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Terra Latinoamericana

versión On-line ISSN 2395-8030versión impresa ISSN 0187-5779

Terra Latinoam vol.39  Chapingo ene./dic. 2021  Epub 13-Sep-2021

https://doi.org/10.28940/terra.v39i0.930 

Artículo científico

The backyard of Tlaxcala. An approach to its composition

El traspatio de Tlaxcala. Una aproximación a su composición

Andrés María-Ramírez1   
http://orcid.org/0000-0003-1376-8388

1 El Colegio de Tlaxcala, A.C. Av. Melchor Ocampo No. 28. 90600, San Pablo Apetatitlán, Tlaxcala, México.


Summary:

The backyard is an agroecosystem located near the home and fulfills several functions and provides various services; in addition, one third of the Rural Production Units in Tlaxcala have this agroecosystem. In the Mexican state of Tlaxcala, México, the primary sector is the one that contributes the least to the gross domestic product; it is divided into 60 municipalities and 66% of its territory is used for agricultural, livestock and forestry activities and little is known about this agroecosystem. The objective of the research was to make an approximation of its composition with respect to the plant and animal species found in the backyard. The Registry of Agricultural Producers of the State of Tlaxcala, Mexico, carried out by the National Institute of Statistics and Geography (INEGI) was used; as a member of the work team, a copy of the original database was obtained informally, which consisted of a total of 53 968 basic information cards; of that total, 17 236 reported backyard activities. The information was analyzed using frequency tables of data grouped and sorted into classes for both plant and animal species. Regarding the composition of the main vegetable species produced in the backyard, fruit trees such as peaches and corn stand out. Of the animal species produced, cattle and poultry are the most produced. On average, 91.15% of what is produced in the backyard is for self-consumption; the average area of the backyard was 215 m2. The composition of the Tlaxcala backyard was determined in terms of plant and animal species of certain economic importance; the results reported here can be useful for other research that continues with the characterization of the structure, composition and functioning of the backyard in the state of Tlaxcala.

Index words: animal production; farmers; pluriactivity; self-consumption; vegetable production

Resumen:

El traspatio es un agroecosistema que se ubica cerca de la vivienda y cumple varias funciones y presta diversos servicios; además, una tercera parte de las Unidades de Producción Rural de Tlaxcala cuenta con este agroecosistema. En el estado mexicano de Tlaxcala el sector primario es el que menos aporta al producto interno bruto; está dividido en 60 municipios y 66% de su territorio se destina a actividades agrícolas, ganaderas y forestales y poco se conoce de este agroecosistema. El objetivo de la investigación fue realizar una aproximación a su composición con respecto a las especies vegetales y animales que se encuentran en el traspatio. Se utilizó el Registro de Productores Agropecuarios del Estado de Tlaxcala, México, realizado por el Instituto Nacional de Estadística y Geografía (INEGI); como miembro del equipo de trabajo, se obtuvo de manera informal una copia de la base de datos original, la cual consistió en un total de 53 968 cédulas de información básica; de ese total, 17 236 reportaron actividades de traspatio. La información se analizó mediante tablas de frecuencias de datos agrupados y ordenados en clases tanto de especies vegetales como animales. En cuanto a la composición de las principales especies vegetales producidas en el traspatio, destacan los frutales como el durazno y el maíz. De las especies animales producidas, el ganado y las aves de corral son las más producidas. En promedio, 91.15% de lo que se produce en el traspatio es para autoconsumo; la superficie promedio del traspatio fue de 215 m2. Se determinó la composición del traspatio tlaxcalteca en cuanto a especies vegetales y animales de cierta importancia económica; los resultados aquí reportados pueden ser útiles para otras investigaciones que continúen con la caracterización de la estructura, composición y funcionamiento del traspatio en el estado de Tlaxcala.

