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Agrociencia

On-line version ISSN 2521-9766Print version ISSN 1405-3195

Agrociencia vol.51 n.8 Texcoco Nov./Dec. 2017

 

Crop Science

Maize diversity in Pátzcuaro, Michoacán, México and its relationship with environmental and social factors

Quetzalcóatl Orozco-Ramírez1  * 

Jorge Odenthal2 

Marta Astier1 

1Centro de Investigaciones en Geografía Ambiental, Universidad Nacional Autónoma de México. Antigua Carretera a Pátzcuaro 8701, Col. San José de la Huerta, Morelia, Michoacán, 58190. México.

2IACATAS A. C. Mexico. (jorge.odenthal@iacatas.org.mx).


Abstract

The diversity of maize in the region of Lake Patzcuaro, Michoacan, Mexico, includes 11 out of the 27 maize races found in the State of Michoacan. This study was carried out from 2012 to 2015, with the aim of exploring the spatial distribution of the diversity of maize and the related environmental and social factors. Our hypothesis was that diversity has a heterogeneous regional distribution: diversity is greater in those locations where traditional agriculture is practiced. This kind of agriculture is associated with the presence of indigenous farmers and a greater diversity of agricultural environments. The ethnobotanical method was used to collect maize and interview farmers. We obtained information about crop management and the socio-economic variables of the production unit and the producer. This information was analyzed at regional, local, and production unit scale, using geographical methods, general linear models, and multi-variable methods. On a regional scale, the association of only some races with the types of soil and altitude was significant. One set of localities with high race diversity featured low altitude and high soil diversity. There are many names for maize in production units where farmers speak an indigenous language and own several smallholdings.

Key words: Zea mays subsp. mays; distribution of diversity; indigenous groups; purhepechas; maize races; general linear model

Resumen

La diversidad de maíces en la región del Lago de Pátzcuaro, Michoacán, México, incluye 11 de las 27 razas de maíz en el estado de Michoacán. El presente estudio se realizó de 2012 a 2015 con el objetivo de explorar la distribución espacial de la diversidad de maíces y los factores ambientales y sociales a los que está asociada. La hipótesis fue que la distribución de la diversidad es heterogénea en la región, la diversidad mayor está en las localidades que practican agricultura tradicional, la cual está asociada con la presencia de agricultores indígenas y diversidad mayor de ambientes agrícolas. Recolectas de maíz y entrevistas a agricultores se realizaron con el método etnobotánico. La información obtenida fue sobre manejo del cultivo y variables socioeconómicas de la unidad de producción y del productor. El análisis se realizó en escala regional, local y unidad de producción con métodos geográficos, modelos lineales generalizados y métodos multivariables. En escala regional la asociación sólo de algunas razas con los tipos de suelo y la altitud fue significativa. Un grupo de localidades con diversidad alta de razas se caracterizó por su altitud baja y su diversidad alta de suelos. En las unidades de producción se observó la asociación de la riqueza de nombres de maíces con el hecho de que el agricultor hable lengua indígena y tenga varias parcelas.

Palabras clave: Zea mays subsp. mays; distribución de la diversidad; grupos indígenas; purhépechas; razas de maíz; modelos lineales generalizados

Introduction

Mexico has the greatest diversity of maize in the world which includes morphological (Sánchez et al., 2000) and genetic (Vigouroux et al., 2008) variability. During the last ten years, maize diversity studies have been encouraged like in the 1970s, when Hernández-Xolocotzi carried out his studies (1972). The diversity of native maize population still prevails, mainly in traditional agricultural areas, because the races described in Mexico during the 1940s still exist (Perales and Golicher, 2014). Diversity is heterogeneously distributed in the country (Kato et al., 2009; Perales y Golicher, 2014); therefore, knowing which social and environmental factors determine high maize diversity areas and which programs should be designed to guarantee its in situ conservation is advisable (Ortega, 2003).

