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Estimación de los servicios ecosistémicos del recurso vegetal de la parroquia Flores, cantón Riobamba

 

Estimation of the ecosystem services of the vegetable resource of the pa= rroquia Flores, cantón Riobamba

 

Marcela Yolanda Brito Mancero. [1] <= /span>& Nataly Alexandra Garcés Chérres. [2]

 

 

Recibido: 15-06-2021 / Revisado: 25-06-2021 /Aceptado: 13-07-2021/ Publicado: 05-08-2= 021

 

= Abstract.                                      DOI: https://doi= .org/10.33262/concienciadigital.v4i3.1.1817

Introduction. The SE are benefits t= hat nature produces for the welfare of humanity, the plant resource is recogniz= ed mainly because it provides food and is related to ancestral knowledge. O= bjective. Estimate the economic value of the productive plant resource of the parroquia Flores. Methodology. The characteris= tics of the area, sociodemographic variables around the vegetable resource were qualitatively analyzed, the total income received by the producers (vegetab= le, forest and pastures) was calculated from the average yields and production costs for the vegetable resource, in order to the forest resource and grasslands were estimated from market prices. The contingent value method w= as used, 350 people from 4 communities of the parish were surveyed under a hyp= othetical scenario of conservation of the plant resource, the willingness to pay of t= he users was estimated. Results. The age variable, for provisioning services, this service was the best scored with a value of 9.2 / 10, this v= alue indicates that users value tangible services more, that generate benefits, = the least valued service was that of ancestral practices with a value of (5,6). Regarding the Willingness to pay, most of the users (85%), would not be wil= ling to cancel because they attribute the responsibility for conservation to the government, 15% are willing to pay $ 10.20 per year. The total environmental economic value of the productive plant resource calculated was $ 724,730.63= , a variable value around the time of year or other external. Conclusions. The supply services in the provision of food were the most appreciated, the least valued were the cultural services in ancestral rituals. The sociodemographic variable of age affects the assessment of both supply and cultural services. In the VET, pasture production obtained the best valuati= on followed by forests and finally agricultural production since this is margi= nal and poor with little investment and irrigation deficiency.

Keywords: Ecosystem services, environmental services, environmental economy, environmental assessment, parroquia Flores.

 

Resumen.

Introducción. Los SE son beneficios que la naturaleza produce = para bienestar de la humanidad, el recurso vegetal es reconocido principalmente porque proporciona alimentos y se relacionada con los saberes ancestrales. = Objetivo.  Estimar el valor económico del recurso vegetal productivo de la parroquia Flores. Metodología. Se analizó cualitativamente las características de la zona, variables sociodemográfica= s en torno al recurso vegetal, se calculó los ingresos totales que perciben los productores (vegetal, forestal y pastos) a partir de los rendimientos prome= dio y los costos de producción para el recurso vegetal, para el recurso foresta= l y pastizales se estimaron partir de precios de mercado. Se utilizó el método = de valor contingente, se encuestaron a 350 personas de 4 comunidades de la parroquia bajo un escenario hipotético de conservación del recurso vegetal,= se estimó la disposición a pagar de los usuarios. Resultados. La variab= le edad, para los servicios de aprovisionamiento, este servicio fue el mejor puntuado con un valor de 9,2/10, este valor indica que los usuarios valoran= más los servicios tangibles, que les generen beneficios, el servicio menos valo= rado fue el de prácticas ancestrales con un valor de (5,6). En lo referente a la Disposición a pagar, la mayor parte de los usuarios (85%), no estarían dispuestos a cancelar pues atribuyen la responsabilidad de la conservación = al gobierno el 15% está dispuesto a pagar $ 10,20 anual.    El valor económico ambiental total del recurso vegetal productivo calculado fue $ 724.730,63, valor variable en to= rno a la época del ańo u otros factores externos. Conclusiones. Los Servicios de abastecimiento en el aprovisionamiento de alimentos fuero los = más apreciados, los de menor valoración fueron los servicios culturales en ritu= ales ancestrales. La variable sociodemográfica de la edad incide en la valoració= n de los servicios tanto de abastecimiento como culturales. En la VET la producc= ión de pasto obtuvo la mejor valoración seguido por bosques y finalmente la producción agrícola ya que esta es marginal y pobre con poca inversión y deficiencia de riego.