Palabras clave: producción animal; campesinos; pluriactividad; autoconsumo; producción vegetal

Introduction

Located in the central eastern part of the country, the state of Tlaxcala belongs to the region of the neovolcanic axis that crosses the central part of the country; its coordinates are 19° 44' and 19° 06' North Latitude and 97° 43' 08'' - 98° 46' West Longitude. It has a temperate climate with a landscape of volcanic mountains of all types, more or less flat. It has an area of 3 991 km2; 96% of the Rural Production Units (RPUs) have agricultural or forestry activity; 56.4% of them have an area of up to 2 hectares, indicating a serious smallholding problem (SAGARPA, 2018); 18.6% of the Economically Active Population performs agricultural activities (Fundación Produce Tlaxcala, 20111). Agricultural and livestock activities account for 4% of the state's Gross Domestic Product (CONACYT-Government of Tlaxcala, 2010). According to Damián et al. (2009), almost three quarters of the corn growers in the state of Tlaxcala were classified as pluriactive. Over the population, 78.2% live in urban areas and 21.8% in rural areas; the entity has a schooling of 8.8 years (INIFAP-SAGARPA, 2015). Poor rural families allocate on average 47.5% of their total expenditure to food consumption, while the urban poor allocate just over 42% (Chávez, Villarreal, Cantú, and González, 2009); for his part, Juárez (20152) says that on average, 27% of rural households report food self-consumption from agricultural activities; in contrast, only 7% of urban households report self-consumption related to service activities, and only 2% report food self-consumption associated with agricultural activities. It is important to consider, in the backyard study environment, that 45.3 percent of the Tlaxcalan population cannot acquire the food basket with their labor income (labor poverty) in the first quarter of 2020, a rate that is 0.6 percentage points higher than the 44.7 percent in the fourth quarter of 2019 (Avendaño, 2020). From field visits in the entity, it is known that backyards have edible plant species such as corn, peach, pecan walnut, plum, pear, apple, etc., and that they raise animals such as goats, sheep, pigs, rabbits, poultry, bees, cows, donkeys, horses, etc.

There are few studies that describe the backyard in Tlaxcala State. The backyard that existed in Tlaxcala after the conquest of Mexico by the Spanish (500 years ago), is described by González (2006): usually located in the Franciscan Convents and cultivated with fruit trees, crops and condiment plants; she makes no mention of livestock activity in the orchards. The home garden present in Tlaxcala State, is characterized by the maguey, plum trees, apricots custard apple, peach, guava, fig, lime, lemon, apple, orange tree, walnut, pear, tejocote, some grape, xoconostle and plant species such as corn. González (2004) describes the backyard based on the investigations on basic ecological aspects that were carried out in four orchards in the community of Tepeyanco, south of Tlaxcala, which were carried out by Stephen R. Gliessman and his students from Agroecology Program, University of California at Santa Cruz, in the years 1981 and 1983; the existence of a total of 82 useful species and an average of 33 in a total area of 1.35 hectares was reported; too, bees, birds, donkeys, mules, pigs, cows, oxen are also reported. Chávez (20073) describes in two different localities in Tlaxcala, the backyard with a study population of 180 people (53% men). The average age of the heads of families was 53.2 years and their level of schooling was 10.1 years of school; 40% of the heads of families are dedicated to agricultural activities. The average size of the backyards was 1 595 square meters. It is striking that only 20% use the entire backyard area for agricultural activities while 25% use half of the area. The backyard is used for the agricultural production of annual crops such as corn, some fruit trees, vegetables, flowers and medicinal plants, as well as for livestock activities, mainly sheep, poultry, pigs and cattle. No more information was found on backyards in the state of Tlaxcala. The objective is to make an approximation of the composition of the backyard in Tlaxcala in terms of the plant and animal species produced and to describe some characteristics such as the size of the backyard area, and the percentages destined to self-consumption and sale of the production obtained, comparing these findings with those of other research on this agroecosystem. The results may be useful for the design of public policies to support rural inhabitants who manage these backyards, to reinforce their food security, referred by Lieffering, Newton, Vibart, and Li (quoted by Vargas-López et al., 2017), regarding species richness have as a challenge to cope with the seasonality of food, with times of excess and scarcity, as well as for experiential tourism ventures.