At least 59 maize races have been described in Mexico (Sánchez et al., 2000). A race includes a set of populations with great genetic variation and which share some characteristics (Ortega, 2003). The authors distinguish four to six diversity centers with races with different names; these centers match the following geographical regions: 1) Chiapas; 2) the valleys and sierras of Oaxaca; 3) the sierras of the west coast; 4) the central plateau; 5) the northwestern sierras; and, 6) the canyons of Chihuahua (Kato et al., 2009; Perales y Golicher, 2014; Orozco-Ramírez et al., 2017). Altitude is a factor that determines race distribution in these regions. The greatest abundance of races is found in average elevations in mountainous zones (Orozco-Ramírez et al., 2017). Perales et al. (2003) pointed out that, in central Mexico, local varieties dominate the agricultural landscape at higher altitudes and that improved varieties are more adopted at average altitudes. In contrast, a greater race abundance was identified at lower altitudes in Chiapas, although color was more diverse in the highlands (Brush and Perales, 2007). Farmers prefer to use local varieties in low quality soils and to sow improved varieties in higher quality soils (Bellon and Taylor, 1993; Fenzi et al., 2017). However, the connection between contrasting technology areas and maize race diversity was not significant in Guanajuato, (Aguirre et al., 2000).

The connection between maize abundance and indigenous communities is complex and very few studies have been made about them. The sampling of maize diversity has not been systematic and the effect of the environment in some indigenous towns in specific areas has not been isolated (Brush, 2004). However, it has been decades since the association between maize diversity and indigenous population was first suggested. When Boege (2008) superimposed the maize diversity map over the map of Mexico’s indigenous territories, he observed a greater diversity in those zones than in zones where industrial agriculture was practiced or where the population was racially-mixed. Exceptionally, some regions with low indigenous presence had high maize diversity. Systematic collection among the indigenous groups of Oaxaca, showed that maize diversity increased along with indigenous presence (Hernández-Xolocotzi, 1972). In some regions of Oaxaca and Chiapas, there is a significant correlation between indigenous population and race abundance; however, in other regions with high race diversity -such as the sierras of the western and northwestern coasts-, correlation is low and in other regions with high indigenous population, such as Yucatan, maize race abundance is low (Perales and Golicher, 2014). In Chiapas, the diversity of maize races and local maize varieties used by indigenous farmers at several altitudes is higher than those used by mixed-race farmers, who use more modern varieties (Brush and Perales, 2007).

Maize races abundance is high in Michoacan, Mexico: 27 of the 59 races reported in Mexico can be found there (Orozco-Ramírez et al., 2017). Taking into consideration its area, Patzcuaro, Michoacan, also has a great diversity of maize races. The main races found in that region are: Cónico, Purhépecha, Chalqueño, Elotes Cónicos, Elotes Occidentales, Tabloncillo, and Cacahuacintle. The diversity of native maize was monitored from 2005 to 2015, showing that the abundance of races and local varieties has remained high. Although the area where maize was sown did diminish, the same races and local varieties that were sown in 2005 are still sown today (Orozco and Astier, 2017).

The aim of this study was to describe the diversity of maize and their distribution in the Lake Patzcuaro region, as well as their connection with environmental and social factors. Diversity distribution was analyzed using a multi-scale approach. Our hypothesis was that diversity is heterogeneously distributed in the region and that maize diversity is greater in those locations where traditional agriculture is still practiced. This kind of agriculture is associated with the presence of indigenous farmers and more diverse agricultural environments.

Materials and Methods

Area of study

The Lake Patzcuaro region is located in the heart of the Trans-Mexican Volcanic Belt, in the State of Michoacan. The population and economic activities of this natural and cultural region are complex and heterogeneous. Indigenous localities, and mixed-raced cities and towns share space and primary production activities mix with tourism in the same landscape (Mapes et al., 1994). The rural localities’ main economic activities are agriculture, cattle raising, handicrafts, and fishing (Castilleja, 1992). The region is made up of the municipalities of Patzcuaro, Erongaricuaro, Quiroga, and Tzintzuntzan. The municipal capitals are the main population centres. The city of Patzcuaro stands out as the region’s economic center. The average human development index for the four municipalities (0.672) is lower than the national index (0.739). Patzcuaro’s index (0.695) is higher than the other three (PNUD, 2014). Indigenous population accounts for 20 % of the overall population. Erongaricuaro is the municipality with the highest percentage (40 %) of indigenous population (CDI, 2010).

The region is dominated by volcanic mountains, intermontane valleys, foothills, and lowhills. The lake surface is located at 2040 meters above sea level and the highest peak reaches 3400 meters above sea level (Barrera-Bassols, 1992). The weather is temperate sub-humid and it rains in the summer. The overall average rainfall is 1100 mm per year. The average yearly temperature is 16.9 °C, with a minimum average of 8 °C and a maximum average of 25.7 °C (CICESE, 2015). The vegetation in the lowhills is made of pine trees and holm oaks. Agriculture is carried out in the plains around the lake and in the valleys. The agricultural landscapes defined by Mapes et al. (1994) and Astier et al. (2010) are associated with the type of soil: a) andosols are residual moisture rainfeed agriculture landscapes where long-cycle maize varieties are sown early; b) acrisols and lithosols are rainfeed agriculture landscapes where short-cycle maize is sown when the rain seasons starts; c) vertisols are lake shore agriculture landscapes or ever humid lands on the bank of the lake; and, d) luvisols are irrigated agriculture landscapes (INEGI, 2013a).