Palabras claves: Servicios ecosistémicos, = servicios ambientales, economía ambiental, valoración ambiental, parroquia Flores.

Intro= ducción.

La reducción de los servicios ecosistémicos desempeńa un papel clave= en el grupo de fenómenos que se denomina crisis ecológica global. La explosión demográfica ha resultado en una sobrepoblación de nuestro planeta. (Hufna= gel, et al, 2018)

Para Hufnagel (2018), el deterioro de las condiciones ecológicas ha causado problemas sociales directa e indirectamen= te, como epidemias, pobreza y crisis humanitarias. Además de estas, las activid= ades económicas contaminantes que destruyen la naturaleza aumentan la riqueza y = la desigualdad de ingresos entre las personas, lo que resulta en más tensiones sociales (crimen, terrorismo, disturbios y guerras).

La situación de Ecuador se ha visto amenazada como resultados de más de quinientos ańos de sobrexplotación de los recursos naturales y excesiva emanación de sustancias contaminantes al ambiente. Es de vital importancia conservar y restaurar los ecosistemas para que provean los bienes y servicios de calidad a las generaciones. (Ministerio del Ambiente-Ecu= ador, 2016)

La cobertura de suelos indica que el 75,10% pertenece a bosques secundarios, de la misma manera esta cobertura presenta degradación debido = a la quema, y las condiciones económicas de la zona.

La actividad agro productiva de la parroquia Flores presenta complejas relaciones debido a la carencia del sistema riego, dando un lugar a suelos infértiles y erosionados que generan baja producción agropecuaria y conllevan a una baja condición socioeconómica baja. (GADPR- Flores, 2015)

La producción es mayormente orgánica lo que aporta a la soberanía alimentaria, uno de los problemas que enfrenta Flores es que los usuarios prefieren consumir alimen= tos de afuera como enlatados, harinas, arroz, entre otros. (GADPR- Flores, 2015)

El bajo rendimien= to de la producción agrícola se le atribuye a las condiciones climáticas 57,14% en sequias, el 42,86% para heladas, además de= que en la parroquia predomina el minifundio, dando como resultado una agricultu= ra de subsistencia que condiciona la actividad económica de sus pobladores. (GADPR- Flores, 2015)

Calcular el valor económico ambiental del recurso vegetal podría contribuir positivamente a la sociedad, ya que muestra los costos que serían causados ​​por la pérdida de biodiversidad y la degradación de los ecosistemas de la parroqui= a a su vez fomenta una gestión más eficiente que permite una mejor conservación= y protección de los activos ambientales y evita su degradación.

Metodología.=

La investigación realizada es de tipo Descriptiva Partiendo de la caracterización de los componentes   de la parroquia Flore= s que inciden en la valoración del recurso vegetal productivo, transversal en el = ańo 2020 y correlacional que relaciona variables significativas que tengan rela= ción con los servicios ecosistémicos en estudio.

La población de estudio fue los habitantes de la Parroquia Flores que es de 5548 y las espe= cies vegetales que hay en ella. Para la determinación del tamańo de la muestra se utilizó la fórmula de Canavos (1998), que dio c= omo resultado 325 encuestas realizadas, para la definición de las unidades de estudio se revisó la información disponible del Plan de Ordenamiento territorial parroquial   y se estab= leció 4 comunidades Naubug, Capiatá, Guantual Grande central y Puesetus Grande, según los parámetros de números de habitantes y producción.

En cuanto a la identificación de variables se trabajó con las características sociodemográficas de los habitantes de Flores como variable independiente y variable dependiente la valoración económica de los recursos vegetales de la parroquia Flores.

