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Recibido: 20-= 06-2021 / Revisado: 29-06-2021 / Aceptado: 18-07-2021 / Publicado: 05-08-2021<= /o:p>

 

Evaluación económica de los servicios ecosistémicos del recurso vegetal de la parroquia Punin, cantón Riobamba

DOI:  https://doi.org/10.33262/a= p.v3i3.1.87

 

Economic evaluatio= n of the ecosystem services of the plant resource of the pa= rroquia Punin, canton Riobamba

 

Marcela Yolanda Brito Mancero. [1], Landy Elizabeth Ruiz Mancer= o. [2] & Karina Viviana Lemache Velarde. [3]

 

<= o:p> 

= Abstract.       

Introduction: The valuation of ecosystem services is not new according to the Food and Agriculture Organization of the United Nations, it considers that ecosystem goods can be valued at 125 trillion USD, their maintenance or degradation h= as an impact on gains or losses of values ​​due to what is require= d to perform analysis and evaluations for development decision making. Punín is one of the rural parishes of the Riobamba ca= nton, its population amounts to 5,976 people and is divided into 23 communities t= hat are mostly recognized as indigenous, the productive economic activities are agriculture and livestock, a large part of the production is commercialized= and other part is used for self-consumption. Objective: To economically estimate the ecosystem services of the productive plant resource. Method= ology: An analysis of the perception of environmental services and the willingness= to pay for the conservation of the plant resource was carried out through the application of 359 in 8 communities selected by the criteria of number of inhabitants and agricultural production area, the inhabitants ranked the Ecosystem services using a Likert scale, the sociodemographic variables that affect the perception of environmental services were analyzed and the econo= mic value of the resource was estimated using the contingent method. Results= : The most valued ecosystem services are provisioning services, followed by support and regulation services that classify them as very important and cultural services as important. The age variable affects the perception of supporting ecosystem services. The calculated DAP is 5,393.63 USD / year, t= he value of direct use of the productive plant resource was established at 4,038,539.60 USD / year and the total economic value through the contingent method amounts to 4043933.23 USD / year. Conclusions: The variable l= evel of education significantly influences the perception of support services, possibly because this category of services is the most complex to distingui= sh. The TEV of the productive plant resource calculated using the contingent me= thod can vary according to the demand for the good in the market and the main products of the parish commercialization such as vegetables and tubers pres= ent constant price fluctuations in the market

Keywords: Ecosystem services, environmental services, <= span class=3DSpellE>economic valuation, environmental perception, parroquia Punín.

 

Resumen.

= Introducción: La valoración de los servicios ecosistémicos no es nueva según la Organización de las Naciones Unidas para= la Alimentación y la Agricultura, considera que los bienes ecosistémicos pueden valorarse en 125 billones de USD, su mantenimiento o degradación repercuten en ganancias o pérdidas de valores p= or lo que se requiere realizar análisis y evaluaciones para la toma de decisio= nes de desarrollo. Punín es una de las parroquias rurales del cantón Riobamba su población asciende a 5976 personas y se divide en 23 comunidades que se reconocen en su mayoría como indígenas, las actividades económicas productivas son la agricultura y la ganadería gran parte de la producción se comercializa y otra parte es utilizada en el autoconsumo. Objetivo: Estimar económicamente los servicios ecosistémicos del recurso vegetal productivo. Metodología: Se realizó un análisis de la percepción de = los servicios ambientales y la disposición a pagar por la conservación del recu= rso vegetal mediante la aplicación de 359 en 8 comunidades seleccionadas median= te los criterios de número de habitantes y área de producción agrícola, los habitantes jerarquizaron los servicios ecosistémicos utilizando una escala = de Likert, se analizó las variables sociodemográficas que inciden en la percep= ción de los servicios ambientales y se estimó el valor económico del recurso utilizando el método contingente. Resultados: Los servicios ecosistémicos más apreciados son los de aprovisionamiento, seguidos por servicios de soporte y regulación que los catalogan como muy importante y l= os servicios culturales como importante. La variable edad incide en la percepc= ión de los servicios ecosistémicos de soporte. El DAP calculado es de 5393,63 U= SD/ańo, el valor de uso directo del recurso vegetal de productivo se estableció en 4038539,60 USD/ańo y el Valor económico total mediante el método contingente asciende a 4043933,23 USD/ańo. Conclusiones: La variable nivel de educación influye significativamente en la percepción que presentan los servicios de soporte posiblemente porque esta categoría de servicios es la más compleja = de distinguir. La VET del recurso vegetal productivo calculada mediante el mét= odo contingente puede variar según la demanda del bien en el mercado y los principales productos de comercialización de la parroquia como las hortaliz= as y tubérculos presentan fluctuaciones constantes de precios en el mercado.