Agriculture is mainly carried out in small production units, with an average area of 3.7 ha (INEGI, 2007). The main annual crops are maize (Zea mays subsp. mays), oat forage (Avena sativa), wheat (Triticum aestivum), beans (Phaseolus vulgaris), squashes (Cucurbita pepo), fig-leaf gourd (C. ficifolia), lentils (Len culinaris), and common vetch (Vicia sativa). Maize covers 8115 ha (71 %) of the cultivated area. In general, farmers sow their own seed; hybrid maize is hardly sown. The most important perennial crops are avocado (Persea americana) and alfalfa (Medicago sativa) (SIAP, 2015).

Field work

From 2012 to 2015, 113 interviews were conducted with farmers from 29 localities in the Lake Patzcuaro region. The samples were selected using the method proposed by Hernández-Xolocotzi (1972): maximizing the gathering of samples from different maize types with the lowest number of interviews. The interviews ended when every kind of maize recognized by each community had been collected. The interviews were specifically focused on those farmers that the community recognized as the ones who sow the highest quantity and quality of local maize races. Crop management and smallholding location were also recorded. In 2012, a minimum of six corncobs were collected; they were chosen by the farmers and their race was identified by José Alfredo Carrera, ScD. In 2015, farmers were interviewed, but no samples were collected. The technical team classified the maize samples at the farmers’ homes. Most of the local and native maize populations had characteristics from two or more races. In order to facilitate the analysis, the dominant race was used. Samples with mixed characteristics that the team was not able to classify were placed in the undetermined category. The GPSlogger Android app was used to georeferenced the smallholdings. Geographical data was processed using ArcMap 10.1 and were combined with the survey’s data.

Data analysis

Data were analyzed per region, locality, and production unit. In the first case, a geographical information system was designed. It included the following elements: 1) elevation digital model, developed based on the level curves of topographic maps (scale: 1:50 000; INEGI, 2015); 2) vector layer of soils, series II by (INEGI 2013a) (scale: 1:250 000); 3) layer of villages and towns from the geostatistical framework, version 6.2 (INEGI, 2014); 4) layer of land use based on series V (INEGI, 2013b), which allowed us to define the moisture system (irrigation, rainfeed, moisture); 5) layer of water sources from the topographic maps (scale: 1:50 000; INEGI, 2015); and 6) vector layer of the location of the maize races, based on the surveys.

The database of maize races and their location was made up of 402 observations with the following fields: race, locality, municipality, grain color, use, type of soil (according to the farmer), moisture system, cultivation system, type of soil (INEGI, 2013a), agri-environment, local variety (local name of the native maize population), altitude, and slope. A map was designed to represent maize race distribution and those races were qualitatively associated with the variables, by means of a visual exploration. The location of the collections was adjusted in the printed map, in order to reduce the superimposition of points. Labels were created for each point in order to make this possible; those points were moved in order to obtain minimum required distance. For each of the races with more records (Purhépecha, Cónico, Elotes Occidentales, Ancho, Chalqueño, and Elotes Cónicos), a general linear model was developed and those races were then associated with environmental variables. A binomial model with a logit link function was used. A separate model was made for each race (with R version 3.3.1; Core Team R, 2016); a point was marked in the map where a race of interest was located. The variables used to model the presence of a race were altitude, type of soil, and slope. The moisture system was not included, due to its association with the type of soil (X2=435.3, p=0.000). The residual moisture system matched andosols, the rainfeed agriculture system matched acrisols, and the irrigated agriculture system matched luvisols.

A local analysis was based on the information of eight variables that set each community apart (Table 1). Localities where only one or two farmers were interviewed were excluded, including the cities of Patzcuaro, Quiroga, and Erongaricuaro. Overall, 18 out of 29 localities in which interviews were carried out were included. Therefore, race abundance, local varieties abundance (number of local names of maize populations tilled in the community), total population, indigenous population, average altitude, abundance of agriculture soil types, and the Shannon diversity index were analyzed using the principal component analysis (PCA) with R (Core Team R, 2016). The Simpson index was excluded from this analysis, because it was significantly correlated with the Shannon index (R=0.98; p=0.000). Ethnographic information was included in the PCA in order to characterize localities with greater abundance of maize types and to explain diversity variation per locality.

