Skip to content

Advertisement

  • Research
  • Open Access

Ixcatec ethnoecology: plant management and biocultural heritage in Oaxaca, Mexico

  • 1, 2,
  • 1Email author,
  • 3,
  • 1 and
  • 3
Journal of Ethnobiology and Ethnomedicine201612:30

https://doi.org/10.1186/s13002-016-0101-3

  • Received: 1 March 2016
  • Accepted: 2 July 2016
  • Published:

Abstract

Background

Studying motives of plant management allows understanding processes that originated agriculture and current forms of traditional technology innovation. Our work analyses the role of native plants in the Ixcatec subsistence, management practices, native plants biocultural importance, and motivations influencing management decisions. Cultural and ecological importance and management complexity may differ among species according with their use value and availability. We hypothesized that decreasing risk in availability of resources underlies the main motives of management, but curiosity, aesthetic, and ethical values may also be determinant.

Methods

Role of plants in subsistence strategies, forms of use and management was documented through 130 semi-structured interviews and participant observation. Free listing interviews to 38 people were used to estimate the cognitive importance of species used as food, medicine, fuel, fodder, ornament and ceremonial. Species ecological importance was evaluated through sampling vegetation in 22 points. Principal Components Analysis were performed to explore the relation between management, cultural and ecological importance and estimating the biocultural importance of native species.

Results

We recorded 627 useful plant species, 589 of them native. Livelihood strategies of households rely on agriculture, livestock and multiple use of forest resources. At least 400 species are managed, some of them involving artificial selection. Management complexity is the main factor reflecting the biocultural importance of plant species, and the weight of ecological importance and cultural value varied among use types. Management strategies aim to ensure resources availability, to have them closer, to embellish human spaces or satisfying ethical principles.

Conclusion

Decisions about plants management are influenced by perception of risk to satisfy material needs, but immaterial principles are also important. Studying such relation is crucial for understanding past and present technological innovation processes and understand the complex process of developing biocultural legacy.

Keywords

  • Biocultural heritage
  • Domestication
  • Ethnoecology
  • Tehuacán-Cuicatlán Valley
  • Ixcatec
  • Cultural value
  • Plant management

Background

In most rural areas of Mexico, especially in those inhabited by indigenous peoples, human subsistence patterns generally involve multiple strategies. Agriculture for direct consumption of products is commonly the main activity, complemented by small scale livestock and the use of numerous forest resources destined to direct consumption and commercialization [1]. These activities occur in territories that are settings of multidimensional and complex interrelationships between humans and nature in socio-ecological systems, integrated as totalities with elements and processes mutually influencing their features and changes [2]. Expressions of these interrelationships are management of wild plant and animal species, domesticated organisms and territories of indigenous and local peoples, which constitute part of the biocultural heritage that are created and maintained through long term by the continuous use and management [35]. Management or transformations and decisions made by humans on ecosystems, and on their elements and functions [6], based on TEK are fundamental in the biocultural heritage development process, and constitute a traditional form of facing the uncertainty inherent to complex systems [3, 79].

Management may include a broad spectrum of strategies and interactions for appropriation and maintaining natural resources [6, 10, 11]; collective actions to protect them [12], as well as those directed to recover or restore them [6]. These practices (praxis) are based on TEK about species and ecosystems (corpus) that are in turn strongly linked to beliefs systems (kosmos) [7, 13], which have direct influence on resources and ecosystem management.

Plant management is influenced by ecological and social factors [1417], including the cultural importance of plant species in human life. Some investigations have found positive correlation between cultural and ecological importance, suggesting that most conspicuous plants have more important use values, but numerous examples have been reported contradicting this hypothesis [18, 19]. More informative for constructing ethnobiological theory has been analyzing the complex of the relationships between cultural significance, ecological importance and management complexity. In edible plants, it has been found that species with high cultural value and limited availability are more intensely managed, as a response to the risk in their availability [1417]. However, humans are not only respondents of critical situations. Curiosity, attraction for beauty, experimentation, innovation, among other intentions are part of human nature and should also be taken into account as factors influencing people’s decision to manage organisms [2022].

Understanding the role of plant resources with different use types in human subsistence patterns, how management interactions are, and how are these influenced by social and ecological factors, may help to understand the principles of the construction of management techniques, management systems, how processes of domestication are originated, and how processes of current technical innovations are developed, in order to understand the process of construction of the biocultural heritage [6].

The Tehuacán-Cuicatlán Valley in central Mexico, is an important region of the Mexican biocultural heritage [3], harbouring more than 3,000 species of vascular plant species and human cultures with ancestors nearly 10,000 years old [23, 24]. Currently, the Popolocan, Mazatec, Mixtec, Chinantec, Cuicatec, Ixcatec, Chocho, Náhuatl and Mestizo communities make use of nearly 1,750 plant species, at least 610 of them receiving management practices [11, 25]. These figures make the Tehuacán Valley an ideal setting for studying processes influencing decision, innovation and diffusion of experiences on plant management.

This study was performed in Santa María Ixcatlán, the only town where the Ixcatec currently live in the world. It was directed to document subsistence strategies, plants use and management locally practiced, and the main motives to manage them. Also, we examined how cultural, ecological and management factors interact and determine the importance of native plants with different use type on Ixcatec biocultural heritage.

We analyzed the hypothesis that the main motive of managing plants is decreasing the risk that represent their low availability and in some cases to enhance their abundance and quality. Therefore, subsistence is based on multiple activities, diversified management strategies to prevent risks in staple resources availability; and the high cultural importance and management intensity may be associated with low ecological importance. But, attraction for beauty, curiosity and ethical concerns, beyond the satisfaction of primary needs, should also be important aspects in decisions to manage plant resources.

Methods

Study area

At present, the Ixcatec live only in the community of Santa María Ixcatlán, a town governed by the regime of traditional practices and customs. Land tenure is communal with 41,530 ha [26, 27] belonging to the Tehuacán-Cuicatlán Biosphere Reserve, Mexico (Fig. 1). The whole territory is mountainous, with elevations ranging from 800 to 2600 m. Soils in most of the territory derived from calcareous rocks, with thin layers of black organic soils. The town has temperate climate, with annual mean temperature of 17.2 °C, and annual rainfall averaging 721 mm [28, 29]. The rest of the territory has semiarid climate [29]. Vegetation types are oak forests, tropical dry forest, induced grassland and secondary vegetation [30].
Fig. 1
Fig. 1

Study area. Location of the the community of Santa María Ixcatlán, Oaxaca, in the Biosphere Reserve Tehuacán-Cuicatlán, central México

In Santa María Ixcatlán live 175 households and 516 people [31]. There is a high migration of young people to the cities of Tehuacán, México, Orizaba, and more recently to the US [32]. Local households’ economy is based on direct consumption of agricultural products, livestock raising and use of forest products [32, 33]. The Communitarian Assembly, conformed by all adult men, is the maximum authority [32], and people obtain rights to have access to resources and lands of the territory through a system of charges and cooperation to communitarian activities [32]. Practically all families are Catholic [32], and have a complex calendar of ceremonies [27, 32, 33]. Nearly a dozen of persons are fluently speakers of Ixcatec, an almost extinct language [34, 35].

