SciELO - Scientific Electronic Library Online

 
vol.97 número3El legado climático histórico y contemporáneo de los patrones de distribución a gran escala de la riqueza vegetal en diferentes niveles taxonómicos: una evaluación de las áreas protegidas en ChinaAmarisólida A y pedalitina como compuestos bioactivos en el efecto antinociceptivo de Salvia circinata (Lamiaceae) índice de autoresíndice de assuntospesquisa de artigos
Home Pagelista alfabética de periódicos  

Serviços Personalizados

Journal

Artigo

Indicadores

Links relacionados

  • Não possue artigos similaresSimilares em SciELO

Compartilhar


Botanical Sciences

versão On-line ISSN 2007-4476versão impressa ISSN 2007-4298

Bot. sci vol.97 no.3 México Jul./Set. 2019

http://dx.doi.org/10.17129/botsci.2122 

Ethnobotany

Traditional medicinal knowledge of tropical trees and its value for restoration of tropical forests

Conocimiento tradicional medicinal de árboles tropicales y su valor para la restauración de bosques tropicales

Juana García-Flores1  2  * 

Mario González-Espinosa1 

Roberto Lindig-Cisneros2 

Alejandro Casas2 

1 Departamento de Conservación de la Biodiversidad, El Colegio de la Frontera Sur (ECOSUR), San Cristóbal de las Casas, Chiapas, México.

2 Instituto de Investigaciones en Ecosistemas y Sustentabilidad (IIES) - Universidad Nacional Autónoma de México (UNAM), Morelia, Michoacán, México.

Abstract:

Background:

Traditional medicinal knowledge (TMK) accounts for attending nearly 80 % of the worldwide needs of health and may guide biodiversity restoration efforts in tropical regions where the greatest diversity of medicinal plants occurs.

Questions:

Can TMK become a strategy to be used in identifying medicinal tree species, with both cultural and ecological importance, that should be considered in tropical forest restoration actions?

Study site and dates:

The study was conducted during 2015 in four communities of the Sierra region of southern Tabasco, Mexico.

Methods:

We obtained from the literature a checklist of medicinal trees native to the study region. We conducted semi-structured interviews and a workshop in each community; we obtained ethnobotanical data about the most common illnesses and the most frequently used plant species for attending them. We identified priority species for forest restoration, and calculated indexes of knowledge richness (IKR) and cultural significance (ICS).

Results:

We recorded a total of 45 tree species. Adult and elder women showed the highest TMK. The main illnesses detected were gastrointestinal (93-97 %) and those related with pain and fever (67-97 %), which were treated with 13 and 16 species, respectively. On average, the IKR was less than 50 % of all species recorded. Gliricidia sepium, Bursera simaruba and Piper auritum had high ICS values, while Brosimum alicastrum, Ceiba pentandra and Castilla elastica had low values and are considered high priority for forest restoration actions.

Conclusions:

TMK is important to select tree species in tropical forest restoration actions in southeastern Mexico.

Key words: ethnobotany; forest restoration; medicinal trees; traditional medicinal knowledge; tropical forests

Resumen:

Antecedentes:

El conocimiento tradicional medicinal (CTM) permite atender necesidades de salud de 80 % de la población mundial y puede servir como guía para recuperar biodiversidad en regiones tropicales, ya que la mayor diversidad de plantas medicinales incluye especies tropicales.

Pregunta:

¿Provee el CTM una estrategia para identificar especies arbóreas que por su importancia cultural y ecológica conviene emplear en proyectos de restauración de bosques tropicales?

Sitio y fechas:

El estudio se realizó en 2015, en cuatro comunidades rurales de la región Sierra de Tabasco, México.

Métodos:

Con base en revisión bibliográfica se obtuvo un listado de referencia sobre árboles medicinales nativos de la región. Efectuamos entrevistas semiestructuradas y un taller participativo en cada comunidad; se documentaron usos medicinales, enfermedades recurrentes, listados libres de especies medicinales y aquellas con prioridad para emplearse en acciones de restauración. Calculamos índices de riqueza de conocimiento (IRC) y de significancia cultural (ICS).

Resultados:

Registramos 45 especies arbóreas medicinales nativas. Las mujeres adultas y ancianas mostraron el mayor CTM. Las principales enfermedades fueron gastrointestinales (93-97 %) y las asociadas a dolores y fiebre (67-97 %), tratadas con 13 y 16 especies, respectivamente. El IRC reflejó un conocimiento promedio menor a 50 %. Gliricidia sepium, Bursera simaruba y Piper auritum tuvieron valores altos de ICS, mientras que Brosimum alicastrum, Ceiba pentandra y Castilla elastica mostraron valores bajos y son consideradas con alta prioridad para la restauración forestal.

Conclusiones:

El CTM es importante para seleccionar especies arbóreas en la restauración de los bosques tropicales del sureste de México.

Palabras clave: árboles medicinales; bosques tropicales; conocimiento tradicional medicinal; etnobotánica; restauración forestal

Traditional ecological knowledge (TEK) is a cumulative body of knowledge, practices and beliefs about the relationship of living beings with their environment, which evolve through adaptive processes and is culturally communicated across generations (Berkes 1993). TEK is crucial for carrying out local actions for conservation, ecological restoration and recovering biological populations, particularly those of useful species (Levy-Tacher et al. 2012, Casas et al. 2014, 2016, Chekole 2017). TEK provides decision makers with valuable information about distribution, abundance, biotic interactions, behavior, recovering capacity of organisms and ecosystems following disturbance, among other issues. In addition, TEK has proved its usefulness in identifying valuable ecosystems and resources to be protected and recovered, as well as management experiences to shorten the ways for attaining sustainable management strategies (Casas et al. 2014, 2016). Some ecological restoration efforts have started from documenting the most valuable resources, among them edible, fuel, and timber producing plants (Vázquez-Yanes et al. 1999, Lindig-Cisneros 2017). Yet few studies have been conducted considering medicinal plants (Charnley et al. 2008, Suárez et al. 2012, Velázquez-Rosas et al. 2018), notwithstanding that this group of plants commonly is the largest in ethnobotanical inventories (Toledo et al. 1995).

Traditional medicinal knowledge (TMK) is a crucial component of TEK. Both TMK and TEK study botanical, zoological, ecological, and technological knowledge combining empirical, rational, logical knowledge and symbolic, mythological and magical thinking that distinguishes the human being as a social and cultural being (Fagetti 2011). TMK focuses on elements associated to treat illnesses (Fagetti 2011), while TEK analyses more general aspects of biological species and their environment and ecosystems (Berkes 1993, Casas et al. 2016). TMK and TEK are locally generated and transmitted from generation to generation through oral, practical or written means (Foster 1953, Pochettino & Lema 2008); however, TMK has played a crucial role in survival and has helped humanity to face threats to its physical, emotional and spiritual integrity; it is widely used for attending health problems, both for preventing and treating illnesses of many populations (WHO 2013). The use of TMK occurs predominantly in poor rural areas, commonly involving traditional physicians recognized within and among communities (Cabrera et al. 2015). Traditional medicine is practiced in almost all countries of the world (WHO 2013), covering nearly 80 % of the global needs of health (Akerele 1993, Fabricant & Farnsworth 2001, WHO 2002). Its use is key for people with poor access to official health services, and it is the main way of providing health help for indigenous communities (Hamilton 2004, Quinlan & Quinlan 2007, WHO 2013).

Despite the relevance of TEK and TMK, their loss is occurring worldwide (Anyinam 1995, Cox 2000, Lulekal et al. 2008, Brito et al. 2017). Among the multiple and complex factors influencing such process, authors like Linares & Bye (1987), Toledo (1987), Berkes & Turner (2005) have identified: (1) decreasing interest of young people to learn and transmit traditional knowledge (Phillips & Gentry 1993, Luoga et al. 2000, Voeks & Leony 2004, Reyes-García et al. 2013); (2) loss of the original languages in which that knowledge is transmitted (Benz et al. 2000, Maffi 2005); (3) modernization (Quinlan & Quinlan 2007) and new economic contexts (Reyes-García et al. 2005) favoring disarticulation of communities, migration, loss of culture and use of local medicinal flora (Vandebroek & Balick 2012, Alencar et al. 2014), and their replacement by modern patented medicines (Luziatelli et al. 2010, Reyes-García et al. 2013). The increasing loss of traditional knowledge may be expected to have consequences on the resilience of socio-ecological systems (Brito et al. 2017) since it tends to weaken the resources and ecosystems value and the need and relevance to maintain them (Toledo et al.1992, Voeks 1996, Weldegerima 2009, Silalahi et al. 2015, Brito et al. 2017).

Most of biodiversity on Earth occurs in tropical regions, particularly in those areas identified as “hotspots, which however are rapidly decreasing (Ryan 1992, Begossi et al. 2000, Myers et al. 2000). It has been recognized that in these areas live most of the indigenous peoples (Mace & Pagel 1995, Moore et al. 2002, Maffi 2005), and that they are the main custodians and stewards of ecosystems and biological diversity of “hotspots. In Mexico, tropical ecosystems are important reservoirs of the country’s biodiversity, harboring nearly 17 % of its flora (Rzedowski 1998, Challenger & Soberón 2008). However, extensive land-use change through deforestation aimed to establish pastures for livestock raising, traditional agriculture, and establishing plantations of commercial crops has reduced the extent and increased the isolation of the remaining fragments of original forest habitats (Challenger 1998, Koleff et al. 2012).

It has been estimated that only one-half of the original cover of tropical rain forest of Mexico remains relatively well preserved (Masera et al. 1992, Challenger & Soberón 2008, Koleff et al. 2012). In the state of Tabasco, where this study was conducted, the estimated original cover of tropical rain forest was 21.7 % of the State´s area, only 1.6 % of which remained at the beginning of this century (Sánchez-Munguía 2005). Ecological restoration implies the process of recovering ecosystems degraded, damaged or destroyed by natural and anthropogenic causes (SER 2004); it is based on a historical past with the aim of achieving short-term community benefits along with long-term social commitments to promote locally the ecological integrity, sustainability and long-term resilience of communities and ecosystems in the face of climate change (Suding 2011, DeFries et al. 2012, Suding et al. 2015). Programs aimed to forest cover restoration are urgent that may consider merging extant TEK and TMK in order to facilitate their local social construction, long-term adoption and foster wider use of biodiversity (González-Espinosa et al. 2008, Ramírez-Marcial et al. 2014, García-Barrios & González-Espinosa 2017).