En cuanto a las técnicas de recolección de datos, para la caracterización de la zona de est= udio se utilizó la revisión bibliográfica de documentación del Plan de ordenamie= nto territorial vigente, datos del instituto nacional de estadísticas y censos (INEC), la técnica de consulta a las partes interesadas identificadas las cuales fueron: representantes del gobierno autónomo descentralizado de la parroquia rural Flores, productores de la parroquia, representantes del ministerio de agricultura y ganadería y representantes de organizaciones de= la comunidad. La técnica de encuesta a los pobladores estuvo distribuida en tr= es secciones: componente social, componente ambiental con el escenario de conservación del recurso vegetal productivo y el componente monetario con la disposición a pagar.

Para la valoración ambiental de los servicios ecosistémicos se utilizó la escala de Likert don= de los pobladores entrevistados quienes apreciaron los servicios en una escala= de 1 a 10. Para la información acerca del recurso vegetal se utilizó datos de = la población económicamente activa (PEA), principales actividades económicas, principales productos, problemática ambiental, bienes y servicios ambiental= es e información cartográfica de la zona de estudio del Ministerio de agricultur= a y ganadería.

La técnica para evaluar económica y ambientalmente el recurso vegetal fue mediante la aplicación del método de valor contingente de valoración económica.

Figura 1: Componentes del Valor económico toral (VET)

Elaboración: Los autores

Valor real de producción vegetal para lo cual se realizó la diferencia entre los precios = de mercado de los principales recursos vegetales con el costo de producción de= los mismos, el valor de bosque que se identificó mediante las licencias foresta= les y el valor del pasto se identificó directamente con los encuestados en sus precios locales. La disposición a pagar DAP se determinó a través del escen= ario hipotético de conservación que los usuarios enunciaron.

 

Resultados.

Caracterización de la zona de estudio

Figura 2: Límites de la parroquia Flores

<= /p>

Elaboración: Nataly Garcés (2020)

 

Ubicación de la parroquia Flores:= La parroquia Flores se encuentra ubicada en el cantón Riobamba, Provincia de Chimborazo en una altitud que varía de 2840m -3555 msnm, sus límites son:  al norte por la parroquia Punín, al sur= la matriz de Guamote y Cebadas, al este la parroquia Licto, al oeste las parroquias de Columbe y Punín. Las coordenadas = GPS de la parroquia Flores son: latitud: -1.8 y longitud: -78.6333.

Clima: Flores posee un clima frio con temperaturas que oscilan de 100 C a 16 0 C, y una media de 110 C, la precipitación se encuentra e= ntre 500 mm a 1250 mm al ańo, se observa la presencia de vientos fuertes en vera= no sobre todo en el mes de agosto, las heladas se presentan en <= span style=3D'mso-bookmark:_Toc41329198'>los meses de mayo, agosto y diciembre; nebli= nas en abril y sequías en de junio y diciembre. (GADPR- Flores, 2015)

Suelo: Los presentan pendientes suaves de hasta 25%, pendientes fuertes de 40 a 70% y muy fuertes c= on más del 70%. pH que va de 4,5 extremadamente ácido a 7 neutro. Las texturas presentes son variables se encuentra suelos francos, franco limoso, francos arcillosos y texturas gruesas. CITATION PDy15 \l 12298  (GADPR- Flores, 2015)<= !--[if supportFields]>.   En la tabla N° 01 se presenta los análisis de suelos de la comunidad de = Nabug.

Tabla 01: Análisis de suelos Comunidad de Nabug – Parroquia Flores

ANÁLISI= S

UNIDADES

RESULTADOS

pH

Unidades de= pH

5,7<= span lang=3DES-EC style=3D'font-size:12.0pt;line-height:115%;font-family:"Time= s New Roman",serif; mso-ansi-language:ES-EC'>

Conductivid= ad

ľS/cm

101,4

Textura

N/A<= span lang=3DES-EC style=3D'font-size:12.0pt;line-height:115%;font-family:"Time= s New Roman",serif; mso-ansi-language:ES-EC'>

Franco arci= lloso

Humedad

%

21,55

Materia Orgánica

%

3,18%

Fuente: (Garcés, 2021)

Elaboración: Los autores

El uso de suelo en la parroquia se distribuye de la siguiente manera; la mayor parte el 75,10% se encuentra cubierto por bosque, seguido por pasturas con el 23,20%, el 0,19% a cuerpos de agua y el 1,51% corresponde a cultivos.