Table 1 Variables included in the analysis per locality and per production unit. 

Excluding localities with one or two interviews. Excluding (12) interviews with incomplete data. Overall, 101 interviews were used in the analysis.

Production unit analysis was carried out using the Poisson model, with a logarithm link function. The variable to be predicted was the number of local names for the native populations. This variable was chosen instead of race abundance, because the average number of races per production unit was low (mean: 1.96 races per production unit). Not only was the number of local names greater, but it also had a practical meaning for farmers, because each name is the basic unit they use to classify maize in their locality. The dependent variable was modelled with 19 variables of the production unit (Table 1). One of the evaluated models was chosen based on residual variance and Akaike’s Information Criterion (AIC). A subsample of units with more than five maize populations was chosen to complete the analysis of the production unit, and each production unit was described using the survey’s data.

Results and Discussion

Diversity distribution on a regional scale

The 11 maize races that were detected showed a typical distribution of species frequency: few races with high frequency and many races with low frequency. The dominant races were Purhépecha (170 records) and Cónico (72). Elotes Occidentales (34), Ancho (26), Chalqueño (20), and Elotes Cónicos (20) showed average frequency. The races with very low frequency were Mushito (9), Pepitilla (8), Cacahuacintle (5), Tabloncillo (3), and Palomero Toluqueño (1). A population that came from a hybrid variety was recorded, and 33 records were not associated with any particular race, due to their undefined characteristics.

The race distribution map showed several patterns (Figure 1). It seems that the Purhépecha races dominated a south-west strip in the highlands, which included the Casas Blancas, Opopeo, Zirahuén, Santa María Huiramangaro, and Pichátaro localities. This strip is dominated by residual moisture lands and its soils have high moisture retention capacity; therefore, they are sown before the rains start (Mapes et al., 1994; Astier et al., 2012). Another pattern showed that the Cónico, Elotes Occidentales, and Elotes Cónicos races dominate in the lowlands of the northwestern bank of the lake, in the localities of Uricho, Napízaro, San Andrés Ziróndaro, and Jerónimo Purenchécuaro. These are rainfeed agriculture lands, with luvisol and acrisol type soils. Fast growth races are sown at the beginning of the rain season. Another agri-environment is irrigated lands, which showed a high diversity of long- and short-cycle races. The greater diversity seems to be located in the lowlands. Three lowland areas have high diversity: the first is located in San Jerónimo Purenchécuaro and San Andrés Ziróndaro, north of the lake; the second is located between Napízaro and Uricho, southeast of the lake; and the third is located in the irrigation zone between Tzurumútaro, El Jagüey, and Nuevo Rodeo, east of the lake.

Figure 1 Distribution map of maize races in the Patzcuaro region. 

Association with type of soil, altitude, slope, and agricultural environments

The analysis of the correlation between races and agro-environment only included Purhépecha, Cónico, Elotes Occidentales, Ancho, Chalqueño, and Elotes Cónicos, because they were the most frequent races. The other five races were not modelled because they had a significantly low frequency.

Binomial models for race distribution indicate that the Purhépecha race is associated with an average altitude of 2260 m, frequently located in andosol soils with minimal slope. The Cónico race was frequently associated with environments in the low part of the basin, but there’s a weak association between this race and altitude. We could not define an association with the plot’s slope, because it was located in valleys and low hills. Due to this race’s association with acrisols and andosols, it seems to be cultivated during the rainy season and with residual moisture (Tables 2 and 3).

Table 2 Results of the binomial model (link=logit) to describe the association of races with environmental factors

Races were modelled separately. *** Pr≤0.001; ** Pr≤0.01; * Pr≤0.05; Pr≤0.1.

Table 3 Distribution variable intervals of the maize races in the region of Patzcuaro, Michoacan, Mexico. 

The Elotes Occidental race was associated with the lowlands and seemingly with acrisols and luvisols; however, the effect of the type of soil was not significant in the model, probably because the number of records for this race (34) was relatively low. This race had a greater frequency in lands with more slope, like the low hills around the lake. The Ancho race was associated with the low hills in the lower part of the basin and was not directly associated with a specific type of soil. The Chalqueño race was associated with lands with low slope and average altitude, and it was not associated with any kind of soil. The Elotes Cónicos race was more common in low lands, but was not directly associated with the slope or the type of soil. The Ancho, Chalqueño, and Elotes Cónicos race models provided few explanations about overall variance, because few records were available. An increased number of cases can generate stronger models (Tables 2 and 3).

