (when de transects were set) and included actively catching and searching for stingless bees between flower patches and flowering trees.

Samples collected from the traps were placed in plastic vials containing 70% ethyl alcohol. Samples collected with the net were transferred to a lethal chamber with ethyl acetate and conserved dry before being transported to the laboratory. In the laboratory, insects were pinned, labeled, boxed, and identified to genus level with the help of specialized identification keys [41,42,43,44,45,46]. Voucher specimens were stored at the Chemical Ecology Laboratory insect collection at Universidad San Francisco Xavier de Chuquisaca, Sucre, Bolivia. Additionally, samples from some of the meliponaries were taken and identified, if possible to species level.

Demographic profile of the subjects interviewed

Among the 52 female informants, half of them were aged between 20 and 39 (young) and half between 40 and 60+ (adults). Male participants were mainly adults (6 of the 7 participants). Most informants (54) came from communities of the municipality of Villa Vaca Guzmán, mostly from La Tapera and from Ticucha (18 from each) and other seven communities; the other five belonged to four different communities from the municipality of Monteagudo. All the interviewed persons carried out meliponiculture as an alternative activity; 45 of the women said their primary occupation was housework, three had apiculture as their main activity, and the rest of the interviewees (males and females) had other occupations such as farmer, teacher, nurse, or carpenter. All the people surveyed were asked whether they felt identified with an indigenous ethnic group; the majority (42) identified themselves as “mestizo” (this also included those who did not identify themselves with any ethnic group), and only eight interviewees identified themselves as Guarani and only seven as Quechuas.

Stingless bee local knowledge and uses

To assess and document knowledge, practice, and management techniques by local people, semi-structured interviews were conducted with 52 women and 7 men (Fig. 2). The interviewed women were part of the meliponiculture project carried out by the Foundation “PASOS.” The men interviewed were mostly these women’s husbands or relatives who were also very interested and involved in meliponiculture and had received the same training along with the women. To carry out the interviews, meetings were organized in the communities, with the participation of all meliponiculturists from Ticucha and La Tapera communities (Villa Vaca Guzmán Municipality). In Monteagudo, meliponiculture representatives from other smaller communities in the area also participated. All interested women were invited to participate in the interviews. The interviews were conducted by previously trained biology thesis students from Universidad Mayor Real y Pontificia de San Francisco Xavier de Chuquisaca (USFX), trained by the coordinators of the study. The interviews lasted approximately 1 h and were conducted in Spanish, the most spoken language in the area. On the question of ethnicity of the interviewees, “mestizo” corresponded to interviewees not belonging to indigenous ethnical group, as well as those who did not feel identified with any ethnic group in particular.

Fig. 2
figure 2

A One of the interviewed meliponiculturists in her meliponary. B Scaptotrigona sp, known locally as Negro

The interviews consisted of 90 questions divided into 5 parts which addressed the following topics: (a) general knowledge about stingless bees, (b) meliponiculture and hive management, (c) honey harvesting and uses, (d) other bee products and their uses, and (e) processing of hive products and their use in traditional medicine. Before the interview, the participants were informed about the study aims, and written informed consent was obtained from all those involved. The open-source app ODK collect (V. 2022.3.4) was used to carry out the interviews.

Ethics approval and consent to participate

International ethical recommendations for research with human beings were followed to protect participants' rights and well-being. The Bioethics Committee of the Faculty of Medicine of the University of San Simón, Cochabamba, Bolivia, approved the research study protocol. An educative process was performed before the information letter. After that, a written informed consent form was provided to each participant. The questionnaire was completely anonymous, voluntary participation was always respected, the information was also handled confidentially, and any situation that could harm the communities was considered. Additionally, we adhere to the principles of the Code of Ethics of the International Society of Ethnobiology (ISE) [47] by recognizing the inalienable rights of the local community over their territories and the use of their natural resources, their right to self-determination, and the role of communities as traditional guardians of culture and ecosystems. On the other hand, the active participation of the meliponiculturists in all phases of the project was encouraged to promote capacity-building, all the communication generated in the project was socialized, and their culture and organization was respected in all steps of the project.

Data analysis

Local stingless bee diversity and richness were analyzed using equations based on Hill numbers q = 0 and q = 1 as proposed by Chao et al. [48]. Integrated extrapolation and rarefaction curves were developed, and thus, the estimated richness was calculated for each Hill number, where q = 0 estimates the species richness and q = 1 weighs the number of species based on relative abundance, obtaining a diversity value based on the exponential of the Shannon index. Also, a sample completeness curve was constructed to find out how complete was the sampling protocol. These analyses were carried out using the iNEXT V.2.0.20 package [48,49,50] from the statistics free Software R version 4.2.1. To determine the cultural importance of the different species of stingless bees, based on the information retrieved from the interviews, the relative cultural importance index (RCI) (Fig. 3) was calculated. This quantitative ethnobiological technique was developed by Bennett and Prance [51] to calculate the relative importance of medicinal plants, but an adaptation was suggested by Gonzales et al. [52] and later by Bhatta et al. [53] to analyze the cultural importance of stingless bees. For this adaptation, first main categories of use (C) and specific uses (U) for the bee products are identified (Additional file 1: Appendix 3), and the following formula used to calculate RCI.

Fig. 3
figure 3

Formula used to calculate the relative cultural importance index

Here, RCIi is the relative cultural importance of species i, Ci is the number of categories reported in the interviews and Cn is the total number of categories, Ui is the number specific uses reported in the interviews and Un is the total number of specific uses. For example, for M. rufiventris two of the four use categories were reported; thus, it had a C value of 2/4 = 0.5. Two out of the 30 specific uses were recorded; thus, it had a U value of 2/30 = 0.07. The combined scores were 0.57 out of a maximum possible value of 2. To express it in a scale of 100, the combined scores were multiplied by 50, thus resulting in a relative importance of 28.33 for M. rufiventris.