Materials and Methods

Database used

Since very little published information was found related to backyards in Tlaxcala, it was decided to use El Padrón de Productores Agropecuarios del estado de Tlaxcala, carried out by the National Institute of Statistics and Geography (INEGI) in 2004 at the request of the State Government; its objective was to obtain basic information on the agricultural and forestry sector, as well as to generate sample frames through which specific studies could be carried out by having a state inventory of land (social, public and common use property) (INEGI, 2004), as is the case of this research; as a member of the work team, a copy of the original database was obtained informally, which consisted of a total of 53 968 basic information cards.

Data used and backyard

The data from the basic information questionnaires was obtained from ejidatarios, communal landholders, small landowners, representatives of agricultural or forestry production groups or any person responsible for land adjacent to the dwelling with agricultural or forestry activity. Given that the complete database consists of 53 967 census Rural Production Units (RPUs), in order to analyze only those that corresponded to the backyard, we considered, first, the definition of Trabanino (2018), which states that "the family garden in Mesoamerica is an agroforestry system with an antiquity of more than 11 000 years; it is located in the surroundings of the domestic unit, it facilitates the care and access to plants without having to travel to the most distant mountains" (p.87); then, from the section land of the responsible person's dwelling, the first question was taken into account that says: between February and August last year, in the land where this dwelling is located, did you have or plant fruit trees or did you plant any crop? Thus, only those RPUs that reported any fruit tree or crop in the area planted next to their dwelling were considered as backyard. This is because both plant and animal species of commercial value are mostly found in backyard conditions, for safety reasons.

Plant and animal species

The reagent applied to find out if the farmer had a backyard area is shown in Figure 1. It was assumed that if the respondent answered yes to P0010101 and P0010202, for example, then he (her) had one or two plant species in the field, respectively.

Figure 1: Reagent to know if you have backyard surface area. Source: INEGI (2004).  

In the case of animal species, the item that indicated whether there were animal species in the backyard was: 7 Do you have or raise animals that sleep on the land where this dwelling is located? (P0070001), marking the answer with yes or no. As for other species, these were identified with item 18: On the land where this house is located, on January 31, did you have: 1. hens or chickens, 2. beehives, 3. other animals. This last item is important because working animals were found there.

Class intervals

To calculate the class intervals, the recommendation of Gorgas, Cardiel, and Zamorano (2011) was followed, "when the number of different values taken by the statistical variable is very large or the variable is continuous... the data are grouped into intervals and a count is made of the number of observations that fall into each interval". The lower and upper limits of the class intervals are shown in hectares.

Results and Discussion

Size of agricultural crop production units

According to the proposed methodology, 17 131 basic information forms (Rural Production Units, RPU) were used. In a first approximation of backyard size, class values were grouped from 1000 to 1000 m2; Table 1 shows that 93.6% have 1 to 10 000 m2 of backyard with crop production. This shows that more than 90% of the backyards in Tlaxcala are less than one hectare in size.

Table 1: Production units with backyard considering crop production. 

Number

L. limit

U. limit

Observations

RPU

%

1

0.0001

0.1

905

12540

76.14

2

0.1001

0.2

358

805

4.89

3

0.2001

0.3

225

693

4.21

4

0.3001

0.4

79

145

0.88

5

0.4001

0.5

49

368

2.23

6

0.5001

0.6

133

162

0.98

7

0.6001

0.7

29

43

0.26

8

0.7001

0.8

76

266

1.62

9

0.8001

0.9

36

47

0.29

10

0.9001

1

19

350

2.13

11

1.001

150

420

1050

6.38

 

Total RPU

16 469*

RPU = rural production units. * With 769 missing or skipped data.