Model adjustment changed from one race to another. The best explanation of data variation (13 % of the total variance) was provided by the model that included the Purhépecha race. The Cónico race model accounted for only 3 % of the variance, because few records were available for it. Additionally, this variance allowed us to suggest that this race is distributed in most of the region’s environments. The analysis of molecular markers usually indicates a greater variation from one population to another, rather than within each population (Vigouroux et al., 2008; Orozco-Ramírez et al., 2017). The high genetic variability between and within populations enables races to have greater adaptation scope.

The altitude distribution for some of the races identified in the Patzcuaro region exceeded the interval reported by Ruiz et al. (2008). According to them, the Elotes Occidentales race was found between 700 and 2170 m; however, our study indicates that this race was distributed up to 2675 m in this region. Our report indicated that the Ancho and Pepitilla races could be found 360 and 400 m above the distribution reported in that study. Meanwhile, the Palomero Toluqueño race was found below the distribution reported by Ruiz and his collaborators.

The races showed great adaptability, because they were found in all agri-environments in the region and we were able to distinguish the localities and the socio-environmental conditions under which some races are most frequently found. Farmers distinguish mainly between maize types for rainfeed systems and for residual moisture systems. The main variation is the length of their cultivation cycles. The highland farmers usually use seeds from the lowlands for the second sowing, when the moisture crops fail, because they know that lowland seeds have shorter cycles.

Local diversity distribution

The abundance, and the diversity of races and local names for native maize did not have any significant association with the variables that were selected according to the locality. Poisson models were discarded because they did not explain the variance. In contrast, PCA per locality indicated that localities with five or seven races shared characteristics, such as altitude (medium to low) and human population size (low to medium). Pichátaro does not fit this pattern, as a result of its abundance of races, big population, and high elevation. The first and second main components (CP) accounted for 69.5 % of the variance (Figure 2). The variables that were more important in the definition of the first CP were Shannon diversity index (0.57 rotation), race abundance (0.55), number of types of agricultural soils (0.42), and medium altitude (-0.38). The most important variables to determine the second CP were the number of local names for native maize types (-0.55), indigenous population (-0.48), and total population (-0.42).

Figure 2 Biplot of the main component analysis of the localities. 

The communities with more races were El Zapote (7), San Andrés Tziróndaro (7), Arócutin (6), San Francisco Uricho (6), Tzurumútaro (6), Napízaro (5), and San Francisco Pichátaro (5). The seven communities showed partially different environmental and socio-economic characteristics; therefore, we were unable to define a high diversity profile for these localities (Table 4).

Table 4 Characteristics of the localities with greater maize race diversity in Patzcuaro, Michoacan, Mexico. 

Analysis per family unit

Among the models used to predict the number of native maize names per production unit, we chose one that only included 3 out of the 19 proposed variables. The variables that provided a better explanation for the dependent variable were total maize area, number of smallholdings, and head of family that speaks an indigenous language. The model’s AIC with the 19 and the 3 variables were 352 and 324 and accounted for 50.3 and 43.4 % of the data variability, respectively.

Based on this model, these three variables have a positive effect on the number of native maize names (Table 5). According to the model, the effect of each factor -when the other factors remain constant- is the following: 1) the number of native maize names will increase by a factor of 1.03 as maize cultivation per hectare increases; 2) the number of names will increase by a factor of 1.11 for each smallholding that is added; and 3) the number of names will increase by 43 % if the farmer speaks Purhépecha.

Table 5 Poisson model results for the number of native maize names per production unit, in Patzcuaro, Michoacan, Mexico. 

*Significant p value.

Out of 113 farmers interviewed, only seven had five or more maize names and 3 production units were located in Pichátaro, 2 were located in Napizaro, 1 was located in Nuevo Rodeo, and 1 more was located in Uricho. Four out of this seven farmers speak Purhépecha and they were 51-66 years old. The farmer who mentioned 11 names or types of maize said that he sows them in 11 smallholdings (28 ha), that he had not gone to school, and that he also raised cattle. The others reported sowing 3-5 smallholdings in 2-11 ha. Six said they had gone 3 years to school and only one had higher education. All of them reported another activity (cattle-raising, handicraft production, or forest-related). The farmer with the highest education was a primary school teacher, he was the youngest, and had used his oldest seed for the shortest time (10 years). The other farmers had used the same seed for an average of 25 years. Some farmers have used the same seed for over 50 years.