Figu= ra 3:<= /span> Mapa de aptitud agrícol= a de la parroquia Flores

Elaboración: Nataly Garcés (2020)<= o:p>

En cuanto a la aptitud agrícola, en la parroquia Flores se observa que se dedican a los cultivos extensivos, que la mano de = obra es escasa, el uso de agua y agroquímicos es mínimo. Los cultivos que preval= ecen son gramíneas como la cebada, el maíz sueve sec= o y quinua, hortalizas como la papa y la cebolla y leguminosas como el haba (Ta= bla N°02), cultivos como fréjol, melloco, oca, mashua, se encuentra formando parte de los mosaicos agropecuarios, es decir no se ha definido espacios dedicados únicamente a estos cultivos; las áreas cosechas= o con poca productividad son aprovechadas para realizar el pastoreo nómada de ovejas y ganado.

Tabla 02: Tipos de cultivo de la parroquia Flore= s

TIPO DE CULTIVO

SUPERFICIE ( ha)

%

 

Gramíneas

Maíz suave seco

65

31,9

Cebada

40

19,7=

Quinua

20

9,82

Hortalizas

Papa=

55,9=

27,5=

Cebolla blanca

7,1

3,47

leguminosas

Haba tier= na

15,6=

7.66=

Fuente: (GADPR- Flores, 2015)

El= aboración: Los autores

 

= En lo referente a riego de la parroquia Flores est= a se abastece de la subcuenca del Río Chambo, por las particularidades de ubicac= ión geográfica el sistema de riego aquí es deficiente, la superficie total con riego comprende un total = 14 Ha, siendo el sistema de riego por inundación es la forma de aplicación de riego.

Análisis del componente social.<= /b>

De las 325 encuestas aplicadas en los habitantes de las comunidades con mayor número de pobladores Naubug<= /span>, Capiatá, Guantual Grande central y Puesetus Grande se obtuvo los siguientes resultados sociodemográficos.

Tabla N°03: Características sociodemográficas que inciden en la valoración de los servicios ecosistémic= os

Característ= icas=

Variables=

Porcentaje<= /span>=

Género=

Hombre

43,83%

Mujer

56,47%

Estado Civi= l

Soltero

25,30%

Unión libre

8,52%

Casado

60,10%

Divorciado

1,22%

Viudo

4,87%

Edad

Menor a 30 ańos

15,00%

31 -60 ańos

66,00%

Mayor 60 ańos

19,00%

Educación

Primaria incompleta

32,50%

Primaria completa

37,05%

Secundaria incompleta=

8,18%

Secundaria completa

15,91%

Tercer nivel incompleto

3,18%

Tercer nivel completo

2,95%

Cuarto nivel

0,23%

Ocupación

Ama de casa

19,00%

Empleado

6,91%

Independiente

56,00%

desempleado

9,00%

Estudiante

9,63%

Jubilado

0,00%

Ingresos

Menor a 394 dólares

87,35%

494 - 778 dólares

6,17%

778 a 1000 dólares

4,63%

1000 a 2000 dólares

1,54%

mayor a 2000 dólares

31,00%

Fuente: (Garcés, 2021)

Elabora= ción: Los autores

Entre los datos más representativos en el análisis sociodemográfico se encuentra que en el componente edad donde la población joven menor a 30 ańos representa el valor más bajo con el 15% lo que coinci= de con lo establecido por GADM – Riobamba en su documento de línea base de gru= pos de atención prioritaria del cantón Riobamba donde manifiestan que Flores qu= e en la población joven en edad de trabajar han abandonado la parroquia (Consejo Cantonal de Protección de dere= chos GADM Riobamba, 2019).  En cuanto al nivel de instrucción se manifiesta que el 69,55% de personas encuestadas cursaron la primaria de fo= rma completa o incompleta, en cuanto a ocupación se obtiene que el 56% de la población se ocupa en actividades como independientes siendo la agricultura= y el pastoreo las principales actividades, y en lo referente a los ingresos se obtuvo que el 87,53% de los encuestados ganan menos del salario mínimo del Ecuador