The purpose of this study was to identify tree species that are used medicinally through traditional medicinal knowledge (TMK) which could be included in restoration practices aimed to increase forest cover. The study was conducted in four Zoque-Maya communities in the southern mountainous region of the state of Tabasco, in southeastern Mexico. We followed an ethnobotanical approach in documenting the use of native medicinal trees, the most important illnesses attended with them, and their cultural value for local people as important species in restoration actions. We also obtained the indexes of cultural significance of the species and knowledge wealth, and we identified the role of gender to discriminate whether it is men or women who possess this wealth of knowledge. Our study aims to illustrate the relevance of TMK for selecting tree species and designing strategies of ecological restoration of tropical forests.

Materials and methods

Study area. The study was conducted in the municipality of Tacotalpa (between 17° 20’ and 17° 42’ North; 92° 32’ and 92° 55’ West; elevation 20-1,000 m) in the Sierra region of the state of Tabasco (INEGI 2005), and in the eco-geographic unit of the abrupt northern slopes of the Sierra Norte of Chiapas (Ortiz-Pérez et al. 2005) in southeastern Mexico. The regional climate is warm-humid, with rains throughout the year, with annual rainfall of 1,500-4,500 mm (INEGI 2015). The area belongs to the Grijalva-Usumacinta hydrological region and the Grijalva-Villahermosa river basin, in which the Puxcatán, Almandros, Amatán, Chinal, and Tacotalpa rivers converge (INEGI 2005). The geology is characterized by Tertiary sedimentary rocks (shale-sandstones and limestones); dominant soils include shallow and rocky lithosols in the slopes and gleysols in lower areas, whose texture is generally clay, silt or silty clay, with problems of excess moisture due to poor drainage in low areas (INEGI 2005, Bensusán 2011).

Vegetation mostly includes secondary plant associations and small relicts of tropical rain forest (Miranda & Hernández-X 2014, Rzedowski 2006), mostly with a high degree of human disturbance (Ramírez-Marcial et al. 2014). In the less accessible areas, an average density of 32 stems per hectare belonging to at least four tree species has been reported for the pasture-dominated landscape (Grande-Cano et al. 2009). Salazar-Conde et al. (2004) report loss of tropical rain forest cover (with Brosimum alicastrum as dominant species) reaching up to 80 % within the last quarter of the past century.

We worked in four communities: Oxolotán (OX, 1,886 inhabitants, 10.4 % speak indigenous language); Cerro Blanco Quinta Sección (CB, 565 inhabitants, 7.1 % speak indigenous language); Tomás Garrido Canabal (TG, 389 inhabitants, 8.5 % speak indigenous language), and La Cumbre (LC, 238 inhabitants, 19.1 % speak indigenous language) (INEGI 2010). People of these communities belong to the Mayan ethnic groups Ch’ol, Chontal, and Tzotzil, yet a significant proportion belong to the Zoque and Mestizo groups. The degree of poverty is high in almost all communities except Oxolotán, where it has been estimated at an intermediate level (INEGI 2010) (Figure 1).

Figure 1 Study area and location of studied communities in the Sierra region of southern Tabasco, Mexico. 

Ethnobotanical studies. We obtained a preliminary checklist of medicinal trees occurring in the area through a literature review of floristic and ethnofloristic sources (Maldonado-Mares 2005, Magaña-Alejandro 2006, López-Hernández 1994, Ramírez-Marcial et al. 2014), which was used as a reference for other steps of the research. In addition, we identified whether or not those species receive any management, particularly if there were previous experiences of using them in restoration programs in the area or somewhere else.

Fieldwork started by asking permission from local authorities, as well as informing people and asking their consent for participating in the interviews. We then carried out semi-structured interviews (Albuquerque et al. 2014, Brito et al. 2017), during September and October 2015, to men and women of the four communities. We used the qualitative method called “snow ball” (Bernard 1995) for sampling interviewees recognized as experts in relation to the medicinal flora of the region.

In the OX community we conducted 28 interviews, 29 in CB, 26 in TG, and 24 in LC (See Appendix 1). We recorded name, gender and age of people interviewed, and questions were addressed to explore their ability to recognize medicinal flora using printed photographs of the species included in the reference checklist referred to above. In addition, we explored people’s identification of medicinal uses, illnesses treated with them, their form of administration, and their opinion on whether the tree species should be used in forest restoration activities in the region. This opinion was generally based on the low availability of the resource and the difficulty of natural regeneration of certain species. By means of the free listing technique we analyzed the most valuable species among medicinal trees.

We carried out a workshop in each community in October 2015 with the participation of the people interviewed: 18 people in CB, 16 in OX, 13 in LC, and 11 in TG. The workshops aimed at collectively selecting those medicinal tree species that could be considered with a high priority for forest restoration. We asked the people to name the 10 species of trees considered the most recommended to carry out actions of forest restoration (including their propagation and reintroduction to floristically enrich fallow stands); participants indicated the highest priority by number 1 and successively down until 10. We also asked them to comment about their criteria for their selection, which was commonly based on the low availability of the resource.

Data processing and analysis. We categorized the individually interviewed women and men from each community in different age groups. In addition, we categorized the most common illnesses and related affections, according to the information of the interviewees. We determined the most important illnesses in each community, the number of species used for treating the same illness, and the number of illnesses treated by each species. In each community we obtained the percentage of interviewees who considered each of the tree species with priority in restoration actions; we also obtained the percentage of the communities in which it was considered with some value of importance to a species.

We analyzed the amount of knowledge on use of medicinal trees through the Index of Knowledge Richness (IKR), following Toscano (2006), Castellanos-Camacho (2011)), and Medellín-Morales et al. (2017). We identified whether men or women possess this wealth of knowledge. For calculating this index we used the reference checklist and the free listing of medicinal trees reported by people interviewed in each community, using the formula:

IKR=Σ([SU]i/[SU]total).

In which, IKR is the proportion of species of medicinal trees reported by each interviewee in relation to the number of medicinal tree species reported by all people interviewed in the whole region; [SU]i is the number of species of medicinal trees recorded by the interviewee with respect to [SU]total, the total number of species of medicinal trees reported in the whole region by all the interviewees. Values of this index may vary from 0 to 1, being 1 the maximum value of richness value of the medicinal trees of the region.

For determining the species that are culturally most significant because of their use as medicines, we calculated the Index of Cultural Significance (ICS), based on parameters of quality (perceived effectiveness as medicines), intensity (use frequency), and exclusiveness (the plant as main or a non-substitutable component of a remedy) of the use of each species, based on Turner (1988) and Stoffle et al. (1990). For this study, we considered only the different medicinal uses reported by people. We adapted the ICS for this study as follows:

ICS=Σ(q×I×e)un/Ninf

The expanded formula being:

ICS=(q1×I1×e1)u1+(q2×I2×e2)u2+(q3×I3×e3)u3(qn×In×en)un/Ninf

The formula indicates the sum of 1 to n medicinal uses (u) for a species, where q = medicinal uses (use values from 5 to 0.5, according to categories of illnesses mentioned by the interviewees); I = intensity of use (values from 5 to 1, where 5 = very intense, 4 = intense, 3 = intermediate intense, 2 = low, 1 = very low); e = exclusivity of use (values from 2 to 0.5, where 2 = high, 1 = intermediate, and 0.5 = low); Ninf = total number of informants of people interviewed.

We finally analyzed the Cumulative Importance of Cultural Significance (CICS) of each species recorded in each community following the index of cultural importance by Stoffle et al. (1990). The CICS makes reference to the sum of ICS of each species of medicinal trees recorded in each community.

Results

Traditional medicinal knowledge of tropical tree species. The reference checklist included 21 species of medicinal trees, belonging to 21 genera and 14 plant families. Based on the free listing technique, we recorded 22 species and 2 morphospecies, belonging to 22 genera and 16 plant families. From the reference checklist and the free listing, in the OX community we summed a total of 34 species, belonging to 30 genera and 16 plant families; values for the other communities were: 31 species, belonging to 29 genera and 19 plant families in TG; 30 species belonging to 28 genera and 15 plant families in LC, and 28 species belonging to 26 genera and 15 plant families in CB. A total of 45 tree species with at least one medicinal use were recorded in the four studied communities (Table 1).

Table 1 Tropical medicinal tree species included in the reference list (*) and the free list (**) in the four study communities in southern Tabasco, Mexico. 

Community
Family Species Oxolotán Cerro Blanco Tomás Garrido La Cumbre
Anacardiaceae Spondias mombin L.** x
Spondias purpurea L.** x x
Annonaceae Annona reticulata L.* x x x x
Annona muricata L.** x x x x
Bignoniaceae Handroanthus guayacan (Seem.) S.O.Grose** x x
Parmentiera aculeata (Kunth) L.O.Williams** x x
Tabebuia rosea DC.* x x x x
Bixaceae Bixa orellana L.** x x
Burseraceae Bursera graveolens Triana & Planch.** x
Bursera simaruba (L.) Sarg.* x x x x
Caricaceae Carica mexicana (A.DC.) L.O.Williams** x
Clusiaceae Mammea americana L.** x
Cochlospermaceae Cochlospermum vitifolium Spreng.** x
Euphorbiaceae Croton draco Schltdl.** x x
Lamiaceae Cornutia pyramidata L.** x
Lauraceae Persea americana Mill.* x x x x
Leguminosae Acacia cornigera (L.) Willd.** x
Cassia grandis L.** x x x
Erythrina americana Mill.* x x x x
Gliricidia sepium (Jacq.) Kunth* x x x x
Haematoxylum campechianum L.** x
Inga jinicuil Schltdl.** x
Inga punctata Willd.** x
Senna sp.** x
Malpighiaceae Byrsonima crassifolia Kunth* x x x x
Malvaceae Ceiba pentandra (L.) Gaertn* x x x x
Guazuma ulmifolia Lam.* x x x x
Pachira aquatica Aubl.* x x x x
Pseudobombax ellipticum (Kunth) Dugand* x x x x
Theobroma cacao L.* x x x x
Meliaceae Cedrela odorata L.* x x x x
Trichilia havanensis Jacq. ** x x x
Moraceae Brosimum alicastrum Sw.* x x x x
Castilla elastica Sessé in Cerv.* x x x x
Ficus glaucescens Miq.** x
Myrtaceae Pimenta dioica (L.) Merr.* x x x x
Psidium guajava L.** x x x x
Piperaceae Piper auritum Kunth * x x x x
Rubiaceae Blepharidium mexicanum Standl.** x
Genipa americana L.* x x x x
Sickingia salvadorensis Standl.** x
Sapotaceae Manilkara zapota (L.) P. Royen* x x x x
Pouteria sapota (Jacq.) H. E. Moore & Stearn* x x x x
Pouteria sp.** x
Urticaceae Cecropia obtusifolia Bertol.* x x x x

We recorded 14 categories of recurrent illnesses that are treated with medicinal tree species within the study region (Table 2). The most common illnesses registered were gastrointestinal (93-97 %) which are attended with 13 species, and those associated to pain and fever (67-97 %), which are attended with 16 species (Tables 3 and 4). The species that were reported for treating the highest number of illnesses were Persea americana and Cecropia obtusifolia (8 categories of illnesses); Genipa americana was not reported to be used as medicine in the communities studied, although it is reported in other communities of the state of Tabasco (Table 4).