Flora inventory

We conducted ethnoecological studies in Ixcatlán in the period 1999–2001 and in the period 2011–2015 with 16 campaigns of field work. Trial walks accompanied with local informants were carried out to identify vegetation types [36] and collecting botanical voucher specimens throughout the territory of the community. Voucher specimens were deposited at MEXU, EBUM, IE-BAJÍO and IBUG herbaria with Selene Rangel, Erandi Rivera, and Ricardo collection numbers. Nomenclature and classification of species are presented following the APG III classification system consulted in the site www.theplantlist.org [37].

Interviews

A total of 130 semi-structured interviews to 62 people were conducted to document common names of plants, their use, management practices and motivations to conduct them. Alive plants in their own homegardens, agricultural fields or seen in trial walks, fresh specimens collected a day before, dried specimens and pictures were used as stimulus in these interviews; 22 of the 62 interviewees (9 women and 13 men, with average age of 58.9 years, SD = 22.5) were considered key informants because of their deep knowledge of the territory and plants or because they were Ixcatec speakers. Key informants were selected by the snowball sampling technique, by asking for people with these skills; 15 of them were interviewed from 2 to 11 times in a total of 77 audio or video-recorded sessions, in which on average 17.2 (SD = 23.4) species were reviewed per work session. The other 40 interviewees were considered occasional participants (21 female and 17 male, whose age averaged 53.2 years, SD = 20.8), and they were selected randomly.

More detailed information about informants and activities are included in the Table 6 of Appendix. All interviews used for the analysis showed in this paper were performed in Spanish. All interviews and participant observation data about plant resources use and management were transcribed and systematized into the format of the ethnobotanical data base of Mexico (BADEPLAM) of the Botanical Garden, UNAM. Audio-visual material was stored in the Ixcatec Culture Archive and The Endangered Languages Archive.

Surveys

Semi-structured surveys with questions on agricultural production and consumption of plant resources were conducted in Spanish between 2000 and 2012 to 21 and 20 households representing the 12 % of the households of Ixcatlán in each year (householders averaging 61.2 years old, SD = 17.2). In 2000 households were selected at random, while in 2012, 24 % of the households surveyed in 2000 were selected, and the rest were selected at random.

Free listing

In order to identify the plant species with the higher cognitive importance, in 2013 we used the free listing method [38]. We requested in Spanish to 38 people (22 men and 16 women, aging on average 50.6 years, SD = 18.8) to spontaneously listing the names of plants that grow in the territory of Santa María Ixcatlán that are used: 1) as food, 2) to attend illnesses and take care of health, 3) as firewood, 4) to feed livestock, 5) to offer them to Saints, dead people or used in ceremonies, and 6) to embellish the houses and crop land. Once informants stopped listing plants for one use, we asked them to listing plants for other use, and we continued this procedure until finishing the lists of plants for the six uses. Of the 38 people interviewed, 19 were previous informants (13 considered key informants and 6 occasional informants), the other 19 people interviewed were selected at random. Details on the number of lists per use type, the number of items named, the levels of saturation of the datasets, and information about interviewees can be consulted in the Appendix.

Vegetation sampling

We conducted vegetation samplings in 22 points of nine natural and transformed vegetation types in order to estimate the ecological importance value of species [36]: Quercus liebmanni and Quercus laeta forest (3 points), Quercus urbanni forest (1 point), riparian forest of Taxodium huegelii (1 point), Juniperus flaccida forest (2 points), izotal of Beaucarnea stricta (2 points), mexical (2 points), palm scrubland of Brahea dulcis (2 points), grassland (2 points), and agricultural fields (7 points). At each point we established a 500 m2 quadrant, where all shrubs and trees were counted and their height and two canopy diameters were measured. Herbs were sampled in five subplots (1 m2 each) randomly placed within the area of each 500 m2 quadrant. Density and frequency was calculated for each species. Shrubs and trees biomass was calculated through volume formulas of geometric figures [39]. In addition, the floristic composition was sampled in 17 homegardens.

Data analyses

Livelihood analysis was conducted to assess the subsistence strategies [38], and descriptive data of use and management of plants species were estimated.

Series of Principal Component Analyses (PCA) with native plants species (species with wild populations or Mesoamerican species with naturalized populations in Ixcatlán territory), were performed. Species were considered as operational taxonomic units according to its number of uses, cognitive importance, consumption, ecological importance, complexity of management practices, and management place, all of them aspects involved in the definition of their importance to the biocultural heritage of plant species. The scores of the first principal component obtained in each PCA were considered as biocultural importance index by type of use, since these values are linear combinations that integrating information of the variables, species with positive and highest values were considered more important [15, 40]. The most important variables and how they interact was identified by the correlation values between variables and the first two components [41]. We also identified how species are grouped according with all the variables studied by representing the cloud of species in terms of the two first components [41]. These PCAs were made in JMP 8. statistical software [42].

The cognitive importance was estimated through free listing data with the index of Sutrop (S) with the formula S = F/(N mP), where F represents the frequency of the species, N the total number of interviewed people per use category, and mP is the medium position in which the term or species was named [43]. We calculated this index with the software FLAME v1.0 [44]. A zero value was assigned to all species that were not listed by consultants [43]. When an informant said that he/she does not know any plant for a given use or when he/she said that all plants could be used for the requested use, we excluded the list of the analysis.

The consumption of products was estimated as the percentage of households that consumed each plant species throughout the year, based on data documented with surveys conducted in 2012.

The ecological importance of species was estimated through the ecological importance value index EIVI = (Relative frequency + Relative abundance + Relative biomass)/3, calculated by each plant species per sampled site [45]. The floristic composition of homegardens was similarly used to calculate ecological importance.

The complexity of management practices was calculated by the sum of numerical values of management practices. Values were assigned based on the typology proposed by Blancas et al. [11] as follows: a) gathering, simple or planned extraction strategies = 1; b) tolerance or let standing of plants = 2; c) enhancement by promoting abundance of useful plant species or phenotypes = 3; d) protection of desirable plants = 4; e) transplanting entire individuals = 5; f) propagation as seed sowing and vegetative propagation = 6. In addition, we assigned values of 0.5 to simple foraging by domestic animals, and uproot or deliberate removal individuals of the species in question. Values of each practices was summarized per plant species. The places of management were categorized in natural populations plants distribution sites (in situ = 1) and sites out of their natural distribution (ex situ = 2) [15, 16].