The data obtained from the interviews were systematized and ordered in frequency tables. The frequencies obtained were transformed to percentages for further analysis; moreover, generalized linear models (GLM) were used to assess whether there was any influence of the interviewees' age (young = 20–39 years old, adult = 40–60+ years old) or ethnicity (Mestizo, Guaraní and Quechua) on their traditional knowledge about bee diversity (number of reported species). Training courses were given by PASOS on the following topics: Main characteristics of stingless bees, management of modern hives, the harvest of honey and other bee products, and product transformation. GLMs were used to assess how the number of these courses (0, 1, 2, 3, 4) influenced the successful management of the bees regarding: (A) colony division (success, failure, and no division), (B) supplementary feeding (yes and no), (C) racking of wild hives into boxes (success and failure), and (D) practice of pest management (yes and no). In all cases, a quasipoisson distribution was used. A Spearman’s rank correlation was used to test for an association between the number of hives bred for each species and the calculated RCI. This was done to see whether the most bred species are also the most culturally important.


Stingless bee survey and identification

During the field trips, a total of 36 individuals were collected using the different sampling methods. Twelve morphospecies of stingless bees were identified, which belonged to 8 genera (Lestrimelitta, Melipona, Paratrigona, Plebeia, Scaptotrigona, Scaura, Tetragonisca, and Trigona), with Plebeia being the most abundant species (Table 1).

Table 1 Number of stingless bee species (n) collected and identify to genera in the municipality of Muyupampa, Bolivia

It was confirmed that the sampling effort was adequate since high values (94.88%) of completeness of the sample were reached. For q = 0, it was estimated a species richness of 13 species, only one more species than observed (Fig. 4a). As for the exponential of the Shannon index (q = 1), an equivalent number of 10 equally common species was observed and 12 estimated (Fig. 4b).

Fig. 4
figure 4

a Sample completeness curve. b Rarefaction and extrapolation curves of species diversity base on the Hill numbers q = 0 (species richness) and q = 1(exponential of the Shannon index). The bands of each curve correspond to the confidence intervals calculated by 95%

Local knowledge on stingless bees

The interviewees reported 15 different species of honey-producing bees with their local names (Table 2). Fourteen of them are stingless bees, and one is the Africanized honeybee (Apis mellifera), locally known as Abeja extranjera. Among the stingless bees, the most cited and valued species were Señorita which was mentioned by all interviewees, followed by Tancarillo and Negro. Other the species locally managed in the meliponaries were identified as Tetragonisca angustula, Melipona rufiventris and Scaptotrigona sp. As summarized in Table 2, local people identified bees based on morphological and behavioral characteristics, and for some species, they were also able to describe their nesting biology.

Table 2 Local knowledge on stingless bees at the municipality of Muyupampa and Monteagudo, Chuquisaca

The well-known Señorita (T. angustula) was recognized by its slim body, small size, yellow–black colors (sometimes also described as dark brown), and very docile behavior. Local people know that this bee builds its nest in a variety of places, including hollow trunks, branches, or logs, underground or even on the wall or poles of the houses, and they build a small yellowish cylindrical cerumen entrance. Another well-known species (mentioned by 71.7% of the interviewees) is the totally black bee Negro (Scaptotrigona sp1), characterized by its medium size, and by the long cylindrical ornament, they build at the entrance of its nest at hollow trees or underground. According to most people, they have very aggressive behavior; however, some people described it as docile, which could be a confusion with another Scaptotrigona species. One person said that the bees were aggressive when the entrance was big, and the bees were docile when the entrance was small. Almost half of the local people (45%) mentioned the bee Tancarillo (M. rufiventris), distinguished by its large size, its yellow/orange color with black stripes, and its docile behavior. It was mentioned that this bee nests on hollow trees and logs and is hard to find since it builds small entrances. Two other black bees, Burro and Burra (cited by 23.3% and 10% of the interviewees, respectively) were described very similarly to the Negro, as docile, midsize, completely black, and nests with long cylindrical entrances built on hollow trees or underground. The bee known as Boca de sapo or Sapito was mentioned by 21.7% of the interviewees and identified by its small size, black color, and docile behavior. They nest in hollow trees and build around the entrance a characteristic ornament that reminds of a frog’s mouth. The other eight stingless bee species were cited by 5% or less of the interviewees. There was no significant difference neither in the influence of age (p = 0.698) or ethnicity (p = 0.554) on the number of species known by the local people, nor in the interaction between age and ethnicity on the number of known species (Additional file 1: Appendix 1 and Appendix 2).

When asked about the places where stingless bees were most commonly seen, 70% of the interviewees answered the forest with Señorita being the most common bee. These bees can also be seen in other places, such as the riverside, open fields, crops, or orchards, but not as often as in the forest. Nevertheless, many of the interviewees (43%) affirmed that in the last 5 years the population of bees had decreased and that this was principally because of the wildfires, climate change and pesticides, but also because the nests were withdrawn from the forest to be bred in boxes. On the other hand, another 39% of the interviewees said that the bee population had actually increased in the last 5 years mostly because of artificial breeding (Table 3). Despite these different perceptions, most of these local meliponiculturists (95%) agreed that bees generally benefit humans and the environment. Honey production was the most mentioned benefit that bees brought (mentioned by 62% of the interviewees) followed by politization (47%), propolis production (23%), and medicine (10%).

Table 3 Informants’ perception on the abundance and conservation status over the last 5 years of local stingless bees

Management techniques

Most interviewees had between 1 and 4 training courses held mainly through the PASOS Foundation. The most attended topics were the following: (1) management of modern hives, attended by 48 of the interviewed women. This course focused on the breeding of bees: the parts of a rational hive (boxes), artificial feeding to strengthen the colonies, divisions, and how to move wild colonies to rational hives. (2) Harvest of honey and other bee products, attended by 41 of the interviewed women. This course aimed to show how to harvest and later to preserve the honey and other hive products, taking into account sanitary measures. (3) Main characteristics of stingless bees, attended by 33 of the interviewed women. This course explained most of the characteristic traits of these bees, such as their social behavior and caste system, reproduction, what they feed on, and how honey is produced.