Table 2 Categories of recurrent illnesses treated with medicinal tree species in the region and their description. 

No. Category of illness Use values Illnesses and symptoms in the category
1 Gastrointestinal 5 vomiting, parasites, constipation, diarrhea, gastritis, colitis, stomach pain-infection, dysintery
2 Respiratory 5 cold, cough, flu, asthma, hoarseness
3 Dermatolological 5 wounds, ulcers, sores, burns, blows, fungus, dandruff (hair not cane), pimples
4 Pain and/or fever 4 fever, muscle pain, bone pain, headache, earache, toothache, nosebleeds
5 Women´s health issues 4 cramps, menstrual problems, infections, childbirth related issues
6 Urological 4 urinary infections, kidney pain, prostate problems
7 Ocular 3 infections, cataracts, conjunctivitis, red teary eyes
8 Cancer 3
9 Diabetes 3 blood sugar and glucose imbalances
10 Smallpox, chicken pox, measles 2
11 Blood related problems 2 anemia, leukemia, high cholesterol, high triglyceride levels, varicose veins, high or low blood pressure
12 Insect and animal bites 1
13 Ceremonies and spirit/sould related problems 1 ritual use, fright, protection, air, evil eye, smudging, crying in children, weakness
14 Others 0.5 nerves, insomnia, convulsions

Table 3 Percentage of recurrent illnesses treated with medicinal tree species in the four study communities. Number of interviews in each community are in parentheses. 

Communities
Oxolotán (28) Cerro Blanco (29) Tomás Garrido (26) La Cumbre (24)
Category of Illness % Category of Illness % Category of Illness % Category of Illness %
Gastrointestinal 93 Gastrointestinal 97 Pain and/or fever 92 Gastrointestinal 96
Pain and/or fever 89 Pain and/or fever 97 Smallpox, chicken pox, measles 77 Pain and/or fever 67
Dermatolological 75 Dermatolological 62 Gastrointestinal 73 Ceremonies and spirit/sould related problems 50
Diabetes 43 Ceremonies and spirit/sould related problems 62 Dermatolological 58 Smallpox, chicken pox, measles 38
Smallpox, chicken pox, measles 39 Smallpox, chicken pox, measles 59 Ceremonies and spirit/sould related problems 46 Women´s health issues 33
Blood related problems 36 Women´s health issues 31 Blood related problems 42 Diabetes 33
Respiratory 29 Diabetes 31 Urological 38 Dermatolological 29
Ceremonies and spirit/sould related problems 25 Ocular 28 Women´s health issues 35 Blood related problems 21
Ocular 25 Urological 17 Diabetes 27 Respiratory 17
Women´s health issues 21 Respiratory 14 Ocular 12 Ocular 4
Urological 14 Blood related problems 10 Insect and animal bites 4 Insect and animal bites 4
Cancer 0 Others 7 Others 4 Others 4
Insect and animal bites 0 Insect and animal bites 3 Respiratory 0 Urological 0
Others 0 Cancer 3 Cancer 0 Cancer 0

Table 4 Recurrent illnesses in the region and medicinal tree species that treat these illnesses in the four study communities of Tabasco, Mexico. 

Category of illness
Medicinal tree species Respiratory Gastrointestinal Dermatological Pain and/or fever Women´s health issues Urological Ocular Cancer Diabetes Smallpox, chicken pox, measles Blood related problems Insect and animal bites Ceremonies and spirit/sould related problems Others Total number of illnesses treated with the species
Persea americana X X x x x x x x 8
Cecropia obtusifolia x x x x x x x x 8
Annona reticulata X x x x x x x 7
Tabebuia rosea X X x x x x x 7
Gliricidia sepium X x x x x x 6
Guazuma ulmifolia X X x x x x 6
Cedrela odorata X X x x x x 6
Piper auritum X X x x x x 6
Manilkara zapota X x x x x x 6
Pouteria sapota X x x x x x 6
Bursera simaruba X x x x x 5
Theobroma cacao X x x x x 5
Pimenta dioica X X x x x 5
Erythrina americana x x x x 4
Byrsonima crassifolia X x x x 4
Pachira aquatica x x x x 4
Castilla elastica X x x 3
Ceiba pentandra x x 2
Brosimum alicastrum x 1
Genipa americana 0
Pseudobombax ellipticum 0
Total number of species that treat the category of illness 7 13 11 16 10 7 2 1 5 2 11 2 9 3

Knowledge Richness and Cultural Significance of the Species studied. Most interviews were carried out to women since the snow ball technique conducted to them, because of their expertise in using medicinal plants. Ages of women were 29 to 100, whereas men were 34 to 87 years old (Appendix 1).

The community of OX had the highest value of IKR (0.62), representing 62 % of the species reported (21 of 34 species reported in the community). In OX the highest IKR was registered among elder women from 71 to 80 years old. In TG the highest IKR (0.58) was registered among women from 61 to 70 years old, whereas in CB it was 0.57 among younger women, 41-50 years old; in LC the IKR was 0.53 among women 41-70 years old. Values of IKR in all communities averaged 10 to 11 species of medicinal trees (Table 5, Appendix 1).

Table 5 Index of Knowledge Richness (IKR) of the four study communities. The total number of medicinal tree species (MTS) is the sum resulting from the floristic reference list and the free list; S = number of species. 

Community Total no. interviews Total no. MTS Max. IKR Smax Min. IKR Smin Mean IKR Smean
Oxolotán 28 34 0.62 21 0.06 2 0.33 11
Cerro Blanco 29 28 0.57 16 0.11 3 0.36 10
Tomás Garrido 26 31 0.58 18 0.19 6 0.35 11
La Cumbre 24 30 0.53 16 0.13 4 0.32 10

The species with the highest cultural importance, according to the cumulative cultural significance was Gliricidia sepium, which had the highest values of ICS in the communities OX, CB, and TG. Bursera simaruba, Piper auritum, Pimenta dioica, Theobroma cacao, Guazuma ulmifolia, and Byrsonima crassifolia were classified in the category of high cultural importance (Table 6).

Table 6 Index of cultural significance (ICS) and cumulative index of cultural significance (CICS) of medicinal tree species in the four study communities in southern Tabasco, Mexico. Levels of cultural significance are based on Turner (1988): very high ≥ 100; high = 50-99; moderate = 20-49; low = 5-19; very low = 1-4; unimportant = 0. 

ICS/ community
Species Oxolotán Cerro Blanco Tomás Garrido La Cumbre CICS Cumulative level of cultural significance
Gliricidia sepium 33 46 36 20 135 very high
Bursera simaruba 13 40 11 25 89 high
Piper auritum 35 31 18 4 87 high
Pimenta dioica 26 7 21 22 75 high
Theobroma cacao 18 20 16 11 65 high
Guazuma ulmifolia 9 15 17 19 60 high
Byrsonima crassifolia 14 19 6 11 50 high
Persea americana 14 7 10 13 45 moderate
Cedrela odorata 17 5 17 3 42 moderate
Pouteria sapota 15 13 9 4 41 moderate
Tabebuia rosea 11 11 9 7 37 moderate
Annona reticulata 12 0 9 8 29 moderate
Cecropia obtusifolia 8 2 6 14 29 moderate
Manilkara zapota 6 3 9 3 20 moderate
Castilla elastica 3 5 6 2 16 low
Erythrina americana 0 0 8 2 10 low
Pachira aquatica 3 2 1 3 9 low
Ceiba pentandra 1 0 2 0 3 very low
Brosimum alicastrum 1 0 0 0 1 very low
Genipa americana 0 0 0 0 0 unimportant
Pseudobombax ellipticum 0 0 0 0 0 unimportant

Priority species for ecological restoration. Information resulting from workshops indicated that 15 tree species are of high interest for actions of forest restoration. This selection is mainly due to the local criterion of low availability of a resource and the difficulty of reproduction since some species are "rogadas", as people say, which means that they do not seem to reproduce easily in the wild. These species were also considered as important by 61-100 % of the people interviewed in each community (Table 7). Such is the case of Manilkara zapota which was considered by all people interviewed in OX and TG as a species that should be considered in restoration actions; the same was recorded for Brosimum alicastrum in TG (Table 7). Annona reticulata, Tabebuia rosea, Persea americana and Brosimum alicastrum received an importance value in the workshops, providing support to their use as priority species in ecological restoration actions in the four communities (100 %). On the other hand, because of their widespread occurrence in the region, Bursera simaruba, Cecropia obtusifolia, Gliricidia sepium, Erythrina americana and Piper auritum did not receive importance values in any community (0 %). Pseudobombax ellipticum is a species was not known to occur in the forest areas by any participant in the workshops and interviews (Table 7).

Table 7 Priority species in the study communities for use in ecological restoration. W = Workshops, VI = Value of importance, range from 1 to 10, where 1 is the species of greatest priority for restoration projects; I = Interviews, Percentage of interviewed who consider the priority species for restoration. 