Results

Subsistence strategies

Households are basic units making decisions on economic activities and forest resource management (Fig. 2). Agriculture is the main activity of all households, but maize and beans produced are insufficient to satisfy their annual requirements (Table 1). Multiple-cropping agriculture in the rainy season is carried out in terrains of 1 to 2 ha located around the town (95 % of households), and in homegardens (0.25 to 0.5 ha, managed by 30 % of households) (Figs. 1, 3 and 4). Prayers and rituals drawing or putting crosses made with plants, offering alcoholic beverages to the earth, among other practices, are common during agricultural labours, seed selection and storage, sowing and harvest, as individual farmer or collective petitions for a good rainy season.
Fig. 2
Fig. 2

General pattern of multiple use strategy of natural resources for subsistence in the community of Santa María Ixcatlán

Table 1

Average and standard deviation of the amounts of maize and beans consumed, produced and productivity (kg/ha) achieved by people of Santa María Ixcatlán, Oaxaca for the periods of the years 1999-2000 and 2011-2012

 

Maize

 

Bean

 
 

1999–2000

2011–2012

1999–2000

2011–2012

Consumption per year (kg)

766.38 ± 94.34

701.7 ± 73.6

155.6 ± 19.4

112.2 ± 23

Production by household (kg)

285.5 ± 79.9

129.7 ± 62.6

76.2 ± 26.9

48 ± 18.6

Productivity (kg/ha)

289 ± 70.5

82.1 ± 46.7

43.9 ± 10

28.6 ± 9.4

Community deficit (T)

82.7

100

13.7

11.2

Data according to surveys realized to 21 households in 2000 and 20 households in 2012. Values are means and standard errors

Fig. 3
Fig. 3

Characteristics of landscapes, general environmental units recognized by people in the territory of Santa María Ixcatlán and plant resources use

Fig. 4
Fig. 4

View of environmental units. a) Quercus liebmanni and Quercus laeta forest; b) Dam “La Laguna”, grassland and oak forest remnant; c) Homegardens, agricultural fields, palm scrublands and mexical in the southwest side of town; d) View of a homegarden and a traditional house with roof of palm leaves; e) Pseudomytrocereus fulviceps shrubland; f) Tillansia grandis and Agave potatorum in Cephalocereus colummna-trajanni shrubland

All people interviewed referred to difficulties in agriculture, mainly due to a low soil fertility and water scarcity. However, people deal with these problems in homegardens and agricultural fields by adding domestic animals manure, oak forest humus, ash, firewood debris and organic waste; agrochemicals are not used at all. In homegardens, recycling water and spatial arrangement of plants according with their water requirements are common. In agricultural fields, terraces and live fences are common for preventing soil erosion, as well as some dams for the accumulation of soil and moisture (Fig. 4).

Animal husbandry is practiced by almost all households as a saving for emergencies, animal power for agricultural and for gathering activities, only 5 % of households commercialize animals in regional markets (Fig. 2). Nearly 55 % of households raise animals in backyards (1–7 chickens, 1–9 turkeys or 1–4 pigs), 75 % nurture draft animals (1–5 donkeys-mules or 1–4 horses), and 25 % raise livestock (5–80 cows, 10–16 sheeps or 5–70 goats) (Fig. 2). Animals feeding bases on domestic sub-products, maize straw, herbs managed in homegardens and agricultural fields, and foraging in communal lands (Figs. 3 and 4).

Gathering and management of native and introduced plants for direct consumption is practiced by all households (Figs. 2 and 3). Plants provide all the firewood and fodder needed and great part of food, medicines, materials for construction, tools, and other goods. Other important plants are ceremonial and ornamental, which are gathered and managed for direct use or as gifts to relatives (Fig. 2).

Few plant resources or their products are destined to economic interchange, the most important are Brahea dulcis and Agave potatorum (Fig. 2). The weaving of hats with Brahea dulcis leaves is carried out by nearly 84 % of the households, while 10 % are specialized in handcrafting baskets, covers for bottles and other products. Hats are interchanged almost every day for maize, food or money in local stores. From 2011 to 2015 the price of each hat was 0.16 US dollars (based on an interchange rate of $20.00 Mexican pesos by one American dollar), while in 2000 it was $0.12. A household weave on average 28.9 ± 3.65 hats per week, and each hat requires 4.1 young leaves, which means approximately one million of leaves used in the whole community per year. Leaves extraction is carried out mainly in palm scrublands, where Brahea dulcis is promoted, protected and tolerated in areas of agricultural fields, but it is widely distributed throughout the whole territory (Figs. 3 and 4). For extracting palm leaves, people cut the young leaves without damaging the apical meristem and avoid gathering leaves during the new moon, otherwise they consider the growth of new leaves can be delayed. Harvesting palm leaves for direct use and local interchange is allowed but sale to regional sellers is forbidden. Palm is considered staple plant as people said “palms are our life because with palm leaves we make hats and we can get all we need to live”.

Approximately 20 % of households prepare mescal with Agave potatorum once to 10 times per year (4.8 ± 1.49) (Fig. 2). For 2012 we estimated that the whole community produced 192 mescal batches, using 91.14 ± 9.78 agaves per batch, in total nearly 17,500 agaves per year, whereas for the year 2000 we estimated the use of 4,900 individuals. The price of one litre of mescal was $2.5 US dollars in 2000 and from $6 to $9 in 2011 to 2015. Although Agave potatorum is widely distributed in temperate and warm parts of the territory of the community (Figs. 3 and 4), the mescal producers said that they have to go progressively farer to extract agaves and they even complement their needs buying agaves to neighbouring communities; sometimes they complement their batches with the wild Agave vivipara extracted in the warm land of the territory. Agave extraction is allowed for all community members; however, the relation between mescal producers and communal authorities has become tense in the last years, since federal environmental authorities are trying to regulate this activity in the region. Since 2011 some mescal producers started to enhance the availability of agaves near their houses or agricultural fields by spreading seeds or cultivating them in homegardens and green houses. Some mescal producers have participated in exchanges of experiences for agave management with other communities, and governmental programs have promoted some actions as reforestations and the construction of a communitarian greenhouse that stared to produce agave plants in 2015.

The activities described are supported by using different environments and sites of the territory (Figs. 3 and 4). The whole territory is of common use, but knowledge about distribution, abundance and quality of plant resources are recognized as basic issues to access to any locality and its resources. The subsistence strategy is complemented by economic subsidies from governmental programs for elderly, child scholarships, creole seeds conservation, and agriculture and stockbreeding development (Fig. 2). In 2000 assistance program started to support the 45 % of households, by 2012 nearly 95 % of the households received monetary incomes from those programs. In almost a half of the households at least one member has temporal or occasional employments at town that allow them to get additional monetary incomes (Fig. 2). Although irregularly, some migrants support their families to pay communal fees for celebrations, maintaining religious monuments and building public infrastructure (Fig. 2).