P= alabras claves: Servicios ecosistémicos, servicios ambientales, valoración económica, percepción ambiental, parroquia Punín.

 

Intro= ducción.

La Clasificación Internacional Común de Servicios de los Ecosistemas reconoce = que las  principales categorías de bien= es y servicios de los ecosistemas son los servicios de aprovisionamiento, de regulación y culturales<= span style=3D'mso-bookmark:_Hlk80710300'> (Haines-Young & Potschin-Young, 2018); los cuales al proveer alimentos y  agua para el consumo, energía y  control  microclimas, permitir acciones co= mo la polinización y formación de suelos y al ofrecer beneficios recreativos permiten el desarrollo d= e la vida humana. (Life adaptamed, 201= 8)

La valoración de los servicios ecosistémicos no es nueva según la Organización de las Naciones Unidas para la Alimentación y la Agricultura, = considera que los bienes ecosistémicos pueden llegar a valorarse en 125 billones de U= SD pero que no han recibido el cuidado necesario en el ámbito económi= co, ambiental ni legal. (FAO, 2021). El mantenimiento o degradación de los recursos naturales repercute= n en ganancias o pérdidas de valores por lo que se requiere realizar análisis y evaluaciones como instrumentos para la toma de decisiones complejas que exi= ge el cuidado de los recursos naturales. (Barbier, Acreman, & Knowler, 1997)<= span style=3D'mso-bookmark:_Hlk80710300'>.

El Recurso vegetal presta variados beneficios sociales como la regulación de pr= ocesos micro climáticos, provisión de alime= ntos y medicinas, y el uso en aspectos espirituales y culturales de la población l= os cuales no siempre son percibid= os o reconocidos por los poblador= es y autoridades. Aunque no todo son efectos son positivos, también se puede advertir algunas problemáticas como en el caso de la agricultura, en la búsqueda del incremento de la productividad con el incorrecto uso de plaguicidas puede conllevar la disminución de la polinización natural, y afeccione= s al recurso suelo, la deforestación aumenta el riesgo de deslizamientos e inundaciones. (Lemache,= 2021)

Punín es una de las parroquias rurales del cantón Riobamba su poblaci= ón asciende a 5976 personas y se divide en 23 comunidades de las cuales 22 se = reconocen como indígenas y la cabecera parroquial como mestiza. (INEC, 20= 21).

Las actividades económicas productivas son la agricultura y la ganade= ría, la agricultura es muy diversa entre los principales cultivos existen gramín= eas tales como maíz, cebada, vicia, trigo, avena, hortalizas como el haba, las = papas, el tomate rińón, el pimiento, frutas por ejemplo mora y frutilla y producto= s andinos como quinua, chochos, oca y melloco. (GADPR PU= NÍN, 2015) La mayor parte de la producció= n está dedicada a la comercialización y otra parte para el autoconsumo. En lo referente a la ganadería existe una gran variedad de especies pecuarias com= o el ganado ovino, porcinos, aves y especies menores como cuyes y conejos que generalmente se lleva cabo de forma extensiva, se establecen en los patios = de las casas y su abono es utilizado directamente las parcelas de tierra sin p= revio tratamiento generalmente. (Rodrigue= z, Herrera, & Ruiz, 2014)

Metodologia.