The most frequently managed stingless bee of this region is Señorita which is being bred by all the interviewees (100%), followed by Negros bred by 20% of the interviewees, Tancarillos 14%, and Sapitos 8.5%. Every meliponiculturist owns between 1 and 25 hives of Señorita, between 1 and 10 hives of Negro, and between 1 and 3 hives of some of the other stingless bee species. On the other hand, A. mellifera is being managed by 68% of the interviewees. Adding all the hives reported by the interviewees, there are in total 702 hives of honeybees, 617 hives of Señorita, 38 hives of Negro, and 27 hives of Tancarilo. A strong significant positive correlation (p = 0.0072, r = 0.881) was found between the percentage of people that own hives of a bee species and the mentioned index of such species, as shown in Table 2.

Some meliponiculturists (22%) obtained their hives by buying them, probably from other local meliponiculturists, while others (6%) got them through traps, dividing them, or as a donation. But most of the stingless bee hives (93%) owned by the interviewees originated from wild hives that were removed from their natural environment in the forest and placed inside wooden boxes. To remove these hives, around 33% of the times the trees or branches supporting the nest were cut off; in the other cases, the hives could just be removed since it was inside a dead log, or it was easier to remove them without cutting off the tree or branch. The survival rate of the hives that underwent these transfer processes was very high according to 55% of the interviewees, but 30% stated that some or most of the hives did not survive the transfer to the box. Once the hives were in the boxes, they were kept mostly around the house or in the meliponaries, where they were taken care and managed in different ways. In 88% of cases, hives hosted some pests in the last 5 years, mostly Phoridae flies, and attacks by other bees or ants. Most interviewees said they gave their hives artificial food (a mixture of water and sugar) to strengthen them when they looked weak, but less than 30% said they took preventive measures against ants, cleaning out the spiders’ nets or others. Regarding the artificial division of the colonies, 62% of the interviewees reported that they practiced this normally once a year, and most of them were successful.

Meliponiculturist who succeeded in artificial division of hives had taken a significantly higher number of training courses compared with those who did not perform artificial divisions (p = 0.0423). Similarly, those meliponiculturists who gave supplementary food to the hives, had taken a significantly higher number of training courses compared with those who did not perform this practice (p = 0.0095). On the other hand, there was no significant difference between the number training courses taken and the success or failure on racking (p = 0.723) or in the presence or absence of practices to fight pests (p = 0.340) (Table 4).

Table 4 Results for the generalized linear models for the influence of the number of training courses on the use and success of management techniques

Stingless bees’ products, productivity, and commercialization

When questioned about the harvesting of the honey, 17% of interviewees said they did not harvest their hives, at least not yet, and the rest said they usually did it once a year. Honey production of the colonies of Señorita varied between 0.5 and 1 L per colony per year, and rarely more than 2 L. In contrast, the colonies of Tancarillo and Negro produced a larger volume of honey, yielding between 1 and 4 L per colony; however, these species are rarely bred. Besides honey, most interviewees also harvested pollen, propolis, and cerumen in lesser amounts. This activity was mostly done in the company of a son or a daughter.

In the communities, honey, pollen, propolis, and cerumen are used but in very different proportions. Honey was the most used product from the hive. Over 90% of the meliponiculturists harvested honey from their hives, most of them at least once a year, in some cases two (26%) or even three (6%) times a year. It is valued for its medical uses, specially to treat eye diseases and common cold, as well as food and as a source of income since it is a very valued product in the market. Despite this fact, just 38% of the meliponiculturists produced enough honey to sell it, approximately half was sold to the public, and the other half was sold in bulk to local NGOs at a price of around USD 21 per liter. This price is four to five times higher than honey sold in bulk from A. mellifera which can be sold for USD 4 to 5 [50]. The rest consumed the honey themselves as food or as medicine. As mentioned previously, Señorita is the most managed bee in this area, although it normally produces between 500 mL and 1 L, whereas Negro or Tancarillo produce on average 4 L and 2.3 L, respectively. The second most harvested product was pollen, locally called “pan de abeja,” being harvested by 35 women (59%). Pollen is mostly used as food, but some women also have medicinal use for it as energizer or nutritional supplement mostly for kids with anemia. Pollen is eaten pure, mixed with banana or with honey. It is rarely sold to the public, generally with a price of USD 15 per kg. Propolis was harvested by 42% of the interviewed women, and they used it equally as medicine or for sale. It was sold principally to the public with a very wide range of price oscillating between USD 3 and 12 per 100 mL. Cerumen was collected only by 31% of women. It was mostly purified and used to strengthen other hives. Three interviewees said they used the cerumen as food; one said she used it as medicine, and just one sold it at USD 22 per kg. Finally, the brood cells were the least harvested and used product of the hive. Just two interviewees (3%) mentioned this medicinal/traditional use; by eating the brood cells, it is believed that it enhances fertility.

The use of honey and its medicinal properties

There is a consensus among the interviewees that the honey produced by Señorita is the most beneficial and the one with more medicinal properties, being used for treating several diseases. According to the frequency of citations, the main therapeutic use was for respiratory system treatments. Treatment of eye problems was cited almost as frequently (18 times), but in this case, honey was not consumed/eaten; instead, a drop or two are released directly on the affected eye. Ten interviewees also mentioned that consuming honey helped with digestive problems, and 9 said it strengthened the body and the immune system. In just a few cases (2), it was mentioned that honey could cure skin damages.

Regarding the uses of the honey produced by the other bees, in three different occasions it was informed that the honey produced by Burro and Burra was used to increase fertility, and two women mentioned that the honey produced by Negro was also helpful to treat digestive and respiratory problems.