Plants use

We inventoried 780 vascular plants species belonging to 119 botanical families; 589 of them are native to Ixcatlán, and the other 191 have been introduced from other parts of Mexico and the world (Appendix). In order to satisfy their broad spectrum of needs people make use of 627 plants species with one to 27 use categories (Table 2), 267 species have one use and 360 have between 2 and 11 different use types.
Table 2

Use categories of Santa María Ixcatlán plant species. Data according to 62 people interviewed in 130 work sessions

Use

Native

Introduced

Total

Fodder

238

30

268

Ornamental

160

110

270a

Medicinal

166

53

219

Edible

72

66

138

Ceremonial

73

55

128

Firewood

44

2

46

Utensils

29

4

33

Living fences

24

6

30

Timber products and construction

27

2

29

Shade

12

11

23

Food aditive (flavor)

9

6

15

Handcrafts

11

1

11

Insects repellent

8

0

8

Soil control

6

2

8

Animals medicine

1

1

6

Facilitatorb

3

2

5

Toys

5

5

5

Alcoholic beverages

2

1

3

Cosmetic

2

1

3

Soap

2

1

3

Paint

3

0

3

Weather predictors

2

0

2

Aromatizing

1

0

1

Tannin source

1

0

1

Water attracter

1

0

1

Glues

1

0

1

Poisons

1

0

1

Unknown

150

3

153

TOTAL

589

191

780

a = 132 species are considered “luxury of houses”, 80 as “luxury of the mountain”, and 59 as “luxury of houses and mountain”; b = Plants used as stake, hosts and nurse plant

Fodder

A total of 268 plant species are consumed by domestic animals (Table 2, Appendix). 238 species being native to Ixcatlán and 165 of them have other uses mainly as edible, medicinal or as ornamental plants. Of the 30 introduced species 15 are propagated, and some of them are highly valued (Appendix). Zea mays is the most valuable specie as fodder, its stubble is used by the 80 % of households and during periods of scarcity, 87 % of the households have to buy it to regional sellers (Fig. 2, Appendix). Other important introduced plants are Avena fatua and Hordeum vulgare which are cultivated specifically for this use.

Ornamental

Ixcatlán people name as “luxury” (‘lujo’ in Spanish) the plant species that embellish or adornment houses, homegardens, agricultural fields and landscapes, in the two last cases these plants are called “mountain luxury”. High variation was documented about which plants are considered as luxury, as most consultants said “it is something that depends on the appreciation of beauty of things by each person”. People consider that luxury plants embellish the house, calls friendship, invites people to come into the house, allows to strength the heart or spirit and it is motive of proud for the owner. The importance of maintaining these plants varies among people, but generally are appreciated because in addition to the quality of embellish, these plants provide shade, good sites for resting and well-being or are used as fodder, edible and medicine. Nearly 270 species were recognized for its quality of embellish, 160 of them are native to Ixcatlán, 37 of them are not used in other form. 19 luxury plant species are transplanted from forest to houses or are propagated through sexual or asexual propagules. Introduced plants are highly valued (Table 2, Appendix), and are common gift of outsiders that visit the town, or these are obtained through governmental programs or by interchanging palm leaves with outside sellers.

Medicinal

We documented 219 species used as medicine (Table 2), 61 of them exclusively used with this purpose, the rest have other uses mainly fodder, edible or are considered as “luxury plants". The medicinal plants commonly are used to treat stomach-ache, cold, fever, ear pain, sprains, and cultural illnesses like “sustos” (shocks caused by impressions), “aires” (malaise caused by uncomfortable situations) and “alferecia” (weakness, loss of appetite and irritability in children). Although knowledge about plants used in childbirth is extensive, few young women recognize to use them. In 2000, all people said to use medicinal plants, but in 2012, 15 % of people interviewed said they only use allopathic therapies and the rest said to combine traditional and institutional medicine. Of the 53 introduced species some are highly valued for their medicinal use (Table 2, Appendix) and are cultivated to have them available as it is the cases of Matricaria chamomilla, Tanacetum parthenium and Artemisia ludoviciana.

Edible

We documented 138 plant species used as food, 99 of them have other uses, mainly as fodder, medicinal and ornamental (Appendix, Table 2). Nearly 50 species complement the diet of people which is based on maize tortillas, beans and chili sauces; 66 introduced edible species are cultivated, as it is the cases of maize, beans, vegetables, condiments and fruits (Appendix). These plants are available in the local stores but people say “the little that we harvest is a saving, these plants are things that we do not have to buy”. Other reasons for cultivating are quality; people argued that vegetables locally produced are of better quality than others from outside particularly Coriandrum sativum and Solanum lycopersicum, they consider that local products have better taste, smell and texture.

Ceremonial

A total of 128 plant species are used to offer them to Catholic Saints in altars at homes, hermitages, thumbs, and the church. Some are used in ceremonies and processions (Table 2, Appendix); 117of them have other uses, 95 are used as ornamental or luxury (Table 2). The introduced plants are highly appreciated (Appendix), and particularly cultivated for their flowers, like Tagetes erecta used by 95 % of households during the great feast of the Day of the Dead (Appendix). People recognize several varieties according to the size, colour and form of flowers, and it is common to store seeds of their favourite variants to be propagated in the next cycle. Local interchange of ceremonial plants flowers is common among households as gifts or trade, especially of introduced species as Tagetes erecta, Zantedeschia aethiopica, Leucanthemum maximum, between others.

Firewood

We recorded 48 species used as firewood (Table 2), 44 of them are native species, and 46 have other uses. These are the main source of cooking energy (only 35 % of households have gas stoves, but all use firewood for cook “maize tortillas”), and is the unique fuel to mescal production and for baking bread. In the year 2000, consumption of firewood per household was of 143.4 ± 11.3 kg/week, and in 2012 it was 108.8 ± 12 kg/week, a decrease apparently due to a governmental program for installing efficient stoves. For mescal production the consumption increased from 16.2 ton in 2000 to 63.36 ton in 2012; nearly 52 % of these quantities is from alive oaks, which is considered the appropriate wood for baking the agave stems in the process of mescal production.

Plant management

Nearly 82 % of all plants species recorded (636 spp.) are recognized to be under interventions by humans or foraged by domestic animals (Appendix); 424 of them are managed through at least two different practice types and 401 species are under practices directed to maintain or increase their availability.

Gathering is the most common practice for obtaining products of native plants and it is the only practice for 83 species (Table 3). This practice was documented among wild and introduced species, some of which have become naturalized (Appendix). We recorded 251 native and introduced species having special protection (Table 3). In homegardens and agricultural fields protection comprises actions like irrigation, exclusion from herbivorous and competitors, nursing, adding of livestock manure, protection against frost, weeding, pruning, and providing or removing shade. In communal lands, protection of native plants is conducted by avoiding pastoral routes in sites where people know valuable plants occur. Also, the Communitarian Assembly construct regulations for protecting some species, based on principles of favoring direct consumption by local people, forbidding extraction for commercialization and cutting of alive trees. However these regulations as practices directed to prevent unnecessary damage not always are followed.
Table 3

Plants management practices realized substitute "realized" by "carried out" in Santa María Ixcatlán

Management practice

Native

Introduced

Total

Gathering

281

18

299

Foraging

223

20

243

Tolerance

152

54

206

Protection

91

160

251

Trasplanting

71

68

139

Uproot

63

13

76

Propagation

33

122

155

Enhancement

9

25

34

Unknown

143

1

144

Data according to 62 people interviewed in 130 work sessions

In total, 206 species are tolerated during clearing vegetation in homegardens and agricultural fields. The main reason is its utility, but 23 species that are not used are tolerated since people said that “plants could be useful in the future”, and “do not interfere with the development of other plants” or because “plants have the right to live” and “are part of nature”.