Área de estudio.

La parroquia rural de Punín cuenta con una poblaci= ón es de 5976 habitantes (INEC, 2001), divididas en 23 comunidades, se ubica a= 12 Km al Sur de la ciudad de Riobamba en la vía a Macas, tiene una extensión d= e 52 Km2, limita al norte con la parroquia San Luis, al sur con la parroquia Flo= res, al este con la quebrada Guaslán de parroquia Li= cto y al oeste limita el cantón Colta. La altitud media de la parroquia es 2.800 m.s.n.m. su área se divide en tres zonas, zona baja que va de 2.720 a 2.950 m.s.n.m.; la zona media de 2.900 a 3.380 m.s.n.m. y zona alta de 3.400 a 3.= 500 m.s.n.m. (GADPR PUNÍN, 2015).

Figura 1

Límites de la parroquia rural de Punín


Elaboración: Los Autores

Según la clasificación ecológica gran parte del territorio de Punin se ubica como bosque seco – Montano Bajo (bs-MB) y las formaciones ecológicas de la zona media se encue= ntra en la zona de vida estepa espinoso montana Baja (eeMB<= /span>). En lo referente al clima las temperaturas que van de 12°C a 18°C, con una precipitación media de 500 mm anuales y una velocidad de viento promedio de 4m/s. (GADPR PUNÍN, 2015).

 

Selección de muestra

Para determinar la selección de la mue= stra se consideró las comunidades con mayor superficie de suelos cultivados, disponibilidad de recursos, facilidad del acceso y número de habitantes por comunida= d por lo que se seleccionaron 8 de las 24 comunidades que posee la parroquia, para la selección del tamańo de la población se utilizó la fórmula de Canavos (1998), el número de encuestas aplicadas p= ara a los 5976 habitantes fue de 359 se detalla en la tabla 1.<= /p>

<= span style=3D'font-size:10.0pt;line-height:115%;font-family:"Arial",sans-serif'>= Tabla 1

<= span style=3D'font-size:10.0pt;line-height:115%;font-family:"Arial",sans-serif'>= Distribución de encuestas por comunidad

<= span style=3D'font-size:10.0pt;line-height:115%;font-family:"Arial",sans-serif'>=  

No

Comunidad

No. Encuestas

1

Cabecera Parroquial

43

2

Gulalag

30

3

San Antonio de Bas= halan

23

4

San Isidro

105

5

San Pedro de Pulsh= i

23

6

Santa Bárbara

42

7

Siguilan<= /span>

57

8

Tzalaron<= /span>

36

 

TOTAL

359

<= b>= Fuente:= (Lemache, 2021)<= !--[if supportFields]>

= Colección de los datos

Las fuentes de información para= el presente trabajo fue la revisión bibliográfica del plan de ordenamiento territorial de la parroquia Punin, la informaci= ón del INEC, consulta a las partes interesadas identificadas que fueron: el presid= ente de la junta parroquial, los moradores de las comunidades y funcionarios del= ministerio de Agricultura; y encuestas a los pobladores de las comunidades seleccionad= as.

Los datos utilizados tienen dos enfoques, el cuantitativo que proviene de la aplicación de encuestas y levantamiento de la información de costos de producción del recurso vegetal mediante la información del sistema        =     único   de información agropecuaria para 2020 y= un enfoque cualitativo resultante de la caracterización de los servicios ecosistémicos brindados por el recurso vegetal del sitio en análisis.  

Clasificación de los servicios ecosistémicos<= /o:p>

La identificación y jerarquización de los servicios ecosistémicos se la realizó mediante la aplicación de encuestas donde se utilizó una escala de Likert donde los habitantes encuestados evaluaron los servicios utilizando los criterios detallados en la tabla 2.