Taking into account that Góngora and Pastrana (quoted by Castañeda, Lope, and Ordóñez, 2018), stated that the size of the orchards analyzed in the literature ranges from 48 m2 in Chemblas, Campeche, to 20 000 m2 in Catmís, Tzucacab, Yucatán, as well as Olvera, Álvarez, Aceves, and Guerrero (2017) reported for three communities in Puebla a backyard size between 300 to 20 000 m2, with an average of 2195 m2, taking into account the results shown in Table 1, the surface between 1 and 1000 m2 was analyzed with intervals of 100 to 100 m between classes.; the results are pointed out in Table 2.

Table 2: Production units with backyard considering crop production between one and 1000 square meters. 

Number

L. limit

U. limit

Observations

RPU

%

1

0.0001

0.01

99

5546

36.35

2

0.0101

0.02

100

1505

9.86

3

0.0201

0.03

100

2505

16.42

4

0.0301

0.04

100

3505

22.97

5

0.0401

0.05

95

633

4.15

6

0.0501

0.06

93

526

3.45

7

0.0601

0.07

92

322

2.11

8

0.0701

0.08

85

289

1.89

9

0.0801

0.09

76

195

1.28

10

0.0901

0.1

65

231

1.51

Total RPU

15 257

100.00

RPU = rural production units.

It is observed in Table 2 that the backyard of up to 400 m2 corresponds to 85.61% of the RPU, concerning 13 061 RPU out of 15 257 counted. When the average value of the range 0.0001 to 0.1000 hectares is obtained, the average area of the backyard is 0.0215 ha, it is, 215 m2; this is consistent with the 200 m2 size reported by CEDRSSA (2018) for backyard livestock in Mexico.

Plant species in agricultural crop production units

A total of 74 different plant species were detected in 17 131 backyards in Tlaxcala, when the responses referred to the first option. When they mentioned up to two different types of plants, or second option, 10 484 backyards were counted, when there were three species this was in 6 498; when four species were 3404 backyards and up to five species of plants, it was in 1586 backyards; clearly it is observed that the greatest diversity of plants is found in the least amount of these production units. Nine were the most common species: corn, peach, plum, pear, pecan nut, apple, lemon, apricot and fig. Their relative importance is related to the number of species in the backyard. Thus, when only one species was mentioned, corn was the most reported plant (33.67%, followed by peach with 20.29%). When two, three or four types of plants were mentioned, the most important were plum and peach (19.52 and 17.85%, respectively); when up to five species were mentioned, the most important were again maize and peach (13.38 and 12.93%, respectively). However, this does not mean that medicinal and ritual plant species are not found in the backyards; there was just a lack of interest in recording them. It is also important to clarify that agricultural crops are mainly established in rainfed conditions, both in the main plots and in the backyards. Figure 2 shows the main plant species present in Tlaxcala's backyard.

Figure 2: Plant species that are grown at tlaxcalteca backyard (%). 

Animal species in backyard production units in Tlaxcala

The main animal species that are produced in the backyard (mentioned as first option) are shown in Figure 3. It is observed that cattle and chickens, are the most produced, followed by sheep. It is important to mention that of 35 animal species, only 5 are not for human consumption (Figure 3). some species are companion such as dogs and birds. This result coincides with that reported by Castaños (quoted by López, Damian, Álvarez, Parra, and Zuluaga, 2012), in which the most abundant animal in the backyard are chickens. Also, according to the OECD (2018), chicken meat is one of the main sources of protein for the Mexican population. Aditionally, the average number of heads or units per Rural Production Unit for the main species were: 11.89, 4.31, 5.11, 13.01, 11.19, 19.22 and 16.62 for chickens, cattle, pigs, sheep, goats, rabbits and beehives, respectively, for the RPUs that had them.

Figure 3: Animal species that are grown at tlaxcalteca backyard. 

Other animals also important in the backyard are working animals and the turkey (endemic species of Mesoamerica) and ducks; they are mentioned as second, third, fourth and fifth option (Table 3). Horses, donkeys and mules are work animals, while the other two are for human consumption. The percentage that is reported corresponds to the RPU that mention these animal species. Table 3 shows the importance of donkeys, standing out as the third, fourth and fifth option in the "other animals", despite the fact that it is a species at risk of extinction, as stated by Germán Flores (Velasco, 2018). As for the turkey (huexolotl), Pérez (2002) calls it the king of the Mexican orchard.