The interviewees also shared some recipes and treatments they used to treat diseases (Table 5). Although some of the secondary ingredients varied, mostly there was a consensus on which ingredients to use for certain illnesses and how to prepare them.

Table 5 Recipes and treatments based on honey and other products of the hive

Relative cultural importance

The interviewees reported 30 different specific uses (#U) for the products of five stingless bee species: Señorita (T. angustula), Negro (Scaptotrigona sp.), Tancarillo (M. rufiventris), Sapito (Plebeia sp.), and Burro/Burra (Scaptotrigona sp.). These specific uses were grouped into 4 categories (#C): commercialization, food, medicine, and others (Additional file 1: Appendix 3). Based on the RCI index, T. angustula was the most culturally important bee in the region, followed by Scaptotrigona sp. (Table 6). There was a significative positive relationship between the percentage of people that managed a bee species and the relative cultural importance index (r = 0.875, p = 0.0044).

Table 6 RCI relative cultural importance index


Knowledge on bee diversity and the problematic of local names

Considering the number of species collected during this study, the number of local names mention in the interviews revealed an overall wide traditional knowledge among the meliponiculturists of the Chaco region. Twelve morphospecies of stingless bees were collected; however, 15 different local names were mentioned in the interviews, together with some characteristics of the species. It is possible that some species were not collected during this study since some bee species may not be effectively attracted to the pan traps or they are infrequent and difficult to collect with a net [54]. Also, it has been proved on several occasions that local knowledge can provide useful information about the ecological and natural history of stingless bees helping to better assess them and even recognize new species [52, 55, 56]. On the other hand, it is also possible that more than one name mentioned by the interviewees correspond to only one species since the people that were interviewed belong to different ethnic groups which may have different names for the bees. Reyes-González et al. [26] documented in Michoacan, Mexico, in three different geographical zones but within the same state, up to five different local names for the same species. In Bolivia, Lestrimelitta limao for example, is called Limoncillo among the Ayoreos due to its characteristic lemon-like smell, but is called Pichi de burro by the Guaranies because of its large nest entrance [16, 57]. In future works, it would be interesting to deepen this knowledge with more extensive workshops with meliponiculturists as well as knowledge holders, analyzing their classification according to linguistic, cognitive, and socio-ecological meanings [58].

Traditional knowledge

Most of the participants in the study did not consider themselves to belong to a specific ethnic group, resulting in an underrepresentation in the analysis carried out to identify an influence of ethnicity on traditional knowledge. Nevertheless, this reflects what is actually happening in most of the communities from Villa Vaca Guzmán, where most people did not feel identified with an ethnic group, probably because of common processes of globalization due to proximity to larger cities and the integration of rural populations to the market economy [59]. In this sense, and based on our results, it appears that traditional knowledge on bees is not significantly different between ethnic groups involved in meliponiculture. Although processes such as globalization potentially result in the loss of traditional knowledge [59], traditional and cultural knowledge is dynamic and in many cases these processes lead to changes and transformation rather than loss [60, 61]. These changes can mean that indeed some traditional knowledge is lost, but they may also lead to the uptake of new knowledge and, when many ethnic groups live together, also to the homogenization of knowledge [62].

The influence of formal education

The influence of the meliponiculture courses given by the NGOs have a significant impact in the current knowledge, management and perception of meliponiculturists. This has also been observed by Zocchi et al. [59] who showed how the influence of external actors can lead to a hybridization of the traditional knowledge and modern apiculture, refining local practices while increasing production. Similarly, Jaffe et al. [63] highlight how the influence of modern practices have a positive effect on the management of hives as well as of the forest.

Influence in the traditional knowledge

Contrary to what was expected, there was no significant difference between ages regarding the knowledge about stingless bees. This could be because of the initiatives from the local NGOs to promote meliponiculture. This initiative helps indirectly to homogenize the knowledge of younger and older people on one hand through workshops (in this case is mostly formal knowledge). On the other hand, these workshops may serve as platforms for the exchange of knowledge between the participants. As Jaffé et al. [63] identified in their study, beekeeper networks were fundamental to better developing the activity through knowledge exchange, recognizing that more experience meliponiculturists are a source of knowledge and promoters of meliponiculture.

Influence in management techniques

The workshops given by the NGOs also influence the management of the hives, since they give the beneficiaries knowledge of new technological and management techniques. Meliponiculturists who have attended many workshops (three or four) were more likely to use some of these techniques, such as supplementary feeding the hives or doing artificial divisions. This was also observed by Jaffé et al. [63] and by Escareño et al. [64], who highlight the importance of acquiring these management skills to make meliponiculture a sustainable practice and since, on the one hand, multiplying colonies through artificial divisions is not easy, while supplementary feeding is an essential part of bee management influencing colony growth, performance and survival. Also, Contreras et al. [31] affirm that new advances in management has “led to a new flourishing of meliponiculture.”

Although there was not a significant difference in the success or failure of the divisions regarding the number of workshops that women assisted, there was a greater success rate in comparison with communities that only used traditional methods to divide the hives. Pat-Fernandes et al. [65] documented a success rate of only 20% from the divisions made by the indigenous people from communities in Campeche, Mexico; similarly, Villanueva-Gutierrez et al. [29, 66] documented a success rate of only 17% in communities within the Zona Maya of Quintana Roo. These figures may be compared to the 47% success rate of the women in Muyupampa.

Influence in the perception and relative cultural importance

In this study, 30 different specific uses for the bee products were recorded, from which 29 were attributed (but not exclusively) to T. angustula, making it the most versatile species, and so the most culturally important species. Similarly, Kujawska et al. [67] reported that honey from five different bee species in Argentina were used to treat 30 affections, and honey was consumed pure or prepared with other plant ingredients. Also in Argentina, Geisa and Hilgert [68] identified 17 medical uses for the honey of Plebeia molesta. Other studies documented fewer specific uses for the honey and other products; for example, Gonzalez et al. [52] reported nine specific uses for Scaptotrigona hellwegeri in Mexico, and Bhatta et al. [53] who reported 18 specific uses for Tetragonula iridipennis in Nepal. Consistently the most treated affection with stingless bee honey were respiratory problems.