Análisis del componente ambiental

El componente ambiental se analizó usando el escen= ario de conservación del recurso vegetal productivo, mediante la identificación y valoración de los servicios ambientales donde los encuestados apreciaron ca= da servicio utilizando la escala de Likert de 1 a 10 donde 1 correspondía a no importante y 10 los resultados se observan en la tabla 04

Tabla N°04: Valoración ambiental de los servicios ecosistémic= os de la parroquia Flores

Comunidades de la parroquia Flores=

Servicios Ecosistémicos=

Guantul Grande Central

Puesetus

Naubug

Capi= atá

Servicios de abastecimiento<= /span>

Alimentos de origen vegetal (cereales, frutos= y legumbres)

9

8,6

9,4

9,2

Pasto (avena, vicia, alfalfa)

8,3

8,9

8,3

8,6

Madera (construcción y leńa)

6.6

7,5

7,5

7,7

Plantas medicinales

7,2

6,4

5,9

6,1

Servicios de Regulación

Control de plagas

6,4

7,9

7,8

7,7

Prevención de deslizamientos de tierra<= o:p>

7,7

8,9

7,6

8,2

Servicios de Soporte<= /i>

Abonos orgánicos para la producción

6,8

7,5

8,7

7,7

Conservación de cultivos

6,3

6,9

7,6

7,3

Servicios Culturales<= /i>

Paisaje

6,6

6,2

7,1

6,5

Saberes Ancestrales

5,5

5,4

6,1

5,1

Fu= ente: (Garcés, 2021)

Elaboración: Los autores

Los servicios ambientales mejores puntuados (Tabla= 04 y Tabla 05) son = los servicios de abastecimiento con un valor medio de 8,5 siendo los pobladores= de la comunidad de Nabug quienes mejores valoraron= este servicio en el componente de producción de alimentos llegando a 9,4 lo que = está relacionado con lo que mencionan el el plan de ordenamiento territorial en que estas comunidades poseen cultivos para la comercialización y para el autoconsumo (GADPR- Flores, 2015)= .  Dos servicios presentan valores muy cer= canos entre sí, los servicios de regulación con 7,7 se encuentran ligeramente por encima de los servicios de soporte con 7,4 esta pequeńa diferencia se le pu= ede atribuir a que los servicios de soporte son más complejos de percibir  (Agbenyega et al, 2019) pero se encuen= tran sobre los valores que obtuvieron los servicios culturales por lo que se considera  que estos ocupan el segu= ndo lugar en las  preferencias de los encuestados, siendo el control de plagas es el mejor valorado. Mientras que= los servicios culturales muestran el valor medio más bajo con 6 siendo la comun= idad de Capiata quienes dieron los presentaron los v= alores más bajos siendo los saberes ancestrales los menor punt= uados con 5,1 lo que concuerda con lo mencionado por la FAO quienes enuncian que = los conocimientos ancestrales e indicadores culturales han ido mermando en las comunidades indígenas y a medida que pasan los ańos pueden desaparecer. (FAO-B= olivia, 2013).

La jerarquización realizada por los habitantes de = la parroquia rural Flores se ajusta a lo mencionado en trabajos previos realiz= ado en áreas rurales donde se evidencia que las preferencias de los servicios ambientales se encuentran en el siguiente orden servicios de abastecimiento, seguidos por los de regulación y finalmente los culturales. (Villamagua, 2017)  <= /span>

Tabla 05:  Promedio por grupo de los servicios ambientales

SERVICIOS AMBIENTALES=

Abastecimiento

Regulación

Soporte

Culturales

 

Alimentos de origen vegetal (cereales, frutos y legumbres)

Pasto (avena, vicia, alfalfa)

Madera (Construcción y leńa)