Propagation of 155 species is carried out by seeds, bulbs, corms, rhizomes, tubers, pseudo-bulbs, bulbils, plantlets, shoots, cladodes and sticks; 33 of them are native wild species used mainly as ornamental. Complete individuals of 139 species are transplanted, 71 of them from wild populations in forests to homegardens and agricultural fields. Occasionally, some epiphytic bromeliads and orchid species are relocated from one branch or tree to other, when their host’s branches are cutting to allow their survival.

The abundance of 26 species or some variants is promoted by tolerating them until seed production, and in some cases seeds are collected, stored and then sown or dispersed; 76 species (63 of them native) are constantly uprooted in agricultural fields and homegardens (Table 3), some of them are also under practices to maintain them and ensure their availability.

Biocultural importance

Fodder

Variation in biocultural importance of 238 fodder native species is mainly explained by management type and number of uses (38 % of variation in the first principal component), and cognitive prominence and consumption (22 % of variation in the second principal component; Table 4). Species with the highest biocultural importance (blue circle in Fig. 5a) are subject to several management practices, but its use as fodder is low with the exception of Quercus liebmani whose acorns are gathered and stored for feeding pigs, and inflorescences of Agave spp. that are occasionally consumed by cattle. Simsia lagascaeformis and Tithonia tubaeformis (pink circle in Fig. 5a) are the species with highest cognitive value, and are tolerated in homegardens or agricultural fields, where these are also uprooted to control their abundance. Similar situation occurs with Amaranthus hybridus, Mirabilis xalapa, Sicyos laciniatus and grass species (green circle in Fig. 5a).
Table 4

Contribution of socio-ecological factors to explain the variation of native plant species biocultural importance

Use type

Fodder

Ornamental

Medicinal

Edible

Ceremonial

Firewood

Factor

PC1

PC2

PC1

PC2

PC1

PC2

PC1

PC2

PC1

PC2

PC1

PC2

Cognitive importance

−0.09

0.78

0.55

0.31

0.72

−0.58

0.44

−0.18

0.54

0.24

0.69

−0.17

Consump-tion

0.04

0.77

0.55

0.12

0.63

−0.64

0.39

−0.32

0.35

−0.63

0.33

0.67

Number of uses

0.76

0.16

0.74

0.47

0.52

0.69

0.47

0.73

0.65

0.61

0.75

0.29

Ecological importance

0.48

0.21

0.53

0.52

0.31

0.65

0.32

0.82

0.51

0.68

0.61

0.57

Management complexity

0.93

−0.01

0.81

−0.52

0.82

0.33

0.93

−0.13

0.89

−0.29

0.9

−0.24

Management site

0.76

−0.22

0.59

−0.76

0.8

−0.01

0.78

−0.36

0.69

−0.58

0.69

−0.66

Data are correlation values between variables and the first two components of Principal Components Analysis PCAs. Values in bold have high influence in principal components, therefore in the classification of biocultural importance too

Fig. 5
Fig. 5

Spatial arrangement of species used as a) edible, b) medicinal, c) firewood, d) fodder, e) ceremonial and f) ornamental, according to the Principal Component Analysis PCA performed with cultural, ecological and management variables. 11 = Agave potatorum, 12 = Agave salmiana subsp. tehuacanensis, 30 = Amaranthus hybridus, 68 = Brahea dulcis, 88 = Ageratina mairetiana, 127 = Grindelia inuloides, 151 = Porophyllum linaria, 152 = Porophyllum ruderale, 159 = Simsia lagascaeformis, 177 = Tithonia tubaeformis, 255 = Bursera biflora, 238 = Hechtia oaxacana,237 = Catopsis compacta, 247 = Tillandsia usneoides, 325 = Sedum dendroideum, 278 = Opuntia lasiacantha, 296 = Dysphania ambrosioides, 343 = Juniperus flaccida, 384 = Quercus acutifolia, 388 = Quercus laeta, 389 = Quercus liebmannii, 392 = Quercus urbanii, 413 = Clinopodium mexicanum, 533 = Anoda cristata, 549 = Morus celtidifolia, 554 = Dasylirion serratifolium, 579 = Laelia albida, 580 = Laelia anceps, 584 = Euchile karwinskii, 601 = Peperomia quadrifolia, 682 = Lindleya mespiliodes, 692 = Chiococca alba, 722 = Lamourouxia dasyantha, 734 = Capsicum annuum, 743 = Physalis philadelphica, 761 = Turnera difussa, 775 = Lippia oaxacana. For all species identity see ID correspondence on Table 5 of Appendix

Legumes, oak acorns, herb species and grasses are the main fodder for cattle, goats and sheep. Management practices to ensure their availability are poor or absent (orange and brown circles in Fig. 5a). Tillandsia gymnobotrya and Hechtia oaxacana are highly valued as fodder, substituting maize stubble (green circle in Fig. 5a). Shepherds drop the epiphytic plants for cattle and goats, and nearly 30 % of households gather and carry them to town for feeding donkeys and horses, extracting 800 to 1920 individuals per year.

Ornamental plants

Biocultural importance of 160 native ornamental plants is explained mainly by their management complexity and number of uses (40 % of the variation explained by the first principal component), and ecological importance and management (25 % of variation explained by the second principal component) (Table 4). The most important plant species (Brahea dulcis, Juniperus flaccida, Quercus liebmanni, Morus celtidifolia and Agave potatorum), with exception of Morus celtidifolia are considered “luxury of the mountain”, all of them are highly valued because of their multiple uses, and have high ecological importance (blue circle in Fig. 5b).

Oaks, grasses and numerous plant species producing beautiful flowers are appreciated to embellish the wilderness and some of them are maintained for this appraisal on agricultural fields or protected against livestock, as it is the case of the terrestrial orchids (Cyrtopodium macrobulbon and Govenia lagenophora), among others (brown circle in Fig. 5b).

Some valuable “luxury of the mountain” plants, are carried to homegardens; for instance, Euchile karwinskii, several spherical and barrel cacti species (Mammillaria spp., Coryphantha retusa, and Ferocactus spp.), Crassulaceae species, Tillandsia spp., among others. These plants are propagated and maintained for embellishing the house and 42 species are used for ceremonial purposes too (green circle in Fig. 5b).