También se relaciona las variables socioeconómicas= que inciden en la percepción de los servicios ambientales del recurso vegetal

= Tabla 2

Escala de valoración de los servicios ecosistémicos.

=  

CRITERIO<= o:p>

No me llama la atención

Nada importante

Poco importante

Importante

Muy importante

ESCALA

0 - 2

2 -4

4 -6

6 - 8

8 -10

Fuente: (Lemache, 2021)

Valoración económica

Para establecer el Valor económico total (VET) se realizó el análisis de los componentes del v= alor de uso y no uso, mediante la estimación del valor total de los bienes y servicios que provee el recurso vegetal y la disposición a pagar (DAP) por = la conservación y el manejo del recurso vegetal productivo en la parroquia. (Baral, Basnyat, Khanal, & Gauli, 2016)

Resultados.

= Estimación ambiental de los servicios ecosistémicos del recurso vegetal

Tabla 3

Valores medios de los servicios ecosistémico estimado por comunidad.

 <= /p>

=  

=  

=  

=  

=  

=  

=  

=  

= Fuente: (Lem= ache, 2021)

=  

=  

=  

Gráfico 1

 Promedios ponderados por servicios ecosistémico= s

 

Fuente: (Lem= ache, 2021)

En la tabla 3 y gráfica 1 se pu= ede observar que la apreciación de los servicios ecosistémicos sigue el siguien= te orden: servicios de abastecimiento, servicios de regulación, servicios de s= oporte y finalmente servicios culturales, lo que se asemeja a resultados anteriore= s en donde han encontrado que la preferencia de los SE están orientan a los servicios de provisión, seguidos por los de regulación y culturales (Agbenyega, Burgess, Co= ok, & J., 2009).

en los pobladores de la parroqu= ia de Punín tienen una alta percepción sobre servicios ecosistémicos brindados po= r el recurso vegetal esto confirma lo dicho por (Martín-López, y otros,= 2021) que establece = que las poblaciones rurales identifican con mayor frecuencia los servicios de abastecimiento, siendo este el  ser= vicio mejor puntuado en la cabecera cantonal el abastecimiento en provisión de alimentos de origen vegetal con 9 que corresponde a muy importante, según lo manifestado por los pobladores esto se debe a que la producción de alimentos está destinada a la comercializa= ción y cierta parte para el autoconsumo, además que la agricultura y la ganadería so= n las actividades económicas de la mayor parte de los encuestados, lo que coincid= e con estudios similares realizados en la provincia de Chimborazo y el cantón Riobamba lo seńalado por (Moreta, 2018) (Carrasco, 2019)= (Mayanquer, 2019) (Collaguazo, 2019). Por otra parte los servicios culturales obtuvieron la menor puntuación, en San Antonio de Bashalan el servi= cio de paisaje obtuvo una estimación de 7 que en la escala evaluada corresponde a importante, esto podría explicarse por qué los servicios culturales son los menos tangibles según lo establece = (Daniel, y= otros, 2012).

 

= Relación de las características sociodemográficas = con la percepción de los servicios ecosistémicos

 

 

 

 

Tabla 4

Características sociodemográficas de la población encuestada en la parroquia Punín

Características

Variables

Porcentaje

Género

Hombre

52,33%

Mujer

47,67%

Estado Civil

Soltero

21,09%

Unión lib= re

5,21%

Casado

56,16%

Divorciad= o

3,86%

Viudo

13,70%

Edad

Menor a 30 ańos

21,37%

31 -60 ań= os

49,03%

Mayor 60 = ańos

29,60%

Nivel de Educación

Primaria incompleta

42,47%

Primaria completa

19,45%

Secundari= a incompleta

22,46%

Secundaria completa

11,51%

Tercer ni= vel incompleto

2,47%

Tercer ni= vel completo

1,64%

Ocupación

Ama de ca= sa

18,90%

Empleado<= o:p>

20,82%

Independi= ente

45,21%

desemplea= do

5,21%

Estudiant= e

6,85%

Jubilado<= o:p>

3,01%

Ingresos

Menor a 3= 94 dólares

79,18%

394 - 788 dólares

15,33%

778 a 1182 dólares

4,94%

1000 a 20= 00 dólares

0,55%

Fuente: (Lemache, 2021)

= Tabla 5:

Variables sociodemográficas que inciden en la apreciación de los servicios ecosistémicos.

