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Importancia de los servicios ecosistémicos del rec= urso vegetal de la parroquia San Juan, cantón Riobamba

 

 

 

Importance of the ecosystem services of the vegetable resource of the parish San Juan, canton Riobamba

 

Marcela Yolanda Brito Mancero.[1], Mary Silvana Moreta Escobar.[2], Alex Vinicio Gavilanes Montoya.[3] & Zoila Valeria Tapia González.[4]

 

 

Recibido: 23-04-2020 / Revisado: 21-05-2020 / Aceptado: 23-06-2020 / Publicado: 03-07-2020

 

   

Abstract.                                        DOI: https://doi.org/10.33262/cienciadigital.v4i3.1333    

Knowing the present relation= ship between the benefits provided by the service of plant ecosystems with the importance and frequency of use assigned by the inhabitants allows establis= hing an assessment of the resource. Twenty ecosystem services distributed in: s = were identified. regulation (7), s. provisioning (6), = s. support (3) and s. cultural (4) by using the methodology of the Inter-Ameri= can Development Bank (IDB) which is based on the study of economic conditions a= nd activities of the population, climatic conditions, identification of the importance of forest conservation, land and water use, current regulations,= and the powers of sectional governments. 326 surveys were applied to the population, the information was processed using non-parametric tests and the inferential analytical method, determining that the population is willing to pay for conservation; variables ethnicity, gender and level of education are those that assign the values of importance and tangible ecosystem services = are those that have a higher valuation.=

=  

Keywords: Rural parish, Riobamba, San Juan, ecosyst= em services, forest resources.

=  

 

Resumen.

El conocer la relación presente entre los beneficios que proporciona el servicio de los ecosistemas vegetales con la importancia y frecuencia de uso que le asignan los pobladores permite establecer una valoración al recurso. Se identificaron 20 servicios ecosistémicos distribuidos en: s. regulación (7)= , s. aprovisionamiento (6), s. soporte (3) y s. culturales (4) mediante uso de la metodología del Banco Interamericano de Desarrollo (BID) que se basa en el estudio de condiciones y actividades económicas= de la población, condiciones climáticas, identificación de la importancia de la conservación de bosques, uso del suelo y agua, normativa vigente, y las competencias de los gobiernos seccionales. Se aplicaron 326 encuestas a la población, el procesamiento de la información s= e lo realizó mediante pruebas no paramétricas y el método analítico inferencial, determinando que la población está dispuesta a pagar por conservación; las variables etnia, género y nivel de educación so= n los que asignan los valores de importancia y los servicios ecosistémicos tangib= les son los que poseen una valoración más alta.

 

Palabras clave: Parroquia rural, Riobamba, San Juan, servicios ecosistémicos, recursos forestales.

 

Introducción.

 

Los servicios ambientales se clasifican e= n: aprovisionamiento, regulación (Haines-Young &am= p; Potschin, 2013); culturales (Rengifo, Rios, Fachín, & Vargas, 2017), y de soporte (Popa= & Bann, 2012).  Los bienes o servicios ecosistémicos que presta la naturaleza son co= nsumidos de forma directa, mediante la interacción entre sí, que mejoran el desarrol= lo y la calidad de vida de las personas (Balvanera, P., 2012).=

Algunos servicios no poseen valores monet= arios de mercado y se necesita tiempo para asignar valor para ellos (Izco & Burneo, 2003); la influencia que tiene las partes interesadas (Lamarque, Quétier, & Lavorel, 2= 011); sobre los servicios puede ser positiva o negativa (Felipe, Comín, & Escalera, 2015). Durante la identificación de los servicios ambientales req= uiere de un proceso interactivo y de consulta regular, estableciendo preguntas cl= aves y concisas y definir indicadores de uso (Brown, et al., 2014).

Expresando de tal manera una necesidad de estudio para la parroquia San Juan mediante la determinación de la importan= cia de los servicios, la identificación de índices ecológicos y la dependencia = de los mismos por los factores sociales (Lundberg & Moberg, 2003); relación población y el entorno ambiental (Nottea, et al., 2017).

Mediante la encuesta se construyó en torn= o a la metodología clave de: servicios derivados únicamente de los ecosistemas loc= ales y que un flujo de servicios (uso real) colocar solo cuando dichos servicios= se consumen directamente (disfrutado) por el destinatario final (Corral, 2010)= .