Priority species for restoration in each community
Oxolotán Cerro Blanco Tomás Garrido La Cumbre % Species priority.
Community workshops
No. Species W (VI) I (%) W (VI) I (%) W (VI) I (%) W (VI) I (%)
1 Annona reticulata 8 82 2 90 3 96 1 83 100
2 Tabebuia rosea 7 68 1 79 8 88 8 79 100
3 Persea americana 9 61 5 69 5 81 10 67 100
4 Brosimum alicastrum 5 82 8 72 2 100 5 71 100
5 Pimenta dioica 6 89 3 97 81 4 83 75
6 Genipa americana 3 68 9 62 9 73 58 75
7 Manilkara zapota 4 100 4 97 4 100 79 75
8 Pouteria sapota 89 6 86 1 96 6 79 75
9 Pachira aquatica 54 7 62 58 2 75 50
10 Byrsonima crassifolia 10 64 31 7 62 33 50
11 Theobroma cacao 2 75 41 6 96 88 50
12 Cedrela odorata 1 89 66 77 3 79 50
13 Ceiba pentandra 54 59 10 65 7 67 50
14 Castilla elastica 64 10 62 50 58 25
15 Guazuma ulmifolia 36 21 38 9 63 25
16 Bursera simaruba 32 17 23 29 0
17 Cecropia obtusifolia 14 3 0 17 0
18 Gliricidia sepium 25 28 27 33 0
19 Erythrina americana 36 38 38 29 0
20 Piper auritum 4 14 15 0 0
21 Pseudobombax ellipticum 7 0 8 0 0

Discussion

Cultural significance of tree species and its value for ecological restoration. In total, we identified 45 species of trees with medicinal use in the region. This group of species includes elements of both primary and secondary vegetation. Such number of tree species represents 5.5 % of the species reported by Toledo et al. (1995) in his study of useful plant species from the tropical rainforest of Mexico. The main categories of illnesses in the study area are gastrointestinal, as well as those causing pain and fever, similarly as reported in other studies among indigenous peoples (Sepúlveda 1993, Magaña-Alejandro et al. 2010, Gómez-Álvarez 2012). In this study, we found different species used for treating different illnesses, which we interpret as conferring resilience to the local capacities for attending health. However, we also identified tree species that may be used for treating different illnesses (up to eight), which is an indicator of the use value of particularly important species; yet it is also an indicator of vulnerability of the traditional health systems since if populations of these species are affected by disturbance, the local capacities for attending health might be affected. Traditional knowledge associated with the use of a particularly declining species also runs that same risk of disappearing at local or regional scales (Albuquerque et al. 2006, Shaheen et al. 2017); in our study, an example of this coupling between ecology and knowledge seems to be the case of Pseudobombax ellipticum, which is not reported any longer to be extant in the region and therefore no associated uses of it were detected.

The analysis of the cultural significance of species (as an integral representation of the multiplicity of uses of a plant species) is a quantitative ethnobotanical evaluation for understanding the most meaningful resources in a human cultural context (Turner 1988, Stoffle et al. 1990, Bennett & Prance 2000, Almeida et al. 2005, Albuquerque & Lucena 2005, Silva & Albuquerque 2005, Silva et al. 2006, Helida et al. 2015), and may be particularly helpful for designing strategies of protection and conservation of biological diversity (Turner 1988, Gupta 2004, Reyes-García et al. 2006, Hoffman & Gallaher 2007). Our study emphasizes ecological restoration, since our efforts are aimed at identifying species of local interest that can be used to recover deforested or degraded forest areas.

A number of studies have been reported where species with high cultural importance may be severely impacted by local exploitation (e.g.Albuquerque & Lucena 2005, Albuquerque 2006). According to Turner (1988), the higher the number of uses of a plant species, the higher the probability of having a higher cultural value for a community. This value may vary for a species in different contexts of knowledge, use, human culture, and environmental conditions (Turner 1988, Pei et al. 2009). Although most valuable resources may probably be most affected, these may also be those on which peoples have developed management experiences (Casas et al. 1997, 2007, 2016, 2017). It has been documented in different parts of Mexico that plant species highly valued by people but with a restricted distribution and scarce availability, as well as other indicators of vulnerability to extraction (long life cycle, specialized breeding system, low capacity of recovering to disturbance, among other features), are those on which people develop more careful and complex management techniques (Arellanes et al. 2013, Blancas et al. 2010, 2013, Rangel-Landa et al. 2017). Managed or not, these species may be in risk to disappear if high use intensity prevails on them; yet if there are management techniques available the restoration programs would be benefited.

In this study, Persea americana and Cecropia obtusifolia are not the most culturally valued species, yet they are widely used for attending the highest number of illnesses; moderate values of cultural significance of these species are due to the low frequency and exclusiveness of their uses. Gliricidia sepium, Bursera simaruba and Piper auritum, have high and very high cultural importance. This would suggest using these species in actions of ecological restoration. However, the quantitative ethnobotanical analysis does not reflect the real interest that people have in using these species in ecological restoration projects. In the case of Gliricidia sepium and Piper auritum, because of their growth habit and habitat restricted to highly lighted spots, it would not be expected to contribute to creating a forest cover. In addition, none of these two species are valued as a source of fuelwood or other timber uses. Finally, this appreciation is also explained because some of these species are locally abundant and, as people say “they grow by themselves”, which makes reference to the fact that these species reproduce and grow easily and their products are also easily obtained. Similar cases are also the species Cecropia obtusifolia and Erythrina americana.

Particular attention deserves the case of Brosimun alicastrum, a species of very low cultural significance but yet considered a priority species for ecological restoration. This latter consideration is based on the recognition of its low availability, which makes necessary to walk long distances to reach its useful products. Similar are the cases of Manilkara zapota and Cedrela odorata, the latter a species registered in the official Mexican norms for protection NOM 059, due to its scarcity (SEMARNAT 2010) and progressive population depletion (Hernández-Ramos et al. 2018). From these cases, a few lessons can be extracted. First, ethnobotanical and cultural value considerations for protection and restoration should not be restricted to a single use criterion but they should consider their broad spectrum of uses and benefits. Second, the local perception of distribution, abundance and vulnerability of the populations should be considered. Third, the local experiences about managing plant species are crucial because they reflect the local worries of people to maintain those plants, and they may also provide particular techniques to planning successful actions.

Species of medicinal trees recorded in this study and with high priority for their use in forest restoration practices are part of the primary vegetation (Brosimun alicastrum and Manilkara zapota), while Pouteria sapota, Genipa americana and Pimenta dioica are part of both primary and secondary forests. Castilla elastica, Cedrela odorata, and Guazuma ulmifolia are pioneer species in secondary vegetation, as well as Ceiba pentandra, Tabebuia rosea, Anonna reticulata, Persea americana, Theobroma cacao and Byrsonima crassifolia (Pennington & Sarukhán 2005, Parker 2008, González-Espinosa & Ramírez-Marcial 2013). Most tree species selected for medicinal use in the study area are part of the secondary vegetation, which is not surprising since as Toledo et al. (1995) and other authors have reported, secondary forests are the main providers of medicinal products, nearly twice than primary forests. Stepp (2004) and Voeks (2004) mention that anthropic landscapes are the main source of medicines in tropical forests. In addition, numerous authors (Toledo et al. 1992, Voeks 1996, Chazdon & Coe 1999, among others) identify disturbed areas as sites where medicinal plants are particularly abundant.

The study area has been drastically impacted by humans for many centuries. Several important cultures inhabited and managed the regional forests for thousands of years. Yet the most drastic destruction started in the mid-20th century, with governmental programs aimed to transform tropical rain forests into pastures and monocultures over extensive areas (Tudela 1989, Sánchez-Munguía 2005); this process has advanced until the present with strong consequences on losing of biodiversity and traditional cultures (Gómez-Pompa et al. 1972, Gómez-Pompa & Kaus 1999, Toledo 1987, Toledo et al. 1995, Sheil & Lawrence 2004, Reyes-Tagle 2007, González-Cruz et al. 2014).

This study aspires to contribute with some methodological elements and insights for linking local medicinal knowledge, values and experiences with ecological research to design strategies for restoration of tropical rain forests. Both ecological and human cultural roles of species deserve to be considered when planning ecological restoration actions. Structural and functional roles of species are important, as well as their role in satisfying local needs and technical experiences for managing the relevant resources. Ethnobotanical and ecological research are both important for recovering resources, their populations and the ecosystems where they occur (Garibaldi & Turner 2004). Particularly important are long-lived trees, which are valuable resources and help to put in perspective long-term conservation and sustainable use actions, which are particularly important in tropical forests (Janzen 1970, Gómez-Pompa et al. 1972, Novotny et al. 2006, Wuethrich 2007, Chazdon 2008).

Due to its identification of medicinal tree species with both cultural and ecological importance should TMK become part of a strategy to be considered in tropical forest restoration actions? Our results show that through TMK we can identify culturally important species for their medicinal uses, we also find that the species that are culturally important are not those considered with priority for their management of propagation and reintroduction in the area for forest restoration. The TMK information shows that regardless of the high values of cultural significance of the species, the criterion for selecting them for restoration is not restricted to the importance of their use, but also, and mainly, to their low availability and the perception of difficulties regarding their natural regeneration.

Our results also provide information on the pressure received by some culturally significant and abundant species (e.g. Gliricidia sepium, Bursera simaruba, Piper auritum, and Cecropia obtusifolia); their wide availability is sustaining increasing use associated to their perceived medicinal value. On the other hand, other species with very low availability have few medicinal uses. We consider that the TMK in particular, as well as TEK when other non-medicinal uses are associated to medicinal trees of the region, are relevant to design local strategies of restoration of tropical forests; it is to be expected that when selecting species of local cultural interest, the long-term ecological restoration actions may be more probably successful due to the involvement of local actors from the early stages of the process.

The role of gender in traditional medicinal knowledge. The highest values of IKR in all communities were recorded among adult and elder women, particularly in Oxolotán, where expert traditional physicians are recognized and, although institutional health services are available, local people still consult them. The localities of Tomás Garrido and La Cumbre have also local experts, mainly for attending births and cultural illnesses. We recorded the lowest number of medicinal trees in the Cerro Blanco community, which could be associated with the ages of the women interviewed, 25 adults and 4 elderly women (see Appendix 1). In addition, it could be due to the particular fact that we were not able to interview any men there that could possibly add to the knowledge of some other species. According to Stagegaard et al. (2002) and Luoga et al. (2000) knowledge of the medicinal flora may be different between men and women, and these authors argue that women have a deeper knowledge of the medicinal properties of herbaceous plants, while men recognize the medicinal attributes of trees and lianas. However, our results show that adult and elderly women have the greatest wealth of knowledge on medicinal tree species detected in this study, contrary to the reports by Stagegaard et al. (2002) and Luoga et al. (2000). Our finding is consistent with the pattern reported in other tropical regions (Kainer & Duryea 1992, Coe & Anderson 1996, Gollin 1997, Begossi et al. 2000, Voeks & Nyawa 2001, Kothari 2003, Voeks 2007). Age is also positively related to a higher TMK, a finding similarly reported by Case et al. (2005), Quinlan & Quinlan (2007), Eyssartier et al. (2008), Silalahi et al. (2015) and Shaheen et al. (2017), among others.