The minor adjustment of the binomial model for the regional presence of the Purhépecha, Cónico, Elotes Occidentales, Ancho, Chalqueño, and Elotes Cónicos races may indicate that the altitude, slope, and type of soil variables are not very relevant to explain the races’ presence. Additionally, this can be the result of the close variation interval of the variables in the region under study. Therefore, the close environmental gradient does not affect the possibility of cultivating one race or another. Expanding the zone under study would be necessary to prove this hypothesis. It is also possible that farmers prefer the Purhépecha and Cónico populations, which were the most frequent races. Although the Purhépecha race was associated with humid lands and the Cónico race was associated with rainfeed agriculture lands, they were not exclusive to those environments. Therefore, these seem to be the most essential maize types consumed in the region. The other maize types were complementary and are sown in small areas, few records about them were obtained, and the models had a low adjustment. This dominant and secondary varieties pattern is common in México (Perales et al., 2003).

The Poisson models used to explain race abundance and the names of local populations per race did not explain the variance. Although PCA accounted for 69.5 % of the variance, the joint results with the Poisson models showed that PCA did not reveal any pattern that allowed us to explain the community-scale abundance and did show which variables had a greater variation.

The family unit provided a better model of the abundance of names in local populations. The variables selected for the final model were: total maize area, number of smallholdings, and indigenous language; it accounted for 43.4 % of the maize abundance. One of the reasons to keep a diversity of local varieties is the diversity of cultivation environments, as expressed by soil diversity (Bellon and Taylor, 1993). Farmers in the basin of Lake Patzcuaro who had sown maize in more smallholdings in greater areas had a greater environmental diversity. Therefore, they required more maize types.

The positive quantitative association between indigenous culture and agrobiodiversity in the production unit has been proven: such is the case of indigenous farmers compared with mixed-raced farmers in an altitude transect in Chiapas (Brush and Perales, 2007). In the Andes, it became evident that farmers with indigenous cultural roots invariably keep a greater agrobiodiversity in their fields. In this case, such association was made clear by the use of indigenous clothing and language and consuming traditional elements (Skarbø, 2014). There is a close bond in the region between maize diversity and community life: the farmers’ world view, the localities’ holiday calendar, and other cultural aspects proves this (Mapes et al., 1994; Orozco and Astier, 2017). The dishes that are prepared during these festivities, which go back to ancient rituals, frequently include maize in various ways (Castilleja et al., 2003).

It seems that the factors that influence diversity are not the same for all scales. Diversity is associated with different variables, at the regional, local, and production unit scales. On a regional scale, we can observe high and low maize abundance zones. The following zones were outstanding: one zone in the north and center-west had high density and most of the communities had high indigenous presence; the east zone also had high density and some of its towns had a majority of mixed-race population. Altitude, slope, and type of soil (or moisture system) explained the distribution of races in these zones. Some races are typical and dominant in certain agro-environments. Local scale provided information about the existence of communities with high diversity which share bio-physical and demographic conditions, except for one community where other patterns prevail. In the production unit scale, abundance/diversity and the type of races/varieties at home resulted from such variables as area, number of smallholdings, presence of animals, and significantly the socio-cultural and ethnic characteristics of the farmer and his or her family.

Conclusions

Diversity is not homogeneously distributed in the region. There are zones, localities, and farmers which stand out, as a result of their high maize diversity. This hypothesis is partially accepted, because at local scale there are both traditional indigenous localities, as well as mixed-race localities with a high abundance of maize races. The production unit analysis points out that farmers who speak an indigenous language and who have a greater number of smallholdings reported a greater diversity of types (names) of maize.