VARIABLES

SA

SR

SS

SC

GÉNERO

0,494161407

0,0679139

0,12646346

0,71003418

EDAD=

0,226413711

0,844651885

0,080610946

0,533298735

ESTADO CI= VÍL

0,478803102

0,95142534

0,201805247

0,715504718

NIVEL DE EDUCACIÓN

0,826297308

0,581506384

0,025230813*

0,062830655

INGRESOS MENSUALES

0,884807128

0,221386125

0,166306905

0,195929009

OCUPACIÓN

0,909401313

0,375177373

0,375177373

0,310836668

* Valor de P <0,05<= /b>

Fuente: (Lemache, 2021)

La relación entre la variable nivel de educación con respecto a los servicios ecosistémicos de soporte presentan una inferencia significativa en comparación a relación del resto de variables con los servicios de abastecimiento, regulación y culturales esto se puede explicar por lo establecido por (Poppenborg & Koell= ner, 2013) quienes indican que la educación presenta una influencia positiva en relación a la comprensión de los servicios de regulaci= ón y apoyo.

Valor de uso directo recurso vegetal productivo<= /i>

ˇ&nb= sp;        Valoración del recurso vegetal productivo

=  

= Tabla 6

Producción del recurso vegetal parroquia Punín.

 <= /p>

=  

 

 

 

 

 

 

 

 

 

 

 

 

Fuente: (GAD= PR PUNÍN, 2015) (SIPA, 2020)

Elaboración: (Lem= ache, 2021)

En el sistema de Información pú= blica agropecuaria se puedo obtener los valores comerciales de productos convencionales tales como la papa, el maíz, el tomate, entre otros; mientras que productos dedicados en mayor parte al autoconsumo como la oca y la vici= a no constan el portal de información por lo que fue necesario recurrir a los precios directos de mercado.

Dentro del cuadro de producción= se puede analizar que el tomate rińón es el cultivo que mayor utilidad represe= nta a los productores, este dato se asemeja a lo establecido en estudios simila= res realizado en las parroquias rurales del cantón Riobamba donde indican que el tomate rińón es el cultivo más rentable (Collaguazo, 2019), seguido por la= papa y el maíz. Los cultivos andinos como chocho, quinua, melloco y oca se encuentran dentro de los productos en que la utilidad es negativa esto puede estar sujeto a que estos cultivos por tradición han formado parte del siste= ma agrícola de los productores de auto subsistencia y que generalmente al mercado llegan los excedentes. (Nieto, y otros, 2016)

ˇ         Disposición a pagar por la conservación del recurso vegetal

 

= Tabla 7: Disposición a pagar.

DAP = USD/AŃO

HABITANTES

PROMEDIO

(Hab/familia)

NÚMERO DE USUARIOS

DAP TOTAL USD/AŃO

10,64<= /p>

3932

3,7

1063

5393,63

Fuente: (Lemache, 2021)

<= i> 

Gráfico= 2

Disposi= ción a pagar por la conservación del recurso vegetal

&n= bsp;

Fuente: (Lemache, 2021)

En cuanto a la DAP el 48% de la población dispuesta a pagar contribuirían con un valor de 10,64 UDS al ańo = lo que resultaría un valor de 5393,63 USD al ańo. En lo referente a la poblaci= ón que no está dispuesta a pagar el 52,33% indica que la principal razón indica que a que su bajo nivel de ingreso limitante que esta seńalada en el docume= nto Métodos de valoración económica de los servicios ambientales. (Cristeche & Penna,= 2008).