In our study, we observed that women have a relevant role in the preservation of medicinal culture, since they have a high wealth of traditional knowledge about medicinal trees in the region. Adult and elderly women recognize species with medicinal uses as well as their low availability for their use. This knowledge input from women has contributed to the selection of species that can be used in programs to restore the forest cover of the tropical forest of the region.

We report an average IKR value of less than half the total number of medicinal trees registered in this study. The wealth of knowledge about the medicinal uses of native tree species can be considered a reference to the current status of the TMK and may also indicate that the current status of the TMK is possibly eroding in the Maya and Zoque communities of the region. This could have negative implications at the local and regional scales (Albuquerque et al. 2006, Shaheen et al. 2017). This study suggests that the maintenance of TMK in the local communities can be attained by selecting tree species of medicinal interest for forest restoration programs.

We conclude that TMK provides useful criteria for the identification of the cultural significance of the tree species included in this study; it also reflects the interest that local people have in the management of the species, in particular those considered to be high priority for restoration actions of the tropical forest. This traditional knowledge provides information on the uses, cultural values and local experiences of species management, which may be considered useful in a comprehensive analysis of possible restoration actions in tropical forests.

Acknowledgements

We would like to thank the Posgrado en Ciencias Biológicas at the UNAM and the Consejo Nacional de Ciencia y Tecnología (CONACYT) for supporting doctoral studies of the first author. Financial support was provided by projects IN206217 (UNAM) and CB-2013-01-221800 (CONACYT), as well as fiscal funds available through ECOSUR and a grant from the Rufford Foundation. We thank the Colectivo Almandros ‘Por un Mundo Mejor’ (CAMUM), Henry E. Castañeda-Ocaña, and Jorge Alberto Cruz Hernández for help in the field, and Lupita Carrillo and Manuel Cach for useful discussions on methodological issues.

Literature cited

Akerele O. 1993. Nature´s medicinal bounty; don´t throw it away. World health forum 14: 390-395. [ Links ]

Albuquerque UP, Lucena RFP. 2005. Can apparency affect the use of plants by local people in tropical forests? Interciencia 30: 506-511. [ Links ]

Albuquerque UP. 2006. Re-examining hypotheses concerning the use and knowledge of medicinal plants: a study in the Caatinga vegetation of NE Brazil. Journal of Ethnobiology and Ethnomedicine 2: 30. DOI: https://doi.org/10.1186/1746-4269-2-30 [ Links ]

Albuquerque UP, Lucena RF, Monteiro JM, Florentino AT, Almeida CFC. 2006. Evaluating two quantitative ethnobotanical techniques. Ethnobotany Research and Applications 4: 51-60. [ Links ]

Albuquerque UP, Alves-Ramos M, Farias-Pavia-Lucena R, Leal-Alencar N. 2014. Methods and techniques used to collect ethnobiological data. In: Albuquerque UP, Cruz LVF, Lucena RFP, Alves RRN, eds. Methods and Techniques in Ethnobiology and Ethnoecology, Springer. [ Links ]

Alencar NL, Santoro FR, Albuquerque UP. 2014. What is the role of exotic medicinal plants in local medical systems? A study from the perspective of utilitarian redundancy. Revista Brasileira de Farmacognosia 24: 506-515. DOI: https://doi.org/10.1016/j.bjp.2014.09.003 [ Links ]

Almeida CFCBR, Lima-Silva TC, Amorim ELC, Maia MBS, Albuquerque UP. 2005. Life strategy and chemical composition as predictors of the selection of medicinal plants from the Caatinga (Northeast Brazil). Journal of Arid Environments 62: 127-142. DOI: https://doi.org/10.1016/j.jaridenv.2004.09.020 [ Links ]

Anyinam C. 1995. Ecology and ethnomedicine: Exploring links between current environmental crisis and indigenous medical practices. Social Science and Medicine 40: 321-329. DOI: https://doi.org/10.1016/0277-9536(94)E0098-D [ Links ]

Arellanes Y, Casas A, Arellanes A, Vega E, Blancas J, Vallejo M, Torres I, Rangel-Landa S, Moreno AI, Solís L, Pérez-Negrón E. 2013. Influence of traditional markets on plant management in the Tehuacán Valley. Journal of ethnobiology and ethnomedicine 9: 38. DOI: https://doi.org/10.1186/1746-4269-9-38 [ Links ]

Begossi A, Hanazaki N, Peroni N. 2000. Knowledge and use of biodiversity in Brazilian hot spots. Environment, Development and Sustainability 2: 177-193. DOI: https://doi.org/10.1023/A:1011409923520 [ Links ]

Bennett BC, Prance GT. 2000. Introduced Plants in the Indigenous Pharmacopeia of Northern South America. Economic Botany 54: 90-102. DOI: https://doi.org/10.1007/BF02866603 [ Links ]

Bensusán N. 2011. Retos de la gestión sustentable de los servicios de agua y saneamiento en comunidades rurales. Caso de estudio de Tacotalpa, Tabasco. Naciones Unidas. CEPAL. México. [ Links ]

Benz B, Cevallos JE, Santana FM, Rosales JA, Graf MS. 2000. Losing knowledge about plant use in the Sierra de Manantlan Biosphere Reserve, Mexico. Economic Botany 54: 183-191. DOI https://doi.org/10.1007/BF02907821 [ Links ]

Berkes F. 1993. Traditional ecological knowledge in perspective. In: Inglis JT, Ed. Traditional Ecological Knowledge: Concepts and Cases, 1-9. Canadian Museum of Nature/International Development Research Centre, Ottawa. e-ISBN: 1552502570 [ Links ]

Berkes F, Turner N. 2005. Conocimiento, aprendizaje y la flexibilidad de los sistemas socioecológicos. Gaceta Ecológica 77: 5-17. [ Links ]

Bernard RH. 1995. Research methods in Anthropology: Qualitative and quantitative approaches. Second Edition. New York: Altamira Press. ISBN 0-8039-5244-9.—ISBN 0-8039-5245-7 (pbk.) [ Links ]

Blancas J, Casas A, Rangel-Landa S, Moreno-Calles A, Torres I, Pérez-Negrón E, Solís L, Delgado-Lemus A, Parra F, Arellanes Y, Caballero J, Cortés L, Lira R, Dávila P. 2010. Plant management in the Tehuacán-Cuicatlán Valley, México. Economic Botany 64: 287-302. DOI: https://doi.org/10.1007/s12231-010-9133-0 [ Links ]

Blancas J, Casas A, Pérez-Salicrup D, Caballero J, Vega E. 2013. Ecological and socio-cultural factors influencing plant management in Náhuatl communities of the Tehuacán Valley, Mexico. Journal of Ethnobiology and Ethnomedicine 9: 39. DOI: https://doi.org/10.1186/1746-4269-9-39 [ Links ]

Brito CC, Silva TC, Albuquerque UP, Ramos MA, Ferreira Júnior WS, Barros FN, Costa Neto EM, Medeiros PM. 2017. The use of different indicators for interpreting the local knowledge loss on medical plants. Revista Brasileira de Farmacognosia 27: 245-250. DOI: https://doi.org/10.1016/j.bjp.2016.09.006 [ Links ]

Cabrera PAJ, Juárez MH, Sánchez GE, Castelán GM, Almazán MBT. 2015. Los saberes en medicina tradicional y su contribución al desarrollo rural: estudio de caso Región Totonaca, Veracruz. Revista Mexicana de Ciencias Agrícolas 6: 1791-1805. [ Links ]

Casas A, Pickersgill B, Caballero J, Valiente-Banuet A. 1997. Ethnobotany and domestication in xoconochtli, Stenocereus stellatus (Cactaceae), in the Tehuacán Valley and la Mixteca Baja, México. Economic Botany 51: 279-292. DOI: https://doi.org/10.1007/BF02862097 [ Links ]

Casas A, Otero-Arnaiz A, Pérez-Negrón E, Valiente-Banuet A. 2007. In situ management and domestication of plants in Mesoamerica. Annals of Botany 100: 1101-1115. DOI: https://doi.org/10.1093/aob/mcm126 [ Links ]

Casas A, Camou A, Otero-Arnaiz A, Rangel-Landa S, Cruse-Sanders J, Solís L, Torres I, Delgado A, Moreno-Calles AI, Vallejo M, Guillén S, Blancas J, Parra F, Farfán-Heredia B, Aguirre-Dugua X, Arellanes Y, Pérez-Negrón E. 2014. Manejo tradicional de biodiversidad y ecosistemas en Mesoamérica: el Valle de Tehuacán. Investigación Ambiental Ciencia y Política Pública 6: 23-44 [ Links ]

Casas A, Lira R, Torres I, Delgado A, Moreno-Calles AI, Rangel-Landa S, Blancas J, Larios C, Solís L, Pérez-Negrón E,Vallejo M, Parra F, Farfán-Heredia B, Arellanes Y, Campos N. 2016. Ethnobotany for sustainable ecosystem management: a regional perspective in the Tehuacán Valley. In: Lira R, Casas A, Blancas J, eds. Ethnobotany of Mexico, 179-206. Springer, New York, NY. DOI: https://doi.org/10.1007/978-1-4614-6669-7_8 [ Links ]

Casas A, Torres I, Delgado-Lemus A, Rangel-Landa S, Ilsley C, Torres-Guevara J, Cruz A, Parra F, Moreno-Calles AI, Camou A, Castillo A, Ayala-Orozco B, Blancas JJ, Vallejo M, Solís L, Bullen A, Ortiz T, Farfán B. 2017. Ciencia para la sustentabilidad: investigación, educación y procesos participativos. Revista Mexicana de Biodiversidad 88: 113-128. DOI: https://doi.org/10.1016/j.rmb.2017.10.003 [ Links ]

Case RJ, Pauli GF, Soejarto DD. 2005. Factors in maintaining indigenous knowledge among ethnic communities of Manus Island. Economic Botany 59: 356-365. DOI: https://doi.org/10.1663/0013-0001(2005)059[0356:FIMIKA]2.0.CO;2 [ Links ]

Castellanos-Camacho LI. 2011. Conocimiento etnobotánico, patrones de uso y manejo de plantas útiles en la cuenca del río Cane-Iguaque (Boyacá-Colombia); una aproximación desde los Sistemas de Uso de la Biodiversidad. Ambiente and Sociedad 14: 45-75. DOI: http://dx.doi.org/10.1590/S1414-753X2011000100004 [ Links ]

Challenger A. 1998. Utilización y Conservación de los Ecosistemas Terrestres de México: pasado, presente y futuro. Instituto de Biología, Universidad Nacional Autónoma de México. México. ISBN: 9709000020 [ Links ]