Literatura Citada

Aguirre G., J. A., M. R. Bellon, and M. Smale. 2000. A regional analysis of maize biological diversity in Southeastern Guanajuato, México. Econ. Bot. 54: 60-72. [ Links ]

Astier, M., N. Barrera-Bassols, J. Odenthal, M. I. Ramirez, Q. Orozco, and J. O. Mijangos-Cortés. 2010. Participatory identification and mapping of maize diversity in the Pátzcuaro-Zirahuén basins, Michoacán, México. J. Maps 6: 1-6. [ Links ]

Astier, M., E. Pérez-Agis, Q. Orozco, M. Patricio-Chavez, y A. Moreno-Calles. 2012. Sistemas agrícolas, conocimiento tradicional y agrobiodiversidad: El maíz en la cuenca del Lago de Pátzcuaro. In: Argueta V., A., M. Gómez S., y J. Navia A. (coords.). Conocimiento Tradicional, Innovación y Reapropiación Social. Grupo Editorial Siglo XXI. México, D.F. pp: 146-172. [ Links ]

Barrera-Bassols, N. 1992. Ecogeografía. In: Toledo, V.M., P. Alvarez-Icaza, y P. Ávila (eds). Plan Pátzcuaro 2000. Investigación Multidisciplinaria para el Desarrollo Sostenido. Fundación Friedrich Ebert. Mexico, D.F. pp: 11-36. [ Links ]

Bellon, M. R., and J. E. Taylor. 1993. “Folk” soil taxonomy and the partial adoption of new seed varieties. Econ. Dev. Cult. Change 41: 763-786. [ Links ]

Boege, E. 2008. El Patrimonio Biocultural de los Pueblos Indígenas de México: hacia la Conservación in situ de la Biodiversidad y Agrodiversidad en los Territorios Indígenas. Instituto Nacional de Antropología e Historia, Comisión Nacional para el Desarrollo de los Pueblos Indígenas. México, D. F. 342 p. [ Links ]

Brush, S. B. 2004. Farmers’ Bounty: Locating Crop Diversity in the Contemporary World. Yale University Press. New Haven, Connecticut. 327 p. [ Links ]

Brush, S. B., and H. R. Perales. 2007. A maize landscape: ethnicity and agro-biodiversity in Chiapas México. Agr. Ecosyst. Environ. 121: 211-221. [ Links ]

Castilleja G., A. 1992. Población. In: Toledo, V. M., P. Alvarez-Icaza, y P. Ávila (eds.). Plan Pátzcuaro 2000. Investigación Multidisciplinaria para el Desarrollo Sostenido. Representación en México de la Fundación Friedrich Ebert. México, D. F. pp: 239-272. [ Links ]

Castilleja G., A., A. G. R. Cervera A., C. García M., y H. Topete L. 2003. La comunidad y el costumbre en la región Purépecha. In: Millan, S., y J. Valle. (coords.). La Comunidad sin Límites. La Estructura Social y Comunitaria de los Pueblos Indígenas de México. Vol. III. Instituto Nacional de Antropología e Historia. México, D.F. pp: 17-112. [ Links ]

CDI (Comisión Nacional para el Desarrollo de los Pueblos Indígenas). 2010. Cédulas de información básica de los pueblos indígenas de México. México, D.F. http://www.cdi.gob.mx/cedulas/ (Consulta: diciembre 2016). [ Links ]

CICESE (Centro de Investigación Científica y Educación Superior de Ensenada). 2015. Datos climáticos diarios del CLICOM del SMN a través de su plataforma web del CICESE. http://clicom-mex.cicese.mx (Consulta: mayo 2016). [ Links ]

Core Team R. 2016. R: A language and environment for statistical computing. R Foundation for Statistical Computing. Vienna, Austria. http://www.r-project.org (Consulta: junio 2016). [ Links ]

Fenzi, M., D. I. Jarvis, L. M. Arias R., L. Latournerie M., and J. Tuxill. 2017. Longitudinal analysis of maize diversity in Yucatan, México: influence of agro-ecological factors on landraces conservation and modern variety introduction. Plant Genet. Resour. 15: 51-63. [ Links ]

Hernández-Xolocotzi, E. 1972. Exploración etnobotánica en maíz. Fitotec. Latinoamer. 8: 46-51. [ Links ]

INEGI (Instituto Nacional de Estadística y Geografía). 2007. Censo Agrícola, Ganadero y Forestal 2007. Tabulados. INEGI. Aguascalientes, México. http://www.inegi.org.mx/est/contenidos/proyectos/Agro/ca2007/Resultados_Agricola/ (Consulta: junio 2016). [ Links ]

INEGI (Instituto Nacional de Estadística y Geografía). 2013a. Conjunto de datos vectorial Edafológico escala 1: 250 000 Serie II (Continuo Nacional). INEGI. Aguascalientes, México. http://www.inegi.org.mx/geo/contenidos/recnat/edafologia/vectorial_serieii.aspx (Consulta: junio 2016). [ Links ]