The meliponiculture workshops focus mostly on one species, T. angustula, and this incentive to work mainly with this one species can also bias the perception of the meliponiculturists and shift the cultural importance to this species. For example, when asked about the most abundant bees, most agree that the most abundant was Señorita, followed by other commonly bred species. However, the most collected species was Plebeia sp, which was only mentioned by 2% of the interviewees as an abundant species. Since the women are more interested in the species they manage, they probably pay more attention to these bees, or search specifically for them when walking through the forest, so they perceive that they are more abundant. Additionally, Sapito had a relatively high mention index (21.7%), and, for the relative cultural importance index (28.33), it is the third most versatile species. According to Gonzalez et al. [52], more abundant species are more versatile since people have more opportunities to work with them, and to experiment and attribute uses to them. Probably Sapito was formerly often managed, explaining it’s relatively high mention index and RCI index, but with the incentives of the NGOs, Señoritas have become the most managed species, and the traditional knowledge of breeding other species can fade off. This is why although the influence of formal knowledge have great advantages, it is important to emphasize that these initiatives have to take into account the local biodiversity to strengthen the breeding and conservation of more than one species. It is also necessary that they have an understanding of the local traditional knowledge to find endogenous elements that can be mixed with modern techniques.

Stingless bee products, productivity, and commercialization

A proper management is also necessary to maintain a healthy environment for the bees, avoiding unnecessary deforestation [63]. In turn, the conservation of bee habitats is of utmost importance to assure a good productivity in the meliponaries. If the availability of adequate food sources decreases, creating an imbalance between the number of bees and their food resources and thus surpassing the carrying capacity of the forest, the bee colonies would produce less honey, and it would have probably lower quality [69, 70]. According to our results, the mean production of Señorita is around 500 ml to 1 L, and in some cases even up to 2 L per colony per year. This is the best productivity expected for this bee species [71, 72], and one of the key factors to achieve this is the quality and quantity of the food source that the bees have access to [69]. The production of honey is not only used for self-consuming, but it is also sold and has become an alternative for economic incomes. In the cities, the honey of Señorita is sold mostly as medicine and therefore in small containers of 20 or 30 mL, and it is sold for USD 2–3. This price is similar in other parts of Latin America; for example, in Costa Rica 10-mL containers cost USD 2–4 and 1-L containers up to USD 50 [72], and in Brazil 1 kg of T. angustula honey costs USD 20–30 [73]. The other products of the hive are mostly used for self-consumption.


Our results showed a high diversity of native bees in the region that are recognized by the communities and represent an important income for the economy of meliponiculturists, especially women, as well as their families and communities. Participation in training that foster the use of modern meliponiculture methods shows better results with hive management and production. It is crucial that these initiatives have a broader perspective, not just focused on one species so that the communities will value cultural richness and biodiversity. On the other hand, it is important that small producers also develop formal competences for the commercialization and elaboration of derived products to promote sustainable development in the region.

Availability of data and materials

The data that support the findings of this study are available from the corresponding author upon request.


  1. Kluser S, Peduzzi P. Global pollinator decline: a literature review. Nairobi: UNEP; 2007.

    Google Scholar 

  2. Potts SG, Imperatriz-Fonseca V, Ngo HT, Aizen MA, Biesmeijer JC, Breeze TD, Dicks LV, Garibaldi LA, Hill R, Settele J, Vanbergen AJ. Safeguarding pollinators and their values to human well-being. Nature. 2016.

    Article  Google Scholar 

  3. IPBES. The assessment report of the intergovernmental science-policy platform on biodiversity and ecosystem Services on pollinators, pollination and food production. In: Potts SG, Imperatriz-Fonseca V, Ngo HT, editors. Secretariat of the intergovernmental science-policy platform on biodiversity and ecosystem services. 2016.

  4. Hrncir M, Maia-Silva C. On the diversity of foraging-related traits in stingless bees. In: Vit P, Pedro SR, Roubik D, editors. Pot-honey: a legacy of stingless bees. Springer: New York; 2013. p. 201–15.

    Chapter  Google Scholar 

  5. Rasmussen C, Cameron SA. Global stingless bee phylogeny supports ancient divergence, vicariance, and long distance dispersal. Biol J Lin Soc. 2010;99(1):206–32.

    Article  Google Scholar 

  6. Michener CD. The meliponini. In: Vit P, Pedro SR, Roubik D, editors. Pot-honey: a legacy of stingless bees. Springer: New York; 2013. p. 3–17.

    Chapter  Google Scholar 

  7. Camargo JMF. Historical biogeography of the meliponini (hymenoptera, apidae, apinae) of the neotropical region. In: Vit P, Pedro SR, Roubik D, editors. Pot-honey: a legacy of stingless bees. New York: Springer New York; 2013. p. 19–34.

    Chapter  Google Scholar 

  8. Michener CD. The bees of the world. 2nd ed. Baltimore: The Johns Hopking University Press; 2007.

    Book  Google Scholar 

  9. Grüter C. Stingless Bees their Behaviour, Ecology and Evolution. Berlin: Springer Nature; 2020.

    Book  Google Scholar 

  10. Slaa EJ, Sánchez Chaves LA, Malagodi-Braga KS, Hofstede FE. Stingless bees in applied pollination: practice and perspectives. Apidologie. 2006.

    Article  Google Scholar 

  11. Giannini TC, Cordeiro GD, Freitas BM, Saraiva AM, Imperatriz-Fonseca VL. The dependence of crops for pollinators and the economic value of pollination in Brazil. J Econ Entomol. 2015.