Challenger A, Soberón J. 2008. Los ecosistemas terrestres. In: Sarukhán J, coord. Capital Natural de México, vol. I: Conocimiento Actual de la Biodiversidad, 87-108. Comisión Nacional para el Conocimiento y Uso de la Biodiversidad. México. ISBN: 978-607-7607-03-8 [ Links ]

Charnley S, Fischer AP, Jones ET. 2008. Traditional and local ecological knowledge about forest biodiversity in the Pacific Northwest. General Technical Report PNW-GTR-751, US. Department of Agriculture, Forest Service, Pacific Northwest Research Station. [ Links ]

Chazdon RL. 2008. Beyond deforestation: restoring forests and ecosystem services on degraded lands. Science 320: 1458-1460. DOI: https://doi.org/10.1126/science.1155365 [ Links ]

Chazdon R, Coe FG. 1999. Ethnobotany of woody species in second-growth, old-growth and selectively logged forests of Northeastern Costa Rica. Conservation Biology 13: 1312-1322. DOI: https://doi.org/10.1046/j.1523-1739.1999.98352.x [ Links ]

Chekole G. 2017. Ethnobotanical study of medicinal plants used against human ailments in Gubalafto District, Northern Ethiopia. Journal of Ethnobiology and Ethnomedicine 13: 55. DOI: https://doi.org/10.1186/s13002-017-0182-7 [ Links ]

Coe FG, Anderson GJ. 1996. Ethnobotany of the Garífuna of Eastern Nicaragua. Economic Botany 50: 71-107. DOI: https://doi.org/10.1007/BF02862114 [ Links ]

Cox PA. 2000. Will tribal knowledge survive the millennium? Science 287: 44-45. DOI: https://doi.org/10.1126/science.287.5450.44 [ Links ]

DeFries RS, Ellis EG, Chapin III FS, Matson PA, Turner II BL, Agrawal A, Crutzen PJ, Field C, Gleick P, Kareiva PM, Lambin E, Liverman D, Ostrom E, Sanchez PA, Syvitski J. 2012. Planetary opportunities: A social contract for global change science to contribute to a sustainable future. BioScience 62: 603-606. DOI: https://doi.org/10.1525/bio.2012.62.6.11 [ Links ]

Eyssartier C, Ladio AII, Lozada M. 2008. Cultural transmission of traditional knowledge in two population of Northwestern Patagonia. Journal of Ethnobiology and Ethnomedicine 4: 1-8. DOI: https://doi.org/10.1186/1746-4269-4-25 [ Links ]

Fabricant DS, Farnsworth NR. 2001. The value of plants used in traditional medicine for drug discovery. Environmental Health Perspectives 109: 69-75. DOI: https://doi.org/10.1289/ehp.01109s169 [ Links ]

Fagetti A. 2011. Fundamentos de la medicina tradicional mexicana. In: Argueta A, Corona ME, Hersch P, eds. Saberes Colectivos y Diálogo de Saberes en México, 137-151. Universidad Nacional Autónoma de México, México. ISBN: 978-607-02-2367-9 [ Links ]

Foster GM. 1953. Relationships between Spanish and Spanish-American folk medicine. The Journal of American Folklore 66: 201-217. DOI: https://doi.org/10.2307/537230 [ Links ]

García-Barrios L, González-Espinosa M. 2017. Investigación ecológica participativa como apoyo de procesos de manejo y restauración forestal, agroforestal y silvopastoril en territorios campesinos. Experiencias recientes y retos en la sierra Madre de Chiapas, México. Revista Mexicana de Biodiversidad 88: 129-140. DOI: https://doi.org/10.1016/j.rmb.2016.10.022 [ Links ]

Garibaldi A, Turner N. 2004. Cultural Keystone species: Implications for conservation and restoration. Ecology and Society 9: 1. [ Links ]

Gollin LX. 1997. Taban Kenyah: a preliminary look at the healing plants and paradigms of the Kenyah Dayak people of Kayan Mentarang. In: Sorensen K, Morris B, eds. People and Plants of Kayan Mentarang, 135-148. Jakarta WWF, Indonesia. ISBN-10: 2880852153 ISBN-13: 978-2880852153 [ Links ]

Gómez-Álvarez R. 2012. Plantas Medicinales en una aldea del Estado de Tabasco, México. Revista Fitotecnia Mexicana 35: 43-49. [ Links ]

Gómez-Pompa A, Vazquez-Yanes C, Guevara S. 1972. The tropical rain forest: a nonrenewable resource. Science 177: 762-765. DOI: https://doi.org/10.1126/science.177.4051.762 [ Links ]

Gómez-Pompa A, Kaus A. 1999. From pre-Hispanic to future conservation alternatives: lessons from Mexico. Proceedings of the National Academy of Sciences 96: 5982-5986. DOI: https://doi.org/10.1073/pnas.96.11.5982 [ Links ]

González-Cruz G, García-Frapolli E, Fernández AC, Rada JMD. 2014. Conocimiento tradicional maya sobre la dinámica sucesional de la selva. Un caso de estudio en la Península de Yucatán. Etnobiología 12: 60-67. [ Links ]

González-Espinosa M, Ramírez-Marcial N, Camacho-Cruz A, Rey-Benayas JM. 2008. Restauración de bosques en montañas tropicales de territorios indígenas de Chiapas, México. In: González-Espinosa M, Rey-Benayas JM, Ramírez-Marcial N, eds. Restauración de Bosques en América Latina, 137-162. Fundación Internacional para la Restauración de Ecosistemas (FIRE)/Editorial Mundi-Prensa México. México. ISBN: 9789687462493 [ Links ]

González-Espinosa M, Ramírez-Marcial N. 2013. Comunidades vegetales terrestres. In: Comisión Nacional para el Conocimiento y Uso de la Biodiversidad (CONABIO)/Gobierno del Estado de Chiapas. La Biodiversidad en Chiapas: Estudio de Estado, 21-42. México. ISBN Vol II: 978-607-8328-00-0 [ Links ]

Grande-Cano JD, Losada H, Cortés J, Rivera JG, Maldonado NM, Pérez-Gil F. 2009. Los árboles dispersos en potreros de la región de la Sierra de Tabasco, México. Revista Brasileira de Agroecologia 4. < http://revistas.aba-agroecologia.org.br/index.php/rbagroecologia/article/view/90920 > (accessed april 23, 2019). [ Links ]

Gupta AK. 2004. WIPO-UNEP Study on the Role of Intellectual Property Rights in the Sharing of Benefits Arising from the Use of Biological Resources and Associated Traditional Knowledge. World Intellectual Property Organization (WIPO)/United Nations Environment Programme (UNEP), India. [ Links ]

Hamilton AC. 2004. Medicinal plants, conservation and livelihoods. Biodiversity and Conservation 13: 1477-1517. DOI: https://doi.org/10.1023/B:BIOC.0000021333.23413.42 [ Links ]

Helida A, Zuhud EAM, Hardjanto H, Purwanto Y, Hikmat A. 2015. Index of cultural significance as a potential tool for conservation of plant diversity by communities in The Kerinci Seblat National Park. Jurnal Manajemen Hutan Tropika 21: 192-201. DOI: http://dx.doi.org/10.7226/jtfm.21.3.192 [ Links ]

Hernández-Ramos J, Reynoso-Santos R, Hernández-Ramos A, García-Cuevas X, Hernández-Máximo E, Cob-Uicab JV, Sumano-López D. 2018. Distribución histórica, actual y futura de Cedrela odorata en México. Acta Botanica Mexicana 124: 117-134. DOI: https://doi.org/10.21829/abm124.2018.1305 [ Links ]

Hoffman B, Gallaher T. 2007. Importance indices in ethnobotany. Ethnobotany Journal 5: 201-218. [ Links ]

INEGI [Instituto Nacional de Estadística y Geografía]. 2005. Prontuario de información geográfica municipal de los Estados Unidos Mexicanos, Tacotalpa, Tabasco. Clave geoestadística 27015. Instituto Nacional de Estadística y Geografía. México. [ Links ]

INEGI. 2010. Censo de Población y Vivienda. Instituto Nacional de Estadística y Geografía. México. [ Links ]

INEGI. 2015. Anuario estadístico y geográfico por entidad federativa 2015. Instituto Nacional de Estadística y Geografía. México. [ Links ]

Janzen DH. 1970. Herbivores and the number of tree species in tropical forests. The American Naturalist 104: 501-528. DOI: https://doi.org/10.1086/282687 [ Links ]

Kainer KA, Duryea M. 1992. Tapping women’s knowledge: Plant resource use in extractive reserves, Acre Brazil. Economic Botany 46: 408-425. DOI: https://doi.org/10.1007/BF02866513 [ Links ]

Koleff P, Urquiza-Haas T, Contreras B. 2012. Prioridades de conservación de los bosques tropicales en México: reflexiones sobre su estado de conservación y manejo. Ecosistemas 21: 6-20. [ Links ]

Kothari B. 2003. The invisible queen in the plant kingdom: Gender perspectives in medical ethnobotany. In: Howard PL, ed. Women and Plants: Gender Relations in Biodiversity Management and Conservation, 150-164. London and New York: Zed Books Ldt. ISBN: 9781842771570 [ Links ]

Levy-Tacher S, Ramírez-Marcial N, González-Espinosa M, Román-Dañobeytia F. 2012. Rehabilitación ecológica de áreas agropecuarias degradadas en la Selva Lacandona: una alternativa fincada en el conocimiento ecológico tradicional maya. In: Bello E, Naranjo EJ, Vandame R, eds. La Otra Innovación para el Ambiente y la Sociedad en la Frontera Sur de México, 248-258. El Colegio de la Frontera Sur, Chiapas, México. ISBN: 978-607-7637-45-5 [ Links ]

Linares E, Bye R. 1987. A study of four medicinal plant complexes of Mexico and adjacent United States. Journal of Ethnopharmacology 19: 153-183. DOI: https://doi.org/10.1016/0378-8741(87)90039-0 [ Links ]

Lindig-Cisneros R. 2017. Ecología de la restauración y restauración ambiental. Universidad Nacional Autónoma de México. ISBN: 9786070294495 [ Links ]

López-Hernández E. 1994. La Vegetación y la Flora de la Sierra de Tabasco (Municipios de Tacotalpa y Teapa), México. Universidad Juárez Autónoma de Tabasco. Villahermosa, Tabasco, México. [ Links ]