Plantas medicinales

Prevención de deslizamientos de tierra

Control de plagas

Abonos orgánicos para la producción de agrícola.=

Conservación de variedad de los cultivos

Paisaje

Rituales ancestrales

Valor medio por componente de servicio<= o:p>

= 9,2

= 8,6

= 7,8

= 6,5

= 7,5

7,7

= 6,7

= 7,2

= 6,6

= 5,6

Valor medio del servicio ambiental=

8,5

7,7

7,4

6

 

Fuente= : (Garcés, 2021)

Elaboración: Los autores

= En lo referente a la relación de las variables sociodemográficas en la valoración de los servicios ambientales (Tabla N°06) se obtuvo que = la variable edad incide en la valoración de los servicios de abastecimiento concordando con lo establecido por (Briceńo, 2016) que seńala que la población adulta = les atribuye más importancia a los servicios de aprovisionamiento.  

La variable edad además tiene incidencia en la percepción del servicio culturales, el grupo de personas mayores a 50 ańos estiman valores más a su entorno esto puede deberse a como indica (INTA, 2015) el tiempo de interacción continua de los seres humanos con los recursos naturales les permite valorarlos de mejor modo y así determinar la identidad cultural y el sentido de pertenencia de una comunidad (Leiva, 2018).

Tabla N°06: Variables que inciden en la valoració= n de los servicios ecosistémicos

= VARIABLES SOCIO DEMOGRÁFICAS

PRUEBA T Y NO PARAMÉTRICA

= ANNOVA DE UN FACTOR

VALOR p

= SA

= SR

= SS

= SC

= Sexo

= X

=  

= 0,87

= 0,075

= 0,244

= 0,140

= Edad

=  

= x

= 0,003

= 0,323

= 0,282

= 5,67E-11

= Estado civil

= X

=  

= 0,36

= 0,54

= 0,75

= 0,59

= Nivel de educación

=  

= x

= 0,002

= 0,221

= 0,853

= 0,35

= Ingresos mensuales

=  

= x

= 0,32

= 0,53

= 4,25E-5

= 0,98

= Ocupación

=  

= x

= 0,98

= 0,06

= 0,84

= 0,43

Fuente: (Garcés, 2021)

Elaboración: Los autores

Análisis del componente monetario

Producción agrícola

En el análisis de la tabla N°07, la parroquia Flor= es presenta una baja producción agropecuaria según lo refiere=  (GADPR- Flores,= 2015), los sistemas productivos son marginales si los productores mejoran la canti= dad y calidad de riego, adquieren tecnificación y hacen uso de una mayor y mejor cantidad de fertilizantes  en un cu= ltivo se podrá obtener mayor producción, pero la incorrecta utilización de la tecnificación y fertilización podría llegar a afectar de manera negativa el nivel y calidad del producto. (VIU, = 2018)

Otro factor que incide en la baja productividad es= la carencia de servicios de asistencia técnica y créditos, lo cual propicia a = los pobladores a migrar hacia la ciudad y otros países. (Conse= jo Cantonal de Protección de derechos GADM Riobamba, 2019).

En la tabla N°08, se establece los cálculos de las especies forestales siendo el Pinus radiata y el Eucalyptus globulus las especies predominantes en la parroquia rural Flores lo que coincide con lo mencionado por = (Paltan, 2020) & (Guevara, 2020)

Tabla N°0= 7: Cálculo de producción de cultivos predominantes

Cultivo

superficie

rendimiento

Producción

Costo

Precio de mercado=

costo de producción

utilidades reaal

(Ha)=

(Ton= /Ha)

(Ton= )

($)/Ton

($)<= o:p>

($)<= o:p>

($)<= o:p>

Maíz suave seco

65

0,76

49,4

400

19.760,00

 

-6.100,00

Papa

55,9

0,78

43,6

560

24.417,12

21.975,48

2.441,64

Cebada

40

0,89

35,6

600

21.360,00

14.311,20

7.048,80

Quinua

20

0,65

13

1.900,00

24.700,00

18.525,35

6.174,65

Haba tierna

15,6

0,55

8,58

140

1.201,20

1.057,23

143,97

Cebolla blanca

7,1

0,35

2,485

525

1.304,63

1.023,87

280,76

 Total

 