Table 3: Backyard´s other animals (%). 

Option

Turkey

Horse Cattle

Donkey

Mule

Duck

Second

32.97

30.00

19.09

13.88

1.53

Third

10.64

27.99

35.00

20.33

2.14

Quarter

13.81

20.59

36.06

20.84

3.96

Fifth

17.52

17.52

42.34

12.41

5.11

%

18.74

24.03

33.12

16.87

3.19

It is also noteworthy that the greatest number of animal species is observed in the smaller backyards, i.e., their number and diversity decreases as the surface area of these agroecosystems increases; this was observed for the animal species shown in Figure 3.

Self-consumption-sales

Vegetable crops. It was found that 16 574 RPUs (95.23%) refused to sell the plant species or products produced, while 831 (4.77%) responded in the affirmative. This indicates, therefore, that approximately 5% of the RPUs that have a backyard sell plant species or products. (Table 4). It was also observed that in a backyard area of up to 1000 m2, 33.05% sell vegetable species or products, while 66.95% of those who sell have more than 1000 m2. This indicates that the smaller the surface area, the greater the self-consumption of agricultural production.

Table 4: Rural production units (RPU) that sell vegetable products. 

Class

L. Limit

U. Limit

Sell

Does not sell

Total RPU*

% Sell

% Does not sell

% Total RPU

1

0.0001

0.01

66

5480

5546

7.93

33.37

32.15

2

0.0101

0.02

36

3137

3173

4.33

19.10

18.39

3

0.0201

0.03

39

1479

1518

4.69

9.01

8.80

4

0.0301

0.04

35

828

863

4.21

5.04

5.00

5

0.0401

0.05

24

609

633

2.88

3.71

3.67

6

0.0501

0.06

20

506

526

2.40

3.08

3.05

7

0.0601

0.07

13

319

332

1.56

1.94

1.92

8

0.0701

0.08

13

276

289

1.56

1.68

1.68

9

0.0801

0.09

12

183

195

1.44

1.11

1.13

10

0.0901

0.1

17

214

231

2.04

1.30

1.34

11

0.10001

150

557

3390

3947

66.95

20.64

22.88

Total

832

16421

17253

100.00

100.00

100.00

* RPUs that do not report surface area in the backyard were omitted.

Animal products or species. Table 5 shows the Rural Production Units that sell animal products or species. It is observed that of the RPU that indicated they have a backyard surface and that have or raise animals, 12.93% sell products or species of animal origin, while 87.07% use it for self-consumption. It can be observed that unlike the RPUs that sell plant products, the RPUs that sell animal products are those with areas between 0.0001 and 0.1000 ha (73.7%). Note that 30.61% of Class 1 (0.0001 to 0.01 hectares) corresponds to 682 RPU out of a total of 2 228 RPU that sell products of animal origin. The low percentage of sales of vegetable and animal products, coincides with what was reported by Martínez and Juan (2005), López et al. (2012), Aznar and Carmona (2014), Covaleda, Paz, and Ranero (2016) and Suri (2020), in that backyard food production is mostly for self-consumption or survival.

Table 5: Rural production units (RPU) who sell cattle. 