Lulekal E, Kelbessa E, Bekele T, Yineger H. 2008. An ethnobotanical study of medicinal plants in Mana Angetu District, southeastern Ethiopia. Journal of Ethnobiology and Ethnomedicine 4: 10. DOI: https://doi.org/10.1186/1746-4269-4-10 [ Links ]

Luoga E, Witkowski E, Balkwill K. 2000. Differential utilization and ethnobotany of trees in Kitulanghalo Forest Reserve and surrounding communal lands, Eastern Tanzania. Economic Botany 54: 328-343. DOI: https://doi.org/10.1007/BF02864785 [ Links ]

Luziatelli G, Sörensen M, Theilade I, Mölgaard P. 2010. Asháninka medicninal plants: a case study from the native community of Bajo Quimiriki, Junín, Perú. Journal of Ethnobiology and Ethnomedicine 6: 1-21. DOI: https://doi.org/10.1186/1746-4269-6-21 [ Links ]

Mace R, Pagel M. 1995. A latitudinal gradient in the density of human languages in North America. Proceedings of the Royal Society: Biological Sciences 261: 117-121. DOI: https://doi.org/10.1098/rspb.1995.0125 [ Links ]

Maffi L. 2005. Linguistic, cultural, and biological diversity. Annual Review of Anthropology 34: 599-617. DOI: https://doi.org/10.1146/annurev.anthro.34.081804.120437 [ Links ]

Magaña-Alejandro MA. 2006. Catálogo de nombres vulgares y científicos de plantas de Tabasco. Universidad Juárez Autónoma de Tabasco. Villahermosa, Tabasco, México. ISBN: 9685748950 [ Links ]

Magaña-Alejandro MA, Gama Campillo LM, Mariaca-Méndez R. 2010. El uso de las plantas medicinales en las comunidades Maya-Chontales de Nacajuca, Tabasco, México. Polibotánica 29: 213-262. [ Links ]

Maldonado-Mares F. 2005. Flora medicinal del Estado de Tabasco, uso, manejo y conservación. Universidad Juárez Autónoma de Tabasco. Villahermosa, Tabasco, México. [ Links ]

Masera O, Ordóñez MJ, Dirzo R. 1992. Emisiones de carbono a partir de la deforestación en México. Ciencia 43: 151-153. [ Links ]

Medellín-Morales S, Barrientos-Lozano L, Mora-Olivo A, Almaguer-Sierra P, Mora-Ravelo GS. 2017. Diversidad de conocimiento etnobotánico tradicional en la reserva de la biosfera “El Cielo”, Tamaulipas, México. Ecología Aplicada 16: 49-61. DOI: http://dx.doi.org/10.21704/rea.v16i1.904 [ Links ]

Miranda F, Hernández-X E. 2014. Los Tipos de Vegetación de México y su clasificación. Edición conmemorativa 1963-2013. Colec. Ediciones Científicas Universitarias. FCE, CONABIO. México. ISBN: 9786071618634; 9786078328086 [ Links ]

Moore JL, Manne L, Brooks T, Burgess ND, Davies R, Rahbek C, Williams P, Balmford A. 2002. The distribution of cultural and biological diversity in Africa. Proceedings of the Royal Society of London B: Biological Sciences 269: 1645-1653. DOI: https://doi.org/10.1098/rspb.2002.2075 [ Links ]

Myers N, Mittermeier R, Mittermeier GC, Dafonseca GAB, Kent J. 2000. Biodiversity hotspots for conservation priorities. Nature 403: 853-858. DOI: https://doi.org/10.1038/35002501 [ Links ]

Novotny V, Drozd P, Miller SE, Kulfan M, Janda M, Basset Y, Weiblen GD. 2006. Why are there so many species of herbivorous insects in tropical rainforests? Science 313: 1115-1118. DOI: https://doi.org/10.1126/science.1129237 [ Links ]

Ortiz-Pérez MA, Siebe C, Cram S. 2005. Diferenciación geográfica de Tabasco. In: Bueno-Soria J, Álvarez-Noguera F, Santiago S, eds. Biodiversidad del Estado de Tabasco, 305-322. Instituto de Biología, UNAM-CONABIO. México. ISBN: 970-9000-26-8 [ Links ]

Parker T. 2008. Trees of Guatemala. The Tree Press, Austin, Texas. ISBN-10: 0971873909 ISBN-13: 978-0971873902 [ Links ]

Pei S, Zhang G, Huai H. 2009. Application of traditional knowledge in forest management: ethnobotanical indicators of sustainable forest use. Forest Ecology and Management 257: 2017-2021. DOI: https://doi.org/10.1016/j.foreco.2009.01.003 [ Links ]

Pennington T, Sarukhán J. 2005. Árboles tropicales de México: manual para la identificación de las principales especies. Universidad Nacional Autónoma de México. México DF: Fondo de Cultura Económica, ISBN: 9789681678555 [ Links ]

Phillips O, Gentry AH. 1993. The useful plants of Tambopata, Peru: II. Additional hypothesis testing in quantitative ethnobotany. Economic Botany 47: 15-32. DOI: https://doi.org/10.1007/BF02862204 [ Links ]

Pochettino ML, Lema VS. 2008. La variable tiempo en la caracterización del conocimiento botánico Tradicional. Darwiniana 46: 227-239. DOI: https://doi.org/10.14522/darwiniana.2014.462.285 [ Links ]

Quinlan MB, Quinlan RJ. 2007. Modernization and medicinal plant knowledge in a Caribbean horticultural village. Medical Anthropology Quarterly 21: 169-192. DOI: https://doi.org/10.1525/maq.2007.21.2.169 [ Links ]

Ramírez-Marcial N, González-Espinosa M, Musálem-Castillejos K, Noguera-Savelli E, Gómez-Pineda E. 2014. Estrategias para una construcción social de la restauración forestal en comunidades de la cuenca media y alta del Río Grijalva. In: González-Espinosa M, Brunel-Manse C, coords. Montañas, Pueblos y Agua. Dimensiones y Realidades de la Cuenca Grijalva, 528-564. El Colegio de la Frontera Sur/Juan Pablos Editor. México. ISBN-10: 6078429019; ISBN-13: 978-6078429011 [ Links ]

Rangel-Landa S, Casas A, García-Frapolli E, Lira R. 2017. Sociocultural and ecological factors influencing management of edible and non-edible plants: the case of Ixcatlán, Mexico. Journal of ethnobiology and ethnomedicine 13: 59. DOI: https://doi.org/10.1186/s13002-017-0185-4 [ Links ]

Reyes-García V, Vadez V, Huanca T, Leonard W, Wilkie D. 2005. Knowledge and consumption of wild plants: a comparative study in two Tsimane’ villages in the Bolivian Amazon. Ethnobotany Research and Applications 3: 201-207. [ Links ]

Reyes-García V, Huanca T, Vadez V, Leonard W, Wilkie D. 2006. Cultural, practical and economic value of wild plants: A quantitative study in the Bolivian Amazon. Economic Botany 60: 62-74. DOI: https://doi.org/10.1663/0013-0001(2006)60[62:CPAEVO]2.0.CO;2 [ Links ]

Reyes-García V, Guéze M, Luz AC, Paneque-Gálvez J, Macía MJ, Orta-Martínez M, Pino J, Rubio-Campillo X. 2013. Evidence of traditional knowledge loss among a contemporary indigenous society. Evolution and Human Behavior: official journal of the Human Behavior and Evolution Society 34: 249-257. DOI: https://doi.org/10.1016/j.evolhumbehav.2013.03.002 [ Links ]

Reyes-Tagle Y. 2007. La protección del conocimiento tradicional a través de las bases de datos y registros en la Convención sobre Diversidad Biológica y la Convención de Lucha Contra la Desertificación. Agenda Internacional 14: 25-39. [ Links ]

Ryan CJ. 1992. Life Support: Conserving biological diversity. Worldwatch Paper 108. Washington, DC: Worldwatch Institute. ISBN-10: 1878071092; 978-1878071095 [ Links ]

Rzedowski J. 1998. Diversidad y orígenes de la flora fanerogámica de México. In: Ramamoorthy TP, Bye R, Lot A, Fa J, eds. Diversidad Biológica de México: Orígenes y Distribución, 129-145. Instituto de Biología, UNAM. ISBN: 9683665888 [ Links ]

Rzedowski J. 2006. Vegetación de México. 1ra. Edición digital, Comisión Nacional para el Conocimiento y Uso de la Biodiversidad. México. [ Links ]

Salazar-Conde EC, Zavala-Cruz J, Castillo-Acosta O, Cámara-Artigas R. 2004. Evaluation spatial and temporal of the vegetation Sierra Madrigal, State of Tabasco, México (1973-2003). Investigaciones Geográficas 54: 7-23. [ Links ]

Sánchez-Munguía A. 2005. Uso del suelo agropecuario y desforestación en Tabasco 1950-2000. Universidad Juárez Autónoma de Tabasco. México. [ Links ]

SEMARNAT [Secretaría del Medio Ambiente y Recursos Naturales]. 2010. Norma Oficial Mexicana NOM-059-SEMARNAT-2010, Protección ambiental - Especies nativas de México de flora y fauna silvestres - Categorías de riesgo y especificaciones para su inclusión, exclusión o cambio - Lista de especies en riesgo. Diario Oficial de la Federación. 2da Sección, 30 de diciembre de 2010. [ Links ]

Sepúlveda J. 1993. La salud de los pueblos indígenas en México. Secretaría de Salud. Instituto Nacional Indigenista. Impresiones y grabados M. Serna. México. [ Links ]

Shaheen H, Qaseem MF, Amjad MS, Bruschi P. 2017. Exploration of ethno-medicinal knowledge among rural communities of Pearl Valley; Rawalakot, District Poonch Azad Jammu and Kashmir. Plos One 12: 1-32. DOI: https://doi.org/10.1371/journal.pone.0183956 [ Links ]

Sheil D, Lawrence A. 2004. Tropical biologists, local people and conservation: new opportunities for collaboration. Trends in Ecology and Evolution 19: 634-638. DOI: https://doi.org/10.1016/j.tree.2004.09.019 [ Links ]

Silalahi M, Supriatna J, Walujo EB, Nisyawati. 2015. Local knowledge of medicinal plants in sub-ethnic Batak Simalungun of North Sumatra, Indonesia. Biodiversitas 16: 44-54. DOI: https://doi.org/10.13057/biodiv/d160106 [ Links ]

Silva ACO, Albuquerque UP. 2005. Woody medicinal plants of the Catinga in the state of Pernambuco (Northeast Brazil). Acta Botanica Brasilica 19: 17-26. DOI: http://dx.doi.org/10.1590/S0102-33062005000100003 [ Links ]