INEGI (Instituto Nacional de Estadística y Geografía). 2013b. Conjunto de datos vectoriales de uso del suelo y vegetación escala 1:250 000, Serie V (capa unión). INEGI. Aguascalientes, México. http://www.inegi.org.mx/geo/contenidos/recnat/usosuelo/ (Consulta: junio 2016). [ Links ]

INEGI (Instituto Nacional de Estadística y Geografía). 2014. Marco geoestadístico 2014 versión 6.2 (DENUE). INEGI. Aguascalientes, México. http://www.inegi.org.mx/geo/contenidos/geoestadistica/m_g_0.aspx (Consulta: junio 2016). [ Links ]

INEGI (Instituto Nacional de Estadística y Geografía). 2015. Conjunto de datos vectoriales de información topográfica escala 1:50 000 serie III. E14A22 (Pátzcuaro). INEGI. Aguascalientes, México. http://www.beta.inegi.org.mx/app/biblioteca/ficha.html?upc=702825271879 (Consulta: mayo 2017). [ Links ]

Kato Y., T. A., C. Mapes S., L. M. Mera O., J. A. Serratos H., y R. A. Bye B. 2009. Origen y Diversificación del Maíz: Una Revisión Analítica. Universidad Nacional Autónoma de México, Comisión Nacional para el Conocimiento y Uso de la Biodiversidad. México, D. F. 116 p. [ Links ]

Mapes, C., V. M. Toledo, N. Barrera, y J. Caballero. 1994. La agricultura en una región indígena: la Cuenca del lago de Pátzcuaro. In: Rojas R., T (ed). Agricultura Indígena, Pasado y Presente. Ediciones de la Casa Chata. Centro de Investigación y Estudios Superiores en Antropología Social. México, D. F. pp: 275-341. [ Links ]

Orozco-Ramírez, Q., and M. Astier. 2017. Socio-economic and environmental changes related to maize richness in México’s central highlands. Agric. Human Values 34: 377-391. [ Links ]

Orozco-Ramírez, Q., H. Perales, and R. J. Hijmans. 2017. Geographical distribution and diversity of maize (Zea mays L. subsp. mays) races in Mexico. Genet. Resour. Crop Evol. 64: 855-865. [ Links ]

Ortega P., R. 2003. La diversidad del maíz en México. In: Esteva, G. y C. Marielle (coords.). Sin Maíz no Hay Pais. Consejo Nacional para la Cultura y las Artes/Dirección General de Culturas Populares. México, D. F. pp: 123-154. [ Links ]

Perales, H., S. B. Brush, and C. O. Qualset. 2003. Landraces of maize in Central México: an altitudinal transect. Econ. Bot . 57: 7-20. [ Links ]

Perales, H ., and D. Golicher. 2014. Mapping the diversity of maize races in México. PloS ONE 9: e114657. [ Links ]

PNUD (Programa de las Naciones Unidas para el Desarrollo). 2014. Indice de Desarrollo Humano Municipal en México: Nueva Metodología. Programa de las Naciones Unidas para el Desarrollo. México, D.F. 102 p. [ Links ]

Ruiz C., J. A., N. Durán P., J. J. Sánchez G., J. Ron P., D. R. González E., J. B. Holland, and G. Medina G. 2008. Climatic adaptation and ecological descriptors of 42 Mexican maize races. Crop Sci. 48: 1502-1512. [ Links ]

Sánchez G., J. J., M. M. Goodman, and C. W. Stuber. 2000. Isozymatic and morphological diversity in the races of maize of México. Econ. Bot . 54: 43-59. [ Links ]

SIAP (Sistema de Informacion Agroalimentaria y Pesquera). 2015. Anuario estadístico de la producción agrícola. Sistema de Información Agroalimentaria y Pesquera, SAGARPA. México, D. F. http://infosiap.siap.gob.mx/aagricola_siap_gb/ientidad/index.jsp (Consulta: mayo 2016). [ Links ]

Skarbø, K. 2014. The cooked is the kept: factors shaping the maintenance of agro-biodiversity in the Andes. Human Ecol. 42: 711-726. [ Links ]

Vigouroux, Y., J. C. Glaubitz, Y. Matsuoka, M. M. . Goodman, J.Sánchez G., and J. Doebley. 2008. Population structure and genetic diversity of New World maize races assessed by DNA microsatellites. Am. J. Bot. 95: 1240-1253. [ Links ]

Received: January 2017; Accepted: May 2017

*Author for correspondence: qorozco@ciga.unam.mx; mastier@ciga.unam.mx

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