Además de conocer la importancia de la conservación de bosques y peligros que enfrentan los ecosistemas, motivos d= el desgaste de los recursos, afectaciones culturales (Mil= cu, Hanspach, Abson, &a= mp; Joern, 2013); conocimiento de las entidades responsab= les de la protección, conservación del área protegida, importancia y frecuencia de= uso de los servicios, actividades comerciales y egresos, motivos por los cuales= no estarían dispuestos a pagar (Kauyeken, 2014); y= la disponibilidad de pago por la conservación de los bosques (Peixer, Giacomini, & Petrere, 2011).

Conjuntamente con el aporte investigativo permite reconoce= r la importancia que tienen los servicios para la economía y la sociedad (Spangenberg, Haaren, &= ; Settele, 2014). Identifican la alta demanda de bienes= y servicios vinculado al aumento poblacional (Groota, Wilson, & Boumansb, 2002), como uno de los factores de la degradación continua del ambiente, a los cuales hay que suma= rle los cambios en el uso de suelo (Tsonkovaa, Quinkensteina, Böhma, Freesea, & Schaller, = 2014); el cambio climático (Lamarque, Tappeiner, Turne= r, & Steinbacher, 2011); entre otros que influ= yen al acelerado daño ambiental (Oropeza, Urciaga, &am= p; Ponce, 2015).

El reconocer las prioridades sociales en = cuanto a la importancia y frecuencia de uso así como la identificación de los servicios favorecerá la aplicación de acciones para su preservación (Campaña, 2015); y reparación del ambiente a 4 categorías: conservación, restauración pasiva y activa, uso sustentable; donde se pueden implementar medidas para un manejo sostenible por zona (GADP-San Juan, 2015= ).

El impacto directo que tendrá esta investigación será sobre los 8443 habitantes de la parroquia y el gobierno autónomo descentralizado de la localidad; quienes son los beneficiaros de e= stos servicios ecosistémicos, mientras que de manera indirecta serán las autorid= ades provinciales, sectoriales y organizaciones no gubernamentales, como parte d= e la planificación territorial.

 

Metodología.

 

Identificación y consulta a las partes involucradas “stakeholders” y revisión bibliogr= áfica. Se aplicaron encuestas a los habitantes de la población y entrevistas a los líderes barriales siguiendo la recomendación del Banco Interamericano de Desarrollo (BID) (Herrera, Felipe, 2017). Como fuente secundaria se revisó = el inventario vegetal, población zonal, sistema comunitario, culturas, sustentabilidad social y económico en el plan de desarrollo y ordenamiento territorial local, cantonal y provincial (FAO, 2009).

 

Tabla 1: Identifi= cación de los “stakeh= olders” de la parroquia

Partes interesadas

Partes involucradas que están trabajando en el manejo de los recursos ambientales

Juntas comunales de pueblos indígenas

Propietarios de bosques (propiedad privada)

Organizaciones de productores

Gobierno Autónomo Descentralizado Parroquial de San Juan

Sociedad local

 

Ministerio de Ambiente del Ecuador

Ministerio de Agricultura y Pesca=

Gobierno Autónomo Descentralizado Municipal de Riob= amba

Gobierno Autónomo Descentralizado Provincial de Chimborazo

Escuela Superior Politécnica de Chimborazo

Universidad Nacional de Chimborazo

ECOPAR

PROMAREN

Cemento Chimborazo

 
                   Fuente: Go=
bierno Autónomo Descentralizado parroquial San Juan,2018<=
/pre>


El cálculo de la muestra se realizó el cá=
lculo
de n-encuestas aplicado para poblaciones finitas (Aguilar, 2005), para un
universo poblacional de 2126, obteniendo 326 entrevistas a aplicarse, distr=
ibuidas
de acuerdo con su densidad poblacional.



 



Tabla 2: Distribu=
ción
de encuestas por barrios (Cabec=
era
parroquial San Juan)







 

  
  
Barrio

  		
  
  
**Promedio de integrantes (4)

  		
  
  
Porcentaje

  		
  
  
N° encuestas

  		
 

 

  
  
 

  
San Francisco=


  		
  
  
 

  
352

  		
  
  
 

  
16,6

  		
  
  
 

  
54

  		
 

 

  
  
 

  
San Vicente

  		
  
  
 

  
313

  		
  
  
 

  
14,7

  		
  
  
 

  
48

  		
 

 

  
  
 

  
Central

  		
  
  
 

  
365

  		
  
  
 

  
17,2

  		
  
  
 

  
56

  		
 

 

  
  
Santa Marianita

  		
  
  
 

  
515

  		
  
  
 