Class

L. Limit

U. Limit

Sell

Does not sell

Total RPU

% Sell

% Does not sell

% Total RPU

1

0.0001

0.01

682

4864

5546

30.61

32.41

32.18

2

0.0101

0.02

419

2754

3173

18.81

18.35

18.41

3

0.0201

0.03

190

1328

1518

8.53

8.85

8.81

4

0.0301

0.04

103

760

863

4.62

5.06

5.01

5

0.0401

0.05

78

555

633

3.50

3.70

3.67

6

0.0501

0.06

63

463

526

2.83

3.09

3.05

7

0.0601

0.07

32

300

332

1.44

2.00

1.93

8

0.0701

0.08

23

266

289

1.03

1.77

1.68

9

0.0801

0.09

20

175

195

0.90

1.17

1.13

10

0.0901

0.1

31

200

231

1.39

1.33

1.34

11

0.10001

50.312

587

3343

3930

26.35

22.27

22.80

Total

2228

15008

17236

100.00

100.00

100.00

Table 6 shows the animals or products of animal origin that are most commercialized from the backyard of Tlaxcala. It is observed that the highest percentage of what is sold (of the little that is sold) is related to cows, female pigs and sheep, showing the importance of these species in the backyard of Tlaxcala. Regarding the animal species produced in the backyard, the results found coincide with those of García and Guzmán (2014), who found two types of livestock production units (producers), those of self-consumption (91%) whose production is for family sustenance and who also see backyard animals as a savings bank, and commercial units (9%) that sell the production obtained.

Table 6: Animals or animal products that are sold from the backyard of Tlaxcala. 

Animal

RPU

%

Accumulated percentage

Cow milk

2165

36.33

36.33

Pig female

1056

17.72

54.05

Sheep cattle

752

12.62

66.67

Calf

471

7.9

74.57

Cattle

299

5.02

79.59

Turkey

223

3.74

83.33

Cows

211

3.54

86.87

Goat cattle

152

2.55

89.42

Rabbit

118

1.98

91.4

Chicken

79

1.33

92.73

Bull

74

1.24

93.97

* RPUs that do not report surface area in the backyard were omitted.

Final considerations

As Rivera et al. (2013) and Ayala, Gutiérrez, and Zapata (2016) said, climate change is one of the most urgent issues on the world agenda and can affect the productivity of plant and animal species, requiring countries to adopt public policies to mitigate its causes and effects; the backyard is a useful strategy in this regard, by improving energy efficiency, reducing water consumption, planting many trees, reducing the use of gasoline-powered machinery, incorporating native species and incorporating organic waste from the home into the soil (National Wildlife Federation, n.d.).

Conclusions

The composition of the Tlaxcala backyard in terms of plant and animal species of some economic importance was determined. The characteristics of the size of the average backyard were described. It was also found that corn is the most important crop in this agroecosystem, only behind peaches; it was also found that cattle and chickens are the most important animals in the backyard, and that in both cases, only 8.8% of the backyards sell part of their production, which confirms their function of production for self-consumption, reported in most of the works on this agroecosystem. Given the current contingency due to the COVID-19 pandemic, the backyard agroecosystem or home garden should be stimulated to improve the diet and nutrition of the people of Tlaxcala. Additionally, the results reported here may be useful for other research that continues with the characterization of the structure, composition and functioning of the backyard in the state of Tlaxcala.

Ethics Statement

Not applicable.

Consent for Publication

Not applicable.

Data Availability

The data supporting the results of this study are available from INEGI, Tlaxcala, but there are restrictions on the availability of these data, which were used under license for this study and are therefore not publicly available. However, the data are available from the authors upon reasonable request and with the permission of INEGI, Tlaxcala.

Conflict of Interests

The author declare that he has no competing interests.

Literature Cited

Ayala C., M. del R., Gutiérrez V., V., & Zapata M., E. (2016). Género, cambio climático y REDD+: experiencias en el tiempo. Terra Latinoamericana, 34(1), 139-153. [ Links ]

Avendaño, J. C. (2020, Mayo 20). El 45.3 por ciento de la población tlaxcalteca se encuentra en pobreza laboral: Coneval. La Jornada de Oriente. Recuperado de https://www.lajornadadeoriente.com.mx/tlaxcala/el-45-3-por-ciento-de-la-poblacion-tlaxcalteca-se-encuentra-en-pobreza-laboral-coneval/Links ]

Aznar, J., & Carmona, R. (2014). La producción con fines de autoconsumo de las familias en El Levante Español. Relaciones de género y reparto de espacios. Actas Iberoamericanas de Conservación Animal, 4, 201-203. [ Links ]