Medicinal plants

The biocultural importance of the 166 native medicinal plant species is explained mainly by their complexity and site of management, and their cognitive prominence in the first principal component (43 % of variation). Number of uses, ecological importance, consumption and cognitive importance are important in the second principal component (29 % of variation) (Table 4). In general, native plants with the highest biocultural importance like Lippia oaxacana, Ageratina mairetiana, Grindelia inuloides and Clinopodium mexicanum have few uses, high cognitive prominence and low ecological importance (orange circle in Fig. 5c). These plants are mainly gathered and stored to ensure their availability when it could be necessary. Some people have propagated these plants but said that “they are experimenting” but “quality of plants growing in nature is better than the cultivated ones”.

There is another group of plants like Agave spp., Juniperus flaccida and Brahea dulcis, which have high ecological importance, are subject to complex management and used with numerous purposes, and occasionally used as medicine (blue circle in Fig. 5c). The rest of the species (green circle in Fig. 5c) are occasionally consumed, collected when they are needed, and some of them are also valued for other types of use.

Edible

Principal components analysis shows that biocultural importance of the 72 native plants is explained mainly by management practices complexity and management site (ex situ or in situ) in the first principal component (36 % of variation), and ecological importance and number of uses in the second principal component (25 % of variation) (Table 4). Native plants with higher biocultural importance are those with greater management complexity, consumed by more families and have few uses, regardless of their ecological importance (brown circle in Fig. 5d).

One of the most important plant species is Capsicum annuum, consumed by all households, mainly getting it by interchange, but it is also cultivated in homegardens but the wild variety is rarely gathered. Species like Porophyllum ruderale, Porophyllum linaria, Amaranthus hybridus, Opuntia lasiacantha, and Dysphania ambrosiodes are consumed by nearly all households and their contribution to diet is greatly important. For instance, the green Amaranthus hybridus is consumed on average 14.4 ± 2.4 times per year from June to September, almost always together with Porophyllum linaria; Dysphania ambrosiodes is cooked with beans and consumed every day by all households. These species are subject to management in agricultural fields and cultivated in homegardens to ensure their availability and to have them close and in case of scarcity are getting in the stores. Physalis philadelphica is consumed in sauces almost always raw to allow its seeds to germinate after dispersed when washing dishes in homegardens, where plants of this species are tolerated, transplanted and protected.

Other species are obtained by gathering (blue circle in Fig. 5d). Some of the most valuable (e. g. Dasylirion serratifolium and Peperomia cuadrifolia) are consumed by nearly all households and commonly are shared with relatives, especially elders who are unable to get them by themselves. Some people have tried to propagate them in homegardens but they said that their experiments were unsuccessful because they obtain low production, it was difficult to maintain them, and require long time to harvest their products. Agave species are grouped (green circle in Fig. 5d), have high biocultural values, are intensely managed, abundant and highly valued for multiple purposes, although the consumption of its flowers as food is currently uncommon.

Ceremonial plants

Variation in biocultural importance of the 73 native species is mainly explained by management complexity and number of uses in the first principal component (40 % of variation), ecological importance, consumption and number of uses (28 % of variation explained by the second principal component; Table 4). The species with the highest biocultural value were those more intensely managed and valued for other uses (orange circles in Fig. 5e), for instance oaks that are part of the game of “El palo” played in the celebration of the Day of the Dead, when teams of young men go to the forest to cut whole dead trees and carry them on to the town to be fired in front of the church. Other examples are Brahea dulcis leaves, which are used to weave shoes for deceased people and Juniperus flaccida whose resin is used when Bursera resin is scarce or unavailable.

The most cognitively salient species are appreciated for their flowers smell and beauty (green circle in Fig. 5e), which receive management practices and are extensively used regardless of their low ecological importance. In the extraction of orchid flowers people take care of leaving some bulbs, and after their ceremonial use, their bulbils are transplanted in homegradens as it occurs in the case of Euchile karwinskii. Laelia albida is cultivated in 65 % of homegardens and Laelia anceps in 35 % of them, this management is motivated by the appreciation of their beauty and scarcity in forests. Resin of Bursera biflora is particularly appreciated and used in a high number of rituals, this tree species is protected in situ, cannot be tamed or even damaged for extracting its resin and most people use only the resin of those trees naturally injured by insects located in warm lands to assure the resin quality (Fig. 3). Other species like Chiococca alba, Rhynchostele maculata and Epidendrum radioferens are highly valued and frequently used species but rarely transplanted into homegardens, in part because people consider they are abundant, but in part because of the difficulties for their propagation. Some species are used to embellish the “Nativity scenes” (Mammilaria spp., Catopsis compacta, Tillandsia spp.) are transplanted in homegardens after their use (brown circle in Fig. 5e). Most of ceremonial species are only gathered as it is the case of Lamourouxia dasyantha (blue circle in Fig. 5e) and in many cases are shared with relatives, especially old people.

Firewood

Principal components analysis shows that biocultural importance of plants used as firewood is mainly explained by the complexity of their management in the first principal component (47 % of variation), and consumption and ecological importance in the second component (23 % of variation) (Table 4). Species used as firewood with the highest biocultural importance are oaks Quercus spp. (orange circle in Fig. 5f), which are consumed by all households, and have the highest cognitive prominence. Oaks are tolerated and protected in agricultural fields, and sometimes people transplanted and take care of them in their houses as ornamental plants. In this group, Agave salmiana subsp. tehuacanensis is valued as good firewood, but its use is uncommon since people prefer to use its dry stalk for house construction. Two important species used as firewood are Brahea dulcis and Juniperus flaccida, which are intensely managed in agricultural fields and homegardens, have high ecological importance, are frequently used, and are highly culturally valued because of their multiple uses (brown circle in Fig. 5f).

The remaining species receive poor management (green and blue circles in Fig. 5f) and differ in their consumption, cognitive prominence and ecological importance. Some of these species have high biocultural value (Quercus urbanii, Quercus castanea, Quercus conspersa, Rhus chondroloma, Rhus standleyi, and Morus celtidifolia; green circle in Fig. 5f).

Although of the most valuable species for all interviewees are Quercus spp., Arbutus xalapensis and Juniperus flaccida, the “charges” (measurement unit which is the amount of material that a donkey is able to carry) composition highly varied among households, oaks being on average \( \left(\overline{\mathrm{X}}=79\kern0.5em \%\right) \), the rest are at least 30 species of shrubs managed in agricultural fields and homegardens being Dodonaea viscosa, Acacia spp., Comarostaphylis polyfolia, Eysenhardtia polystachya, and Garrya ovata, among the most common species.

Discussion and conclusions

Subsistence strategy

The multiple use of resources that including a great variety of ecosystems and resources and characterizing the Ixcatec subsistence are expressions of common patterns of interactions between humans and plants found among indigenous peoples of Mesoamerica [1, 3, 39, 4649]. Such pattern is particularly important in a region like the Tehuacan Valley where the scarcity and uncertainty of rainfall and agricultural yield are also characteristic [17, 33, 39, 50]. Interchange of natural resources in the regional markets for obtaining staple food and other goods is clearly a strategy to face problems of availability of resources since pre-Columbian times [51]. For instance, commercialization and barter of local products like palm leaves, hats, mescal, and domestic animals, is a common strategy in numerous Mesoamerican communities [5254] and many rural regions in the world to deal with the uncertainty [55].