    Article  Google Scholar 

  12. Potts SG, Biesmeijer JC, Kremen C, Neumann P, Schweiger O, Kunin WE. Global pollinator declines: trends, impacts and drivers. Trends Ecol Evol. 2010.

    Article  Google Scholar 

  13. Giannini TC, Maia-Silva C, Acosta AL, Jaffé R, Carvalho AT, Martins CF, Zanella FCV, Carvalho CAL, Hrncir M, Saraiva AM, Siqueira JO, Imperatriz-Fonseca VL. Protecting a managed bee pollinator against climate change: strategies for an area with extreme climatic conditions and socioeconomic vulnerability. Apidologie. 2017.

    Article  Google Scholar 

  14. Toledo-Hernández E, Peña-Chora G, Hernández-Velázquez VM, Lormendez CC, Toribio-Jiménez J, Romero-Ramírez Y, León-Rodríguez R. The stingless bees (Hymenoptera: Apidae: Meliponini): a review of the current threats to their survival. Apidologie. 2022.

    Article  Google Scholar 

  15. Lima MA, Cutler GC, Mazzeo G, Hrncir M. Editorial–the decline of wild bees: causes and consequences. Front Ecol Evol. 2022.

    Article  Google Scholar 

  16. Szabo HE, Sterlin E. El Conocimiento sobre las abejas nativas entre los Ayoreos de la TCO Guaye. 1st edn. PNUD, FCBC, AGUARAGUE. 2005.

  17. Dos Santos GM, Antonini Y. The traditional knowledge on stingless bees (Apidae: Meliponina) used by the Enawene-Nawe tribe in western Brazil. J Ethnobiol Ethnomed. 2008.

    Article  Google Scholar 

  18. Souza BA, Lopes MTR, Pereira FM. Cultural aspects of meliponiculture. In: P. Vit, D. Roubik, editors, Stingless bees process honey and pollen in cerumen pots. 2013

  19. Reyes-González A, Camou-Guerrero A, Reyes-Salas O, Argueta A, Casas A. Diversity, local knowledge and use of stingless bees (Apidae: Meliponini) in the municipality of Nocupétaro, Michoacan, Mexico. J Ethnobiol Ethnomed. 2014.

    Article  Google Scholar 

  20. Cortopassi-Laurino M, Imperatriz-Fonseca VL, Roubik DW, Dollin A, Heard T, Aguilar I, Venturieri GC, Eardley C, Noguera-Neto P. Global meliponiculture: challenges and opportunities. In: Apidologie. 2006; doi:

  21. Ayala R, Gonzalez VH, Engel MS. Mexican stingless bees (hymenoptera: Apidae): diversity, distribution, and indigenous knowledge. In: Vit P, Pedro SR, Roubik D, editors. Pot-honey: a legacy of stingless bees. New York: Springer New York; 2013. p. 135–52.

    Chapter  Google Scholar 

  22. Chuttong B, Chanbang Y, Burgett M. Meliponiculture: stingless bee beekeeping in Thailand. Bee World. 2014.

    Article  Google Scholar 

  23. Vit P, Roubik DW, Pedro SRM. Pot-honey: a legacy of stingless bees. In: Pot-honey: a legacy of stingless Bees. Springer New York, New York. 2013.

  24. Zamudio F, Hilgert NI. Cultural, psychological, and organoleptic factors related to the use of stingless bees by rural residents of northern Misiones, Argentina. In: Vit P, Pedro SR, Roubik DW, editors. Pot-Pollen in stingless bee melittology. Springer International Publishing; 2018. p. 283–97.

    Chapter  Google Scholar 

  25. Baquero L, Stamatti G. Cría y manejo de abejas sin aguijón. 1st Edn. Fundación ProYungas, Ediciones del Subtrópico; 2007.

  26. Reyes-González A, Camou-Guerrero A, Ek D-V, Ramírez MI, Porter-Bolland L. Biocultural diversity loss: the decline of native stingless bees (Apidae: Meliponini) and local ecological knowledge in Michoacán, Western México. Hum Ecol. 2020.

    Article  Google Scholar 

  27. Stearman AML, Stierlin E, Sigman ME, Roubik DW, Dorrien D. Stradivarius in the jungle: traditional knowledge and the use of “black beeswax” among the Yuquí of the Bolivian Amazon. Hum Ecol. 2007.

    Article  Google Scholar 

  28. Lehm Z, Townsend W, Salas H, Lara K. Bolivia: estrategias, problemas y desafios en la gestiondel territorio indigena siriono. Copenhague: IWGIA; 2004.

    Google Scholar 

  29. Villanueva-G R, Roubick DW, Colli-Ucán W. Extinction of Melipona beecheiiand traditional beekeeping in the Yucatán peninsula. Bee World. 2005;86(2):35–41.

    Article  Google Scholar 

  30. Arnold N, Zepeda R, Dávila MV, Maya MA. Las abejas sin aguijón y su cultivo en Oaxaca, México con catálogo de especies; 2018.

  31. Contrera FAL, Menezes C, Venturieri GC. New horizons on stingless beekeeping (Apidae, Meliponini). Rev Bras Zootecnia. 2011;40:48–51.

    Google Scholar 

  32. Barbiéri C, Francoy TM. Theoretical model for interdisciplinary analysis of human activities: meliponiculture as an activity that promotes sustainability. Ambiente Soc. 2020.

    Article  Google Scholar 

  33. Municipio villa vaca Guzmán. Plan de desarrollo municipal. Sucre: Diagnóstico Municipal Consolidado; 2000.

    Google Scholar 

  34. Delgado FA, Martínez GE. Guía práctica: manejo de abejas nativas sin aguijón. Bolivia: Fundación Pasos Chuquisaca-Bolivia; 2021.

    Google Scholar 

  35. Instituto Nacional de Estadística. Departamento de Chuquisaca; Estadísticas e Indicadores Sociodemográficos. La Paz: Productivos y Financieros por Municipio; 2005.