ˇ      =    Valor económico total (VET)

=  

=  

=  

 

Tabla 8

Cálculo de la valoración económica del recurso vegetal por el método contingente= .

&= nbsp;

MÉTODO DE VALORACIÓN

USD ANUAL

VALOR DE USO DIRECTO (Valor del recurso vegetal productivo)

4038539,597

DAP ANUAL

5393,63

VET

4043933,227

Fuente: (Lemache, 2021)

El cálculo del VET por el métod= o contingente permite calcular el valor total del bien empleando datos de valor de uso del recurso vegetal productivo que esta en función = de la demanda del bien en el mercado (Cristeche & Penna,= 2008) que en este ca= so es muy fluctuante por lo que estos datos pueden estar sujetos a la variación d= el mercado. El recurso vegetal productivo de la parroquia Punín se calcula en 4043933,227 USD  al ańo el cual debería destinarse a actividades de tanto de conservación como = de recuperación del recurso (Laurans, Rankovic, Bil= lé, Pirard, & Mermet, 2013) proponen que el valor económico total de los bienes y servicios deben utilizarse en propósi= tos relevantes a implementación de políticas informativas, y técnicas de conservación de los recursos.

Conclusiones.

ˇ      =    La población de la parroquia rural de Punín muestra una buena percepción de los servicios ecosistémicos del recurso productivo vegetal, el orden de jerarquización de los mismos fue en primer lugar los servicios de abastecimiento, seguido por los servicios de regulación, soporte que los catalogaron como muy importante y finalmente los servicios culturales fueron clasificados como importantes.

ˇ      =    La variable nivel de educación influye significativamente en la percepción que presentan los servicios de soporte posiblemente porque esta categoría de servicios es la más compleja de distinguir.

ˇ      =    La valoración económica del recurso vegetal productivo calculada mediante el método contingente puede variar según la demanda del bien en el mercado y l= os principales productos de comercialización de la parroquia como las hortaliz= as y tubérculos presentan fluctuaciones constantes de precios en el mercado, por= lo que el VET puede verse modificado por esta variable.

ˇ      =    La principal razón por la cual los pobladores de la parroquia Punín no present= an disposición a pagar por la conservación del recurso se debe a que sus ingre= sos son muy limitados.

 

Referencias=

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Barbier, E., Acreman, M., & Knowler, D. (1997). Economic valu= ation of Wetlands. Ramsar convention Bureau department of environmental economics and environmental management, University of York institute of hydrology IUCN-the world conservation union, Switzerland.

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Collaguazo, C. (2019). Valoración económica ambiental del recurso vegetal productivo de la parroquia San Luis, cantón Riobamba, provincia de Chimborazo. Trabajo de titulación presentado para obtar por el grado académico de Ingeniera en Biotecnología Ambiental. Retrieved from http://dspace.espoch.edu.ec/bitstream/123456789/13799/1/236T0476.pdf=

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GADPR PUNÍN. (2015). PLAN DE DESARROLLO Y ORDENAMIENTO TERRITORIAL 2015-2019. Retrieved from http://app.sni.gob.ec/sni-link/sni/PORTAL_SNI/data_sigad_plus/sigadplusdo= cumentofinal/0660821640001_PDOT%20PUNIN%202015-2019(reformado)_28-06-2016_2= 2-41-43.pdf

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Laurans, Y., Rankovic, A., Billé, R., Pirard, R., & Mermet, L. (2013). Use of ecosystem services economic valuation for decision making: Questioning a literature blindspot. Journal of Environmental Managemen= t, 208 - 219. doi:https://doi.org/10.1016/j.jenvman.2013.01.008.<= /span>

Lemache, K. (2021). Valoración económica ambiental del recurso vegetal de la parroquia Punin. Riobamba: ESPOCH. Retrieved from http://dspace.espoch.edu.ec/bitstream/123456789/14524/1/236T0515.pdf=