Castañeda-Navarrete, J., Lope-Alzina, D. G., & Ordóñez D., M. J. (2018). Los huertos familiares en la península de Yucatán. En M. de J. Ordóñez Díaz (Coord.) (2018). Atlas biocultural de huertos familiares en México: Chiapas, Hidalgo, Oaxaca, Veracruz y península de Yucatán (pp. 331-389). México: Universidad Nacional Autónoma de México. https://doi.org/10.22201/crim.0000007p.2018 [ Links ]

CEDRSSA (Centro de Estudios para el Desarrollo Rural Sustentable y la Soberanía Alimentaria). (2018). La ganadería en ejidos y comunidades. Situación y perspectivas. Investigación interna. México: Cámara de Diputados LXIII Legislatura. [ Links ]

Chávez M. del C., J. C., Villarreal P., H. J., Cantú C., R., & González S., H. E. (2009). Efecto del incremento en el precio de los alimentos en la pobreza en México. El Trimestre Económico, 76(303), 775-805. [ Links ]

CONACYT (Consejo Nacional de Ciencia y Tecnología-Gobierno de Tlaxcala). (2010). Agenda de innovación de Tlaxcala. Resumen Ejecutivo. México: Concejo Nacional de Ciencia y Tecnología. Consultado el 18 de enero, 2021, desde Consultado el 18 de enero, 2021, desde http://www.agendasinnovacion.org/wp-content/uploads/2015/03/AgendaTlaxcala.pdfLinks ]

Covaleda, S., Paz, F., & Ranero, A. (2016). Carbono edáfico en Chiapas: planteamiento de políticas públicas de mitigación de emisiones. Terra Latinoamericana, 34(1), 97-112. [ Links ]

Damián H., M. A., Ramírez V., B., Parra I., F., Paredes S., J. A., Gil M., A., López O., J. F., & Cruz L., A. (2009). Estrategias de reproducción social de los productores de maíz de Tlaxcala. Estudios Sociales, 17(34), 111-146. [ Links ]

García F., A., & Guzmán G., E. (2014). La ganadería familiar, elemento cotidiano de los traspatios de la comunidad Juan Nepomuceno Álvarez, Copala, Guerrero, México. Sitientibus série Ciências Biológicas, 14(1), 1-11. https://doi.org/10.13102/scb282 [ Links ]

González J., A. (2004). Cultura y agricultura: transformaciones en el agro mexicano. México: Universidad Iberoamericana. ISBN: 9789688595176. [ Links ]

González J., A. (2006). El ambiente y la agricultura en Tlaxcala durante el Siglo XVI. Perspectivas Latinoamericanas, 3, 19‑46. [ Links ]

Gorgas G., J., Cardiel L., N., & Zamorano C., J. (2011). Estadística básica para estudiantes de ciencias. Universidad Complutense de Madrid. Consultado el 18 de enero, 2021, desde Consultado el 18 de enero, 2021, desde https://webs.ucm.es/info/Astrof/users/jaz/ESTADISTICA/libro_GCZ2009.pdfLinks ]

INEGI (Instituto Nacional de Estadística y Geografía). (2004). Reunión Nacional de geografía 2004. Memoria. En el camino…¡fortalecemos alianzas! Padrón de productores de Tlaxcala (pág. 187). México: INEGI. [ Links ]

INIFAP-SAGARPA (Instituto Nacional de Investigaciones Forestales, Agrícolas y Pecuarias-Secretaría de Agricultura, Ganadería, Desarrollo Rural, Pesca y Alimentación). (2015). Agenda Técnica Agrícola de Tlaxcala. Consultado el 07 de mayo, 2021, desde https://issuu.com/senasica/docs/29_tlaxcala_2015_sin [ Links ]

López G., J. L., Damian H., M. A., Álvarez G., F., Parra I., F., & Zuluaga S., G. P. (2012). La economía de traspatio como estrategia de supervivencia en San Nicolás de los Ranchos, Puebla, México. Revista de Geografía Agrícola, 48-49, 51‑62. [ Links ]