Other activities like commerce and income subsidized by governmental programs, are part of the process of adaptation that may contribute to face eventual environmental and social adversities, similarly as recently documented among Mayan communities in southern Mexico [53]. The assistance support programmes from Government are progressively more important in the local subsistence strategies, but also, these programmes represent risks for the systems of management of natural resources, as it has been documented for programmes supporting agriculture, which promote the removal of trees and shrubs in agricultural land, thus affecting the maintenance of agroforestry systems [8, 21]. Seasonal employments allow solving some problems [17], but also these may cause the regardless or abandonment of traditional activities, the loss of TEK and, in some cases, the abandonment of the community.

Management diversity

The widely management practices set and other cultural and social strategies documented have allowed to maintain plant species that sustain the multiuse subsistence strategies as it has been reported at regional level [11, 56, 57]

At regional level, gathering and foraging of plant resources by humans and their domestic animals are the most common and simple form of interaction between social and ecological systems [56], but for most useful species recorded people carry out practices directed to maintain and ensure their future availability [11], and a broad variety of strategies are being carried out for such a purpose [17]. These general trends were observed in Santa María Ixcatlán, is practiced in an even higher percentage of plant species (nearly 65 %), which is an expression of the particularly deep of TEK developed by the Ixcatec.

Management practices such as tolerance, enhancing, protection and cultivation (by sowing, planting or transplanting) look for ensuring availability of plant resources and controlling its uncertainty, are primary mechanism in the domestication process for some species [10, 58]. It has allowed through selection of particular individual (phenotypes) and germplasm to start cultivation, maintaining and continuing processes of domestication. These processes were evident in the staple crops, as well as in wild and semi-domesticated Physalis philadelphica, Tagetes erecta and Cosmos bipinnatus in which selection to satisfy particular flavours, colours, and size, among others characteristics is carried out by people.

The socio-cultural strategies documented in all types of use as it is the mobility in resource gathering of valuable species, the diversification of resources to satisfy a need, and the substitution of one species with another or with other materials, have been recognized as buffer mechanisms to uncertainty [17, 59]. Other important strategies based on social interactions as was the interchange of plants as gifts and interchange of information about management techniques, allow important diffusion of experiences among households and communities and are important mechanisms of social cohesion, an important issue to maintain traditional institutions [17, 60]. Strategies associated to governance as it is the case of regulations are being effective for conserving some species. This is for instance the case of Litsea glaucescens and several oak species Quercus spp., whose populations are conserved in Ixcatlán through local regulations that only allow the extraction for direct consumption by househlds, but in other villages of the region have been severely affected and became extinct [15, 16]. However, in other species regulations have been ineffective for controlling new intensities of extraction required because of socio-economic needs. This is clearly the case of Agave potatorum in which the increasing demand of mescal has been for the moment higher than the capacity for collective regulations and technical responses.

Other interactions like removal (uprooting), opposed to maintenance, shows the complexity of interactions between humans and plants and the importance of detailed knowledge that people may have to take into account to make a decision based in the balance of the negative effects and utility that these species could provide [15]. For instance, in some cases like Thitonia tubaeiformis, Amaranthus hybridus and other weeds, which are valuable plants, people control its abundance inside of the agricultural field at begging the cycle in order to prevent competition with maize, but at the same time protect them in the borders to prevent fodder scarcity just in case that maize straw become scarce or to ensure the availability of greens.

The management practices have involved the transformation of ecosystems through intentional or incidental changes in the composition and structure of vegetation, the modification of relief, hydrological systems and biogeochemical processes in soils [61]. Concrete examples of this process are the creation and maintaining of secondary vegetation as induced grasslands and palm scrubland, changes in vegetation structure in forest zones where grazing routes are, erosive process in current and abandoned agricultural fields, and engineering works to retain soil and water for agriculture and livestock (Figs. 1, 2 and 3). Homegardens, crop fields and pasturelands distributed in the three types of environments recognized by the Ixcatec within their territory (Fig. 3), have originated a great variety of landscape units where management of wild and domesticated plant species take place, conforming forest, agroforestry, agro-silvo pastoral, and silvo-pastoral systems [62, 63]. In these systems people maintain a high level of biodiversity; for instance, on average people of Ixcatlán maintain 29 woody native species in their agricultural plots [22]. These systems are biocultural expressions and areas continually generating new biocultural diversity through also continual observation and experimenting management techniques [8, 64]. In the palm scrublands, for instance, which are highly important for the Ixcatec, people have shaped their conformation managing Brahea dulcis in order to increase its availability in agricultural and fallow plots, as well as in homegardens. This practice has happened most probably since pre-Columbian times, since this species is important for Ixcatec people [51, 52].

The role of plant species in the Ixcatec subsistence and in the interactions of humans to conserve plant resources may define particularities of their own culture [3, 65]. Management of some plant species is closely related with the form of preparation of food stoves, as it was described for Physalis philadelphica. Relation of the Ixcatec with the palm Brahea dulcis is particularly significant, this species is part of almost all activities in their daily life, and it has been considered as an indissoluble element of Ixcatec culture [32, 33, 51, 52, 66, 67].

The high levels of diversity and interactions documented in Ixcatlán compared with the regional flora (30 % of the total regional flora, 36 % of all useful plants recorded in the region, and 66 % of managed species identified in the Tehuacán Valley) [11, 24, 25], confirm the importance of the Ixcatec biocultural heritage and the character of the Tehuacan Valley as a priority biocultural region of Mexico [3].

Our research and sampling effort is one of the highest carried out by ethnoecological studies in the Tehuacán Valley [11, 1517, 56, 6871]. This fact confirms that it is still needed continuing efforts to documenting TEK, biocultural processes of diversification and their connection with management innovation and domestication. In this region, archaeological records in caves has been source of information about biocultural construction since prehistory, whereas local studies should continue documenting one of the areas with highest richness of ethnobotanical knowledge of Mexico and a place where ongoing processes for sustainable resource management and local processes of domestication are taking place.

Biocultural importance

The integration of socio-cultural and ecological variables for understanding the importance of plant species, follows the proposal by Castaneda and Stepp [72] for estimating ethnoecological importance. Our evaluation found that variables associated to management complexity are in general those more contributing to explain the variation in the first principal component of the six use categories analysed. This fact suggests that management is representative of the socio-ecological factors interacting and mutually influencing their properties [73]. In other words, studying management of natural resources is a good methodological basis for understanding socio-ecological systems and construction of biocultural heritage.

Brahea dulcis, Juniperus flaccida, and Agave salmiana subsp. tehuacanensis have particularly high biocultural importance values in almost all use types analysed. This fact is because of their multipurpose use, their cultural and ecological importance and their intensive management. The positive relation between cultural and ecological importance might be explained through the hypothesis of ecological appearance [18, 74, 75], but we rather propose that the ecological importance currently observed is in part a result of ancient ecosystem management directed to increase their availability. The high resistance to disturbance, reproductive capacity of these species, among other ecological factors have favoured the enhancing of their abundance.