Life adaptamed. (2018). Qué son los servicios ecosistémicos y cómo podemos beneficiarnos de ellos. Retrieved from https://www.lifeadaptamed.eu/?p=3D1113

Martín-López, B., Iniesta-Arandia, I., García-Llorente, M., Palomo, = I., Casado-Arzuaga, I., García del Amo, D., . . . Palacios, I. (2021). Uncovering ecosystem service bundles through social. PloS One. doi:https://doi.org/10.1371/journal.pone.0038970

Mayanquer, P. (2019). Valoración económica ambiental del recurso vegetal productivo de la comunidad de San Nicolás de la parroquia de Lict= o. Riobamba: Escuela Superior Politécnica de Chimborazo. Retrieved from http://dspace.espoch.edu.ec/handle/123456789/13204

Moreta, M. (2018). Valoración Economica Ambiental del recurso veg= etal en la parroquia San Juan, cantón Riobamba. Trabajo de titulación presentado para obtar por el grado académico de Ingeniera en Biotecnología Ambiental, Riobamba. Retrieved from http://dspace.espoch.edu.ec/bitstream/123456789/10556/1/236T0415.pdf=

Nieto, C., Ańazco, M., Hidrobo, G., Flor, E., Nieto, M., Borrero, J.= T., & Paredes, N. (2016). Informe nacional sobre el estado de la Biodi= versidad para la alimentación y la agricultura en el Ecuador. Quito. doi:http://www.fao.org/3/CA3493ES/ca3493es.pdf

Poppenborg, P., & Koellner, T. (2013). Do attitudes toward ecosy= stem services determine agricultural land use practices? An analysis of farmer= s’ decision-making in a South Korean watershed. Land Use Policy, 422 - 429. doi:https://doi.org/10.1016/j.landusepol.2012.08.007

Rodriguez, N., Herrera, S., & Ruiz, R. (2014). Plan de desarrollo turístico comunitario en la parroquia Punín, cantón Riobamba, provincia de Chombora= zo. Quito: UCE. Retrieved from http://www.dspace.uce.edu.ec/handle/25000/3065

SIPA. (2020). Sistema de Información Pública Agropecuria. Retrieved from http://sipa.agricultura.gob.ec/

 

 

 

 

PARA CITAR EL ARTÍCULO INDEXADO.

 

 

Brito Mance= ro, M. Y., Ruiz Mancero, L. E., & Lemache Velarde, K. V. (2021). Evaluación económica de los servicios ecosistémicos = del recurso vegetal de la parroquia Punin, cantón <= span class=3DGramE>Riobamba . AlfaPublicaciones, 3(3.1), 188–201. https://= doi.org/10.33262/ap.v3i3.1.87

=  

 

 

 

 

El artículo que se publica es de exclusiva responsabilid= ad de los autores y no necesariamente reflejan el pensamiento de la Revista Alfa Publicaciones.

 

El artículo qu= eda en propiedad de la revista y, por tanto, su publicación parcial y/o total en otro medio tiene que ser autorizado por el director de la Revista Alfa Publicaciones.

 

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[1] Escue= la Superior Politécnica de Chimborazo, Facultad de Recursos Naturales. Riobamb= a, Ecuador. mybrito@e= spoch.edu.ec, https://orcid.org/0000-0003-2689-3516

[2] Escue= la Superior Politécnica de Chimborazo, Facultad de Informática y Electrónica. Riobamba, Ecuador. lruiz@esp= och.edu.ec, https://orcid.org/0000-0003-1818-1084

[3] Inves= tigador independiente en el área, karilv90@hotmail= .com, https://orcid.org/0000-0002-7828-6331.

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Alpha publicaciones<= o:p>

ISSN: 2773-7330=                                                 =                        Vol. 3, 3.1, p. 188-201

=                                                       =                                                                    agosto, 2021

 

Educación Superior                                                =                                                            =                              Página 171

 

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