 

 

 

92.742,95

82.753,13

$22.189,82

Fu= ente: (Garcés, 2021)

El= aboración: Los autores

Producción Forestal

Tabla N°08:  Valor de la producción Forestal

 ESPECIE

Ha (licencias forestales)

($/árbol)

(Árboles /Ha)

PRODUCCIÓN

VALOR ($ / árbo= les)

Pinus radiata 

6,5

4

1111

7221,5

25997,83

Eucalyptus globulus

46

3

1111

51550

175.271,36

= Total

33

 

 

18220

$201.268,51

Fuente: <= !--[if supportFields]>CITATION Gar202 \l 12298 (Garcés, 2021)

Elaboración: Los autores

Producción de pastizales

Tabla N°09: Valor de producción de pastizales

 =

Cobertura( Ha)

Precio $/ha

Valor total

Pastos

825,5

565<= span lang=3DES-EC style=3D'font-size:12.0pt;line-height:115%;mso-ansi-language= :ES-EC'>

$ 466.407,5

Fuente= : (GADPR- Flores, 2015)=

El= aboración: Los autores

Disposicion a pagar

En las Gráficas 01 y 02= se observa que la mayor parte de la población encuestada el 85% no está dispue= sto a pagar para la conservación de los servicios ecosistémicos que provee el recurso vegetal productivo por diversos motivos entre ellos el más sobresaliente está en que le atribuyen al gobierno la responsabilidad de conservar el recurso vegetal lo que no concuerda con las razones expuestas = en estudios anteriores donde se evidencia que la principal razón por la que la= población no está dispuesta a pagar tiene que ver con que el nivel de ingresos no lle= ga al salario mínimo vital (Lemache, 2020)  el 15% restante pagaría hasta un valor = del $ 10,20 anual.

Graf= ica 01: DAP de los usuarios de la parroquia

Fuente: (Garcés, 2021)

Elaboración: Los autores

 =

Grafic= a N° 02: Motivos por lo que los usuarios no estarian dispue= stos a pagar

<= /p>

Fuente: (Garcés, 2021)

El= aboración: Los autores

&n= bsp;

Ta= bla 10: DAP total anual

DAP ($/ańo)<= /o:p>

PEA (2020)

DAP TOTAL($/ańo)

$ 10,20

3419=

$34.873,8=

Fuente: (Garcés, 2021)

El= aboración: Los autores

 =

<= span style=3D'mso-spacerun:yes'>  Valor económico ambiental total del recurso vegetal productivo<= span lang=3DES-EC style=3D'font-size:12.0pt;line-height:115%;mso-ansi-language:E= S-EC'>

Tabla N°11: Cálculo del VET del recurso vegetal productivo

TIPO DE VALOR

COMPONENTE

VALOR MONETARIO ($)

Valor de uso directo

Recurso vegetal=

$ 22.189,82=

Valor de uso directo

Bosqu= es

$ 201.268,51=

Valor de uso directo

Pastos=

$ 466.407,50=

DAP

=  

$ 34.= 873,80

VET total

 

$ 724.730,63

Fuente: (Garcés, 2021)

Elaboración: Los autores

El valor monetario total calculado para el recurso vegetal productivo de la parroquia Flores se estimó en $ 689.865,83, dicho valor puede variar de acuerdo a los rendimientos de los componentes productivos y los precios de mercado que oscilan de una tempora= da a otra como lo mencionan (Collaguazo, 2019)& (Coronel, 2019).=

Conclusiones.

ˇ&nb= sp;        Los pobladores de la parroquia rural de Flores identificaron con los valores más altos los servi= cios de abastecimientos con un puntaje de 8,5/10 siendo el mejor valorado el aprovisionamiento de alimentos, los servicios con menor valoración fueron l= os servicios culturales con 6/10 de los cuales el menor puntuado fue el de rituales ancestrales. La variable sociodemográfica de la edad incide en la valoración de los servicios de abastecimiento y culturales.