    Google Scholar 

  36. Navarro G, Ferreira W. Clasificación y Caracterización de la Vegetación del Departamento de Chuquisaca. In: Carretero A, Serrano M, Brochsenius F, Balslev H, editors. Pueblos y Plantas de Chuquisaca. Herbario del Sur de Bolivia-Universidad Mayor, Real y Pontificia de San Francisco Xavier de Chuquisaca, Sucre. 2011a. pp. 25-53

  37. Navarro G, Ferreira W. Bioclima del Departamento de Chuquisaca. In: Carretero A, Serrano M, Brochsenius F, Balslev H, editors. Pueblos y Plantas de Chuquisaca. Herbario del Sur de Bolivia-Universidad Mayor (pp. 15–21). Real y Pontificia de San Francisco Xavier de Chuquisaca, Sucre. 2011a.

  38. SERNAP. Resumen Plan de Manejo del Parque Nacional y Área Natural de Manejo Integrado Serranía del Iñao. 2013.

  39. Shapiro LH, Tepedino VJ, Minckley RL. Bowling for bees: optimal sample number for “bee bowl” sampling transects. J Insect Conserv. 2014.

    Article  Google Scholar 

  40. LeBuhn G, Droege S, Connor E, Gemmill-Herren B, Azzu N, Food and Agriculture Organization of the United Nations. Protocol to detect and monitor pollinator communities: guidance for practitioners. Food and Agricultural Organization of the United Nations (FAO). 2016.

  41. Camargo JMF, Moure JS. Meliponinae neotropicales: os generos Paratrigona Schwarz, 1938 e Aparatrigona Moure, 1951 (Hymenoptera, Apidae). Arq Zool. 1994;32:33–109.

    Article  Google Scholar 

  42. Melo GAR, Costa MA. A new stingless bee species of the genus Scaura (Hymenoptera, Apidae) from the Brazilian Atlantic forest, with notes on S. latitarsis (Friese). Zootaxa. 2004.

    Article  Google Scholar 

  43. Oliveira FF, Marchi P. Três espécies novas de Lestrimelitta Friese (Hymenoptera, Apidae) da Costa Rica, Panamá e Guiana Francesa. Rev Bras Entomol. 2005.

    Article  Google Scholar 

  44. Gonzalez VH, Griswold TL. Two new species of Paratrigona and the male of Paratrigona ornaticeps (Hymenoptera, Apidae). ZooKeys. 2011.

    Article  Google Scholar 

  45. Alvarez LJ, Rasmussen C, Abrahamovich AH. Nueva especie de Plebeia Schwarz, clave para las especies argentinas de Plebeia y comentarios sobre Plectoplebeia en la Argentina (Hymenoptera: Meliponini). Rev Del Museo Argent Cienc Nat. 2016.

    Article  Google Scholar 

  46. Rasmussen C, Gonzalez VH. The neotropical stingless bee genus Nannotrigona Cockerell (Hymenoptera: Apidae: Meliponini): an illustrated key, notes on the types, and designation of lectotypes. Zootaxa. 2017.

    Article  Google Scholar 

  47. International Society of Ethnobiology. ISE code of ethics (with 2008 additions) 2006. Online:

  48. Chao A, Gotelli NJ, Hsieh TC, Sander EL, Ma KH, Colwell RK, Ellison AM. Rarefaction and extrapolation with Hill numbers: a framework for sampling and estimation in species diversity studies. Ecol Monogr. 2014.

    Article  Google Scholar 

  49. Chao A, Ma KH, Hsieh TC. User’s guide for iNEXT online: software for interpolation and extrapolation of species diversity. Inst Stat. 2016.

    Article  Google Scholar 

  50. Hsieh TC, Ma KH, Chao A. iNEXT: an R package for rarefaction and extrapolation of species diversity (H ill numbers). Methods Ecol Evol. 2016.

    Article  Google Scholar 

  51. Bennett BC, Prance GT. Introduced plants in the indigenous pharmacopoeia of Northern South America. Econ Bot. 2000.

    Article  Google Scholar 

  52. Gonzalez VH, Amith JD, Stein TJ. Nesting ecology and the cultural importance of stingless bees to speakers of Yoloxóchitl Mixtec, an endangered language in Guerrero, Mexico. Apidologie. 2018.

    Article  Google Scholar 

  53. Bhatta C, Gonzalez VH, Smith D. Traditional uses and relative cultural importance of Tetragonula iridipennis (Smith) (Hymenoptera: Apidae: Meliponini) in Nepal. J Melittol. 2020.

    Article  Google Scholar 

  54. Hudson J, Horn S, Hanula JL. Assessing the efficiency of pan traps for collecting bees (Hymenoptera: Apoidea). J Entomol Sci. 2020.

    Article  Google Scholar 

  55. Portugal-Araújo V, Kerr WE. A case of sibling species among social bees. Rev Bras Biol. 1959;19(3):223–8.

    Google Scholar 

  56. Townsend W, Adler M, Martinez MT, Cuellar W, Rodríguez F, Cuellar P, Toledo M. Explorando la relación de las abejas sin aguijón y plantas en los TCOs Sirionó y Lomerío Guía ilustrada (1st. edN.). Museo de Historia Natural Noel Kempff Mercado. 2021.

  57. CABI-Capitanía del alto y bajo Isoso, WCS Bolivia, CIMCI-Central Intercomunal de Mujeres Isoceñas. Manejo Abejas Nativas en el Isoso (Chaco Boliviano). Industrias gráficas SIRENA; 2003.

  58. Zamudio F, Hilgert NI. Multi-dimensionality and variability in folk classification of stingless bees (Apidae: Meliponini). J Ethnobiol Ethnomed. 2015.

    Article  Google Scholar 

  59. Turner NJ, Turner K. “Where our women used to get the food”: cumulative effects and loss of ethnobotanical knowledge and practice; case study from Coastal British Columbia. Botany. 2008;86:103–15.