The relation between ecological and cultural importance varied in the different use types analysed. Among plants used as ceremonial and medicinal, the species with higher cognitive prominence and consumption have low availability, and their management is mainly through socio-cultural strategies, directed to ensure their availability, as the harvest technics to ensure their survival after the harvest, but not necessarily are directed to increase their abundance.

The number of uses was an important factor in edible, medicinal, fodder, ceremonial and ornamental plants; however, among medicinal plants, the species with higher cognitive prominence were those with few uses, in other words their properties determining them specialized medicinal plants, which is apparently related with their quality as resource [76].

Highly cognitive valued species not always are the most consumed or managed. For instance, species highly valued as ceremonial, like orchids have a low consumption because the difficulty to obtain them or be manipulated to increase their availability. These results and those found by several authors studying factors influencing management of edible plants [15, 77, 78], indicate that management motives may be variable not only related with cultural importance and scarcity, which suggests the importance of continuing research in this line.

Conclusion

Management factors and motives

A case that allows observing how people dynamically construct processes of decision making about management is Agave potatorum, in which the perception of risk of disappearing of the resource is the main factor detonating management actions, as documented for other plant resources of the Tehuacán Valley [15]. The strategies developed depend on TEK of both species and ecosystems [17], but there are external factors influencing experimenting innovation in management actions, as illustrated in the cases of several species of Agave [40, 79], in which markets have influenced increasing of extraction and pressures on agave populations and new management techniques [16, 17, 40]. This case illustrates that crises detonate innovation, activating processes of experimenting, monitoring, adapting, testing and interchanging local and external experiences, as well as enhancing processes of social organization, collaboration with governmental and academic sectors, learning and adaptation, in which the communitarian platforms of dialogue are crucial for facing risks and uncertainty [80, 81].

In other cases, the uncertainty in the availability of highly valued resources are motives for managing other species with redundant use and are able to substitute particular desirable resources, as are the cases of Tithonia tubaeformis and Simsia lagascaeformis whose abundance is promoted in controlled ways before the uncertainty of the main fodder of the study area (maize stubble). Such a complex decision making has important consequences in households’ economy [82] and biodiversity conservation in agroforestry systems [21, 22, 83].

Uncertainty operates associated to several factors, and ensuring the products quality is another management motive. People prefer consuming their own crops, which are considered of better quality over those commercialized in stores. Practices to assure the quality not are exclusively on crop plants, others like Bursera biflora have specialized resin extraction techniques that take advantage of natural processes assuring the resin quality avoiding injure the trees, instead of cutting trunks, a common practice in other localities [84]. Moreover, the perception of quality loss discourages ex situ management, in addition to energy investment and difficulties involved in maintaining these species outside their environments, as was noted in Bursera biflora and medicinal plants.

The aesthetical sense, expressed by people that consider that plants embellish the spaces where they occur, as Cook noted [33] in mid 20th century, appears to be an important motive that determining the permanence of numerous native species in homegardens and crop fields as forests conservation. This motive has been reported by other authors in agroforestry systems of the region [21, 22], and our study suggests its high importance because of the high number of species considered as house or “mountain luxury”, which receive some type of management practices.

Ethical principles like the fact that people recognize that plants are living beings with a right to exist, that plants should not be damaged because of whim, are ethical principles that motive management practices as tolerance. Also the including of several species in belief systems and matching cycles of plant management with the rituals calendar, suggest that although the Ixcatec kosmos is permeated by Catholic thinking, it maintains features with other Mesoamerican views of the world reported by other authors [20, 85].

Curiosity was mentioned to be involved in all management practices in response to motives such as uncertainty in plant resources’ availability or aesthetical needs. It enhances testing new techniques or new species or be persistent when reproductive requirements make difficult the plants propagation.

Deepen the study of motivations and socio-economic and cultural factors that influence plant management allow understanding the processes of decision making construction and biocultural legacy. Such studies could provide unique opportunities for strengthening conservation strategies of sustainable forms of management of resources and ecosystems.

Abbreviations

TEK, traditional ecological knowledge; UNAM, Universidad Nacional Autónoma de México; USA, United States of America

Declarations

Acknowledgements

We deeply thank people of Santa María Ixcatlán, the authorities and people who collaborated and gave us their hospitality. We also thank Luz E. García and Emanuel E. González for field work assistance, and Sandra Smith, Michael Swanton, Nicholas Johnson and Denis Costaouec for their support and collaboration in the Ixcatec Ethnobiology Project. We thank the botanical experts of MEXU, PATZ, IZTA and UDG herbaria (Appendix), for their help in identifying the voucher specimens, especially Rosalinda Medina-Lemos and Ismael Calzada, and to three anonymous referees for their suggestions for improving this manuscript.

Funding

The authors thank the Posgrado en Ciencias Biológicas at the Universidad Nacional Autónoma de México (UNAM) and the Consejo Nacional de Ciencia y Tecnología (CONACYT, Mexico) for supporting PhD studies and a grant for the first author. We also thank financial support for field work from CONACYT (Project CB CB-2013-01-221800), the PAPIIT, UNAM (Research project IN209214), Fundación Alfredo Harp Helú Oaxaca and Fundación UNAM (project IE-282.311.190).

Availability of data and materials

Data that support the analysis and additional data are provided in Appendix.

Authors’ contributions

SRL main author, involved in the study design, field work, analysis of data, wrote the first draft and concluded the final version of this paper. AC main coordinator-supervisor of the research project; participated in data analyses and reviewed several drafts of the manuscript. ERL, MVR and RLF contributed to field work and reviewed final drafts of the manuscript. ITG contributed to data analyses and reviewed the final drafts of the manuscript. All authors read and approved the final manuscript.

Authors’ information

SRL postgraduate student at the Instituto de Investigaciones en Ecosistemas y Sustentabilidad (IIES), UNAM. AC full-time researcher at IIES, UNAM. ERL Master in Sciences student at the Centro de Investigaciones en Geografía Ambiental (CIGA), UNAM. ITG & MVR posdoctoral at IIES & CIGA, UNAM. RLF technician of Pronatura México A.C.

Competing interests

The authors declare that they have no competing interests.

Consent for publication

Not applicable.

Ethics approval and consent to participate

Permits for conducting our investigation was obtained in the two phases of field work, with Federal agencies (SEMARNAT and Tehuacán-Cuicatlán Biosphere Reserve-CONANP), local authorities (municipal and land tenure) and Communitarian Assembly to realize the investigation and collect voucher plants in communal lands. Prior oral informed consent was obtained from all participants to realize the interview, survey, free lists and audio-visual recording or visit and gather plants in their homegardens or agricultural fields. Reports of activities and preliminary investigation outcomes have been doing via oral and written reports to the authorities and public presentations to the community of Ixcatlán.

Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.