ˇ&nb= sp;        El 15% de la población está dispuesta a pagar por la conservación del recurso vegetal productivo c= on un DAP estimado de $10,20 el mayor número de encuestados el 85% no están dispuestos a pagar y la principal razón para no pagar que expresaron fue qu= e la responsabilidad de la conservación es del gobierno.

ˇ&nb= sp;        El valor económico to= tal calculado fue de $ 724.730,63 de los cuales el que mayor aporta es la producción de pasto con $466.407,50, seguido por bosques con $201.268,51= , DAP con $34.873,8 y finalmente el que menos aporta es la producci= ón agrícola con $22.189,= 82, esto debido a que esta es un producción marginal y pobre con poca inversión= y deficiencia de riego.

Referencias bibliográficas<= w:sdtPr>

Agbenyega et al. (2019). Application of an Ecosystem Function Framework to Perceptions of Community Woodlands. Researchgate, 1, 4.<= span style=3D'font-family:"Times New Roman",serif;mso-ascii-font-family:Calibr= i; mso-ascii-theme-font:minor-latin;mso-hansi-font-family:Calibri;mso-hansi-= theme-font: minor-latin;mso-bidi-theme-font:minor-bidi'>

Briceńo, J. I.-G. (2016). Factores que influyen en la percepción de servicios de los bosques secos en el sur del Ecuador. Ecología, 25(2), 46 - 58. doi:10.7818=

Collaguazo, C. (201= 9). VALORACIÓN ECONÓMICA AMBIENTAL DEL RECURSO VEGETAL PRODUCTIVO DE LA PARROQUIA SAN LU= IS, CANTÓN RIOBAMBA, PROVINCIA DE CHIMBORAZO. Trabajo de titulación presentado para optar al grado académico de Ingeniera en Biotecnología Ambiental, Riobamba.

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Coronel, N. (2019).= VALORACIÓN ECONÓMICA AMBIENTAL DEL RÍO CHAMBO EN EL TRAMO DEL RELLENO SANITARIO PORL= ÓN. Trabajo de titulación presentado para optar al grado académico de Ingenie= ra en Biotecnolgía Ambiental, Riobamba.

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Garcés, N. (2021). = Valoración económica ambiental del recurso vegetal de la parroquia Flores, cantón Riobamba. Proyecto de titulación: trabajo previo a la obtención del titulo de Ingeniera en Biotecnología Ambiental, Riobamba.

Guevara, E. (2020).= Valoración económica ambiental del recurso suelo en la parroquia rural de Licto. Trabajo de titulación presentado para optar al grado académico de Ingenie= ro en Biotecnología Ambiental, Escuela Superior Politécnica de Chimborazo.

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 =

 

 

PARA CITAR EL ARTÍCULO INDEXADO.

 

 

Brito Mancero, M. Y., & Garcés Ché= rres, N. A. (2021). Estimación de los servicios ecosistémicos del recurso vegetal= de la parroquia Flores, cantón Riobamba . ConcienciaDigital, 4(3.1), 105-121. https://doi.org/10.33262/concienciadigital.v4i3.1.1817

 

 


 

 

 

El artículo que se publica es de exclusiva responsabilidad de los autores y no necesariamente reflejan el pensamiento de la Revista Concienc= ia Digital.

 

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 Conciencia Digital.

 

                                                 =                                                                            =                       

 

 



[1] Escuela Superior Politécnica de Chimborazo, Facult= ad de Recursos Naturales. Riobamba, Ecuador. mybrito@espoch.edu.ec, https://orcid.org/00= 00-0003-2689-3516

[2] Investigador independiente e= n el área, alexandrita.garces@gmail.com, https://orcid.org/0000-0001-9063-8873 <= o:p>

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www.concienciadigital.org

                                                 =                                                                       ISSN: 2600-5859

                                                    =                              Vol. 4, N°3.1, p. 105-121, agosto, 20 21

 

Análi= sis Informático                                                =                                        =                                                 Página 95

 

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