    Article  Google Scholar 

  60. Zocchi DM, Volpato G, Chalo D, Mutiso P, Fontefrancesco MF. Expanding the reach: ethnobotanical Knowledge and technological intensification in beekeeping among the Ogiek of the Mau Forest, Kenya. J Ethnobiol Ethnomed. 2020;16(1):57.

    Article  Google Scholar 

  61. de Carvalho RM, Martins CF, Mourao JD. Meliponiculture in Quilombola communities of Ipiranga and Gurugi, Paraíba state, Brazil: an ethnoecological approach. J Ethnobiol Ethnomed. 2014;10(1):1–2.

    Article  Google Scholar 

  62. Berkes F, Colding J, Folke C. Rediscovery of traditional knowledge as adaptive management. Ecol Appl. 2000;10:1251–62.

    Article  Google Scholar 

  63. Jaffé R, Pope N, Carvalho AT, Maia UM, Blochtein B, de Carvalho CAL, et al. Bees for development: brazilian survey reveals how to optimize stingless beekeeping. PLoS ONE. 2015.

    Article  Google Scholar 

  64. Escareño FC, Echazarreta CM, Gusmán-Nóvoa E, Macías-Macías JO. Traditional knowledge and potential use of stingless bees (Hymenoptera: Meliponinae) in the Manantlan Sierra, Jalisco, Mexico. Sociobiology. 2019;66(1):120–5.

    Article  Google Scholar 

  65. Pat Fernández LA, Franceschi FA, Fernández JMP, Reyes RR. Condition and perspectives of meliponiculture in Mayan communities at Los Petenes biosphere reserve in Campeche, Mexico. Estudios Cult Maya. 2018.

    Article  Google Scholar 

  66. Villanueva-Gutiérrez R, Roubik DW, Colli-Ucán W, Güemez-Ricalde FJ, Buchmann SL. A critical view of colony losses in managed Mayan honey-making bees (Apidae: Meliponini) in the heart of Zona Maya. J Kansas Entomol Soc. 2013.

    Article  Google Scholar 

  67. Kujawska M, Zamudio F, Hilgert NI. Honey-based mixtures used in home medicine by nonindigenous population of Misiones, Argentina. Evid-Based Complement Altern Med. 2012.

    Article  Google Scholar 

  68. Geisa MG, Hilgert NI. The honey of Plebeia molesta and other melliferous insects in the peasant culture of the Northwest of Cordoba, Argentina. Ethnobiol Conserv. 2019.

    Article  Google Scholar 

  69. Al-Ghamdi A, Adgaba N, Getachew A, Tadesse Y. New approach for determination of an optimum honeybee colony’s carrying capacity based on productivity and nectar secretion potential of bee forage species. Saudi J Biol Sci. 2014.

    Article  Google Scholar 

  70. Wan Mohamad WSN, Hassan K, Awang A, Mohd Nasir MR, Ramle H, Ramlee N, Pulli H. The Relationship between Stingless Bee and Native Plants Studies. Serangga. 2022.

  71. Gennari GP. Manejo racional de las abejas nativas sin aguijón (ANSA). Geneva: Ediciones INTA; 2019.

    Google Scholar 

  72. Aguilar I, Herrera E, Zamora G. Stingless bees of Costa Rica. In: Vit P, Pedro SR, Roubik D, editors. Pot-Honey: A Legacy of Stingless Bees. Springer: New York; 2013. p. 113–24.

    Chapter  Google Scholar 

  73. De Oliveira Alves RM. Production and marketing of pot-honey. In: Vit P, Pedro SR, Roubik D, editors. Pot-honey: a legacy of stingless bees. Springer: New York; 2013. p. 541–56.

    Chapter  Google Scholar 

Download references


The authors would like to acknowledge all informants who shared their knowledge and Fundación PASOS for their logistical support, as well as Noelia Janko, who generate the map of the study area and assisted in the field and Gina Zambrana Camacho, who also assisted in the field.


The study had financial support from the International Science Programme at Uppsala University (ISP grant BOL-01), the Center for International Health of the University Hospital Munich (LMU), and the OH-TARGET project supported by the German Academic Exchange Service (DAAD) with funds from the Federal Ministry for Economic Cooperation and Development (BMZ)–Germany.

Author information

Authors and Affiliations



All authors contributed to the study conception and design. MA, LEM and CFP performed bees sampling, material preparation, data collection, and analysis. MA wrote the first draft of the manuscript, and all authors commented on and edited different versions of the manuscript. All authors read and approved the final manuscript.

Corresponding author

Correspondence to Carlos F. Pinto.

Ethics declarations

Ethics approval and consent to participate

Following the respective institutional ethics protocols, full free informed consent was obtained from all participants in the study, before interviews were conducted. The research and resulting publication were approved by all participants.

Consent for publication

The signed form was attached in the submission system.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Supplementary Information

Additional file 1. Appendix 1

. Results for the Generalized Linear Model for the influence of age and ethnicity on the number of species known be the local meliponiculturists. Appendix 2. Influence of age and ethnicity on the knowledge of stingless bees' species. Appendix 3. Categories of uses (#C), and specific uses (#U) of all the reported bee species (Common names) in the region of Monteagudo. Abbreviations: H = honey; Po = pollen; Pr= propolis; Ce= Cerumen.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit The Creative Commons Public Domain Dedication waiver ( applies to the data made available in this article, unless otherwise stated in a credit line to the data.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Adler, M., Escóbar-Márquez, L., Solis-Soto, M.T. et al. Stingless bees: uses and management by meliponiculturist women in the Chaco region of Bolivia. J Ethnobiology Ethnomedicine 19, 5 (2023).

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI:


  • Ethnobiology
  • Meliponini
  • Traditional knowledge
  • Medicinal honey
  • Conservation
  • Relative cultural importance