Silva VA, Andrade LHC, Albuquerque UP. 2006. Revising the cultural significance index: the case of the Fulni-ô in northeastern Brazil. Field Methods 18: 98-108. DOI: https://doi.org/10.1177/1525822X05278025 [ Links ]

SER [Society for Ecological Restoration]. 2004. Ponencia introductoria de SER lnternational sobre la restauración ecológica. SER y Tucson: Society for Ecological Restoration International. [ Links ]

Stagegaard J, Sorensen M, Kvist L. 2002. Estimations of the importance of plant resources extracted by inhabitants of the Peruvian Amazon flood plain forests. Perspectives in Plant Ecology, Evolution and Systematics 5: 103-122. DOI: https://doi.org/10.1078/1433-8319-00026 [ Links ]

Stepp JR. 2004. The role of weeds as sources of pharmaceuticals. Journal of Ethnopharmacology 92: 163-166. DOI: https://doi.org/10.1016/j.jep.2004.03.002 [ Links ]

Stoffle RW, Halmo DB, Evans MJ, Olmsted JE. 1990. Calculating the cultural significance of American Indian plants: Paiute and Shoshone ethnobotany at Yucca Mountain, Nevada. American Anthropologist 92: 416-432. DOI: https://doi.org/10.1525/aa.1990.92.2.02a00100 [ Links ]

Suárez A, Williams-Linera G, Trejo C, Valdez-Hernández JI, Cetina-Alcalá VM, Vibrans H. 2012. Local knowledge helps select species for forest restoration in a tropical dry forest of central Veracruz, Mexico. Agroforestry systems 85: 35-55. DOI: https://doi.org/10.1007/s10457-011-9437-9 [ Links ]

Suding K. 2011. Toward an era of restoration in ecology: successes, failures and opportunities ahead. Annual Review of Ecology, Evolution and Systematics 42: 465-487. DOI: https://doi.org/10.1146/annurev-ecolsys-102710-145115 [ Links ]

Suding K, Higgs E, Palmer M, Callicott JB, Anderson CB, Baker M, Gutrich JJ, Hondula KL, LaFevor MC, Larson BMH, Randall A, Ruhl JB, Schwartz KZS. 2015. Committing to ecological restoration. Science 348: 638-640. DOI: https://doi.org/10.1126/science.aaa4216 [ Links ]

Toledo VM. 1987. La etnobotánica en Latinoamérica. Vicisitudes, contextos, desafíos. Memorias del IV Congreso Latinoaméricano de Botánica. Simposio de etnobotánica: perspectivas en Latinoamérica. Medellín, Colombia. [ Links ]

Toledo VM, Batis AI, Becerra R, Esteban M, Ramos CH. 1992. Products from the tropical rain forests of Mexico: an ethnoecological approach. In: Plotkin M, Famolare L, eds. Sustainable Harvest and Marketing of Rain Forest Products, 99-109. Island Press, Washington, DC. ISBN-10: 1559631686; 978-1559631686 [ Links ]

Toledo VM, Batis AI, Becerra R, Martínez E, Ramos HC. 1995. La Selva útil: Etnobotánica cuantitativa de los grupos indígenas del Trópico húmedo de México. Interciencia 20: 177-187. [ Links ]

Toscano GJY. 2006. Uso tradicional de plantas medicinales en la vereda San Isidro, Municipio de San José de Pare-Boyacá: Un estudio preliminar usando técnicas cuantitativas. Acta Biológica Colombiana 11: 137-146. [ Links ]

Tudela F. 1989. La modernización forzada del trópico: El caso de Tabasco. Proyecto integrado del Golfo. El Colegio de México. ISBN: 968120419 0 [ Links ]

Turner NJ. 1988. “The importance of a rose”: Evaluating the cultural significance of plants in Thompson and Lillooet interior Salish. American Anthropologist 90: 272-290. DOI: https://doi.org/10.1525/aa.1988.90.2.02a00020 [ Links ]

Vandebroek I, Balick MJ. 2012. Globalization and loss of plant Knowledge: challenging the paradigm. Plos One 7: e37643. DOI: https://doi.org/10.1371/journal.pone.0037643 [ Links ]

Vázquez-Yanes C, Batis MAI, Alcocer SMI, Gual DM, Sánchez DC. 1999. Árboles y arbustos nativos potencialmente valiosos para la restauración ecológica y la feforestación. Reporte técnico del proyecto J084. CONABIO-Instituto de Ecología, UNAM, México. [ Links ]

Velázquez-Rosas N, Silva-Rivera E, Ruiz-Guerra B, Armenta-Montero S, Trejo González J. 2018. Traditional Ecological Knowledge as a tool for biocultural landscape restoration in northern Veracruz, Mexico: a case study in El Tajín region. Ecology and Society 23: 6. DOI: https://doi.org/10.5751/ES-10294-230306 [ Links ]

Voeks RA. 1996. Tropical forest healers and habitat preference. Economic Botany 50: 381-400. DOI: https://doi.org/10.1007/BF02866520 [ Links ]

Voeks RA. 2004. Disturbance pharmacopoeias: Medicine and myth from the humid tropics. Annals of the Association of American Geographers 94: 868-888. DOI: https://doi.org/10.1111/j.1467-8306.2004.00439.x [ Links ]

Voeks RA. 2007. A women reservoirs of traditional plant knowledge? Gender, ethnobotany and globalization in northeast Brazil. Singapore Journal of Tropical Geography 28: 7-20. DOI: https://doi.org/10.1111/j.1467-9493.2006.00273.x [ Links ]

Voeks RA, Nyawa S. 2001. Healing flora of the Brunei Dusun. Borneo Research Bulletin 32: 178-195. [ Links ]

Voeks RA, Leony A. 2004. Forgetting the forest: assessing medicinal plant erosion in Eastern Brazil. Economic Botany 58: 294-306. DOI: https://doi.org/10.1663/0013-0001(2004)58[S294:FTFAMP]2.0.CO;2 [ Links ]

Weldegerima B. 2009. Review on the importance of documenting ethnopharmacological information on medicinal plants. African Journal of Pharmacy and Pharmacology 3: 400-403. [ Links ]

WHO [World Health Organization]. 2002. Medicina tradicional: necesidades crecientes y potencial. Ginebra: Organización Mundial de la Salud. < http://www.who.int/iris/handle/10665/67296 > (accessed January 16, 2019). [ Links ]

WHO. 2013. WHO traditional medicine strategy: 2014-2023. World Health Organization. Geneva, Switzerland. < http://apps.who.int/iris/bitstream/10665/92455/1/9789241506090_eng.pdf > (accessed January 16, 2019). [ Links ]

Wuethrich B. 2007. Reconstructing Brazil’s Atlantic rainforest. Science 315: 1070-1072. DOI: https://doi.org/10.1126/science.315.5815.1070 [ Links ]

1Associated editor: Andrea Martínez Ballesté.

Appendix 1

Index of Knowledge Richness (IKR) by age range of women and men in each study community; n= number of interviewees; S = Number of known species; Max.= maximum, Min.= minimum. 

Oxolotán
Women (IKR) Men (IKR)
Age range n Max. IKR SMax Min. IKR SMin n Max. IKR SMax Min. IKR SMin
20-30 0 _ _ _ _ 0 _ _ _ _
31-40 1 0.41 14 _ _ 0 _ _ _ _
41-50 5 0.53 18 0.26 9 0 _ _ _ _
51-60 4 0.41 14 0.18 6 3 0.44 15 0.06 2
61-70 7 0.35 12 0.12 4 0 _ _ _ _
71-80 5 0.62 21 0.29 10 0 _ _ _ _
81-90 2 0.59 20 0.38 13 1 0.32 11 _ _
91-100 0 _ _ _ _ 0 _ _ _ _
No. interviewees (%) 24 (86%) 4 (14 %)

Cerro Blanco Quinta Sección
Women (IKR)
Age range n Max. IKR SMax Min. IKR SMin
20-30 1 0.39 11 _ _
31-40 8 0.50 14 0.11 3
41-50 8 0.57 16 0.18 5
51-60 8 0.54 15 0.29 8
61-70 3 0.39 11 0.21 6
71-80 1 0.43 12 _ _
81-90 _ _ _ _ _
91-100 _ _ _ _ _
No. interviewees (%) 29 (100%)

Tomás Garrido Canabal
Women (IKR) Men (IKR)
Age range n Max. IKR SMax Min. IKR SMin n Max. IKR SMax Min. IKR SMin
20-30 1 0.23 7 _ _ _ _ _ _ _
31-40 3 0.48 15 0.26 8 1 0.42 13 _ _
41-50 5 0.42 13 0.29 9 _ _ _ _ _
51-60 3 0.55 17 0.23 7 3 0.35 11 0.19 6
61-70 4 0.58 18 0.23 7 2 0.45 14 0.35 11
71-80 _ _ _ _ _ 2 0.32 10 0.29 9
81-90 _ _ _ _ _ 1 0.26 8 _ _
91-100 1 0.48 15 _ _ _ _ _ _ _
No. interviewees (%) 17 (65%) 9 (35%)

La Cumbre
Women (IKR) Men (IKR)
Age range n Max. IKR SMax Min. IKR SMin n Max. IKR SMax Min. IKR SMin
20-30 1 0.37 11 _ _ _ _ _ _ _
31-40 1 0.20 6 _ _ 1 0.33 10 _ _
41-50 2 0.53 16 0.27 8 1 0.27 8 _ _
51-60 3 0.30 9 0.17 5 1 0.43 13 _ _
61-70 5 0.53 16 0.13 4 1 0.27 8
71-80 3 0.40 12 0.37 11 3 0.30 9 0.23 7
81-90 _ _ _ _ _ 1 0.27 8 _ _
91-100 1 0.23 7 _ _ _ _ _ _ _
No. interviewees (%) 16 (67%) 8 (33%)

Received: October 20, 2018; Accepted: April 09, 2019

* Corresponding author: Juana García-Flores, e-mail: jgarcia@iies.unam.mx.

Author Contributions: JGF conceived, designed and carried out the fieldwork, drafted and finalized the manuscript. MGE conceived and designed the fieldwork; translated parts of the text, drafted, reviewed and final-edited the manuscript. RLC reviewed drafts of the manuscript. AC conceived and designed the fieldwork, translated, drafted and reviewed the manuscript.

Creative Commons License This is an open-access article distributed under the terms of the Creative Commons Attribution License