Martínez B., R., & Juan P., J. I. (2005). Los huertos, una estrategia para la subsistencia de las familias campesinas. Anales de Antropología, 39(2), 25-50. http://dx.doi.org/10.22201/iia.24486221e.2005.2.9966 [ Links ]

OECD (Organization for Economic Co-operation and Development). (2018). Market examinations in Mexico: Case study of the chicken meat market. Discharged from https://www.oecd.org/daf/competition/ENG-WEB-REPORT-Chicken-MeatMarketMexico2018.pdfLinks ]

Olvera-Hernández, J. I., Álvarez-Calderón, N. M., Aceves-Ruiz, E., & Guerrero-Rodríguez, J. de D. (2017). Perspectivas del traspatio y su importancia en la seguridad alimentaria. Agro productividad, 10(7), 39-45. [ Links ]

Pérez-San Vicente, G. (2003). Reflexiones y una teoría sobre la gastronomía mexicana. En Patrimonio cultural. Cuadernos. Congreso sobre patrimonio gastronómico y turismo cultural en América Latina y el Caribe. Memorias, Tomo I (pp. 79-96). México: CONACULTA. Consultado desde https://patrimonioculturalyturismo.cultura.gob.mx/publi/Cuadernos_19_num/cuaderno1_vol1.pdfLinks ]

Rivera S., M. del R., Nikolskii G., I., Castillo A., M., Ordaz Ch., V. M., Díaz P., G., & Guajardo P., R. A. (2013). Vulnerabilidad de la producción del café (Coffea arabica L.) al cambio climático global. Terra Latinoamericana, 31(4), 305-313. [ Links ]

SAGARPA (Secretaría de Agricultura, Ganadería, Desarrollo Rural, Pesca y Alimentación). (2018). Evaluación alianza para el campo 2005. Informe de Evaluación Estatal. Programa de Desarrollo Rural. Tlaxcala. Consultado el 07 de octubre, 2020, desde Consultado el 07 de octubre, 2020, desde https://www.agricultura.gob.mx/sites/default/files/sagarpa/document/2018/11/20/1561/20112018-2005-tlx-dr.pdfLinks ]

Suri, S. (2020). Nutrition gardens: a sustainable model for food security and diversity. ORF Issue Brief No. 369, June 2020, Observer Research Foundation. Accessed January 22, 2021, from Accessed January 22, 2021, from https://www.orfonline.org/wp-content/uploads/2020/06/ORF_Issue_Brief_369_Nutrition_Gardens.pdfLinks ]

Vargas-López, S., Bustamante-González, A., Vargas-Monter, J., Hernández-Zepeda, J. S., Vázquez-Martínez, I., & Calderón-Sánchez, F. (2017). Diversidad y prácticas de crianza de animales domésticos en traspatios de comunidades indígenas en Guerrero, México. Agro productividad, 10(7), 15-20. [ Links ]

Velasco, A. (2018, enero 26). El burro mexicano se extingue; es otro de los desplazados. Excelsior. Recuperado de https://www.excelsior.com.mx/nacional/2018/01/26/1094029Links ]

11 Fundación Produce Tlaxcala. (2011). Agenda de Innovación Tecnológica. Tlaxcala, México.

2Juárez T., M. (2015). https://www.banxico.org.mx/publications-and-press/banco-de-mexico-working-papers/%7B04AE64F6-9DAE-E817-37A4-EFD934A09152%7D.pdf

3Chávez Hernández, E. X. (2007). Transferencia y adopción de ecotecnias a nivel de traspatio en dos comunidades rurales de Tlaxcala. Tesis de Maestría. Colegio de Postgraduados, Montecillo, México. Discharged from February 18, 2020 http://colposdigital.colpos.mx:8080/jspui/bitstream/handle/10521/1457/Chavez_Hernandez_EX_MC_Desarrollo_Rural_2007.pdf?sequence=1&isAllowed=y

Received: February 15, 2021; Accepted: May 20, 2021

Corresponding author (mariaramirez.andres@coltlax.edu.mx)

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