  
24,2

  		
  
  
 

  
79

  		
 

 

  
  
 

  
Rumipamb=
a

  		
  
  
 

  
581

  		
  
  
 

  
27,3

  		
  
  
 

  
89

  		
 

 

  
  
 

  
TOTAL

  		
  
  
 

  
2126

  		
  
  
 

  
100,0

  		
  
  
 

  
326

  		
 








               Fuente: Elaboración pr=
opia.=




 <=
/span>



El área de aplicación se obtuvo de los va=
lores
de importancia y frecuencia de uso de los servicios, se identificó sitios en
los que: los pobladores de la parroquia local son altamente dependientes de=
 la
naturaleza ya que con ella obtienen su capital de ingreso y beneficios (Affek & Kowalska, 201=
7).



         =
               



Identificación de los servicios ecosistém=
icos
que proporciona el recurso vegetal se realizó mediante conversatorios centr=
ados
hacia los actores principales se identificaron los servicios prestados por =
la
vegetación distribuidos entre las categorías: aprovisionamiento, regulación,
soporte y culturales.



Para el desarrollo de la encuesta se elab=
oraron
preguntas básicas detenidamente expuestas a revisión, adaptadas a la realid=
ad
de la zona de estudio después de haber recopilado información por parte de =
las
autoridades locales, cantonales provinciales y personas voluntarias con
criterio que habitan en la parroquia.



A los encuestados se les indicó que limit=
aran
sus consideraciones a los servicios proporcionados por los ecosistemas loca=
les.
Los servicios ecosistémicos identificados se distribuyeron por categorías en
los cuales se obtuvo: 6 de aprovisionamiento, 7 de regulación, 3 de soporte=
 y 4
culturales (Affek & Ko=
walska,
2017). 



Para la evaluación de los servicios
ecosistémicos se eligió un rango corto de calificación se aplicó una escala
numérica del 1 al 5 ante los servicios enlistados ya sea por importancia o
frecuencia de uso.



&n=
bsp;



Tabla 3. Escala de colores para la evaluación de l=
os
servicios identificados según la importancia y la frecuencia de uso







 

  
 

  
  
VALORES

  		
  
 

 

 

  
 

  
  
1 - 1,99

  		
  
  
2 - 2,99

  		
  
  
3 - 3,99

  		
  
  
4 - 4,99

  		
  
  
5

  		
  
 

 

 

  
  
*I

  		
  
  
Poco
  o nada importante

  		
  
  
Algo
  importante

  		
  
  
Medianamente importante

  		
  
  
Importante

  		
  
  
Muy importante

  		
 

 

  
  
*F

  		
  
  
Poco o nada frecuente

  		
  
  
Algo frecuente

  		
  
  
Medianamente frecuente

  		
  
  
Frecuente

  		
  
  
Muy frecuente

  		
 

 
 

  
  
  
  
  
  
  
  
  
  
  
  
 

 







*I=3D Importancia del servicio ecosistémico, *F=3D
Frecuencia de uso del servicio ecosistémico



Fuente:
Elaboración propia.



Para averiguar la importancia=
 y la
frecuencia del uso otorgado a los servicios provenientes de los ecosistemas=
 se
obtuvo el promedio de las respuestas emitidas por los encuestados según la
escala de Likert del 1 al 5, diferenciado a la importancia del servicio con=
 la
de frecuencia de uso del servicio.



Elementos que cambiaron la
percepción del ecosistema se realizó mediante el análisis estadístico
desarrollado con los resultados obtenidos de las encuestas aplicadas a la
población, se consideró los siguientes factores (variables independientes):
barrio, género, etnia y nivel de instrucción.



 



Tabla
4: Pruebas aplicadas en =
el
análisis estadístico.



 







 

  
  
Distribución
  Normal

  		
  
  
Análisis

  		
  
  
Prueba

  		
  
 

  
  
  
 

 

  
  
Incluye todos los datos levantados.

  		
  
  
Kolmogorov Smirnov

  		
  
 

  
  
  
 

 

  
  
  
  
 

 

  
  
Distribución
  no Normal

  		
  
  
Pruebas
  no paramétricas

  		
  
  
Para el factor género

  		
  
  
Mann Whitney

  		
  
  
  
  
 

 

  
  
Para los factores: barrio, nivel
  instructivo y etnia

  		
  
  
Kruskal Walls

  		
  
  
  
  
 

 

  
  
Encuestas (Conservación)

  		
  
  
Disposición a pagar (DAP)

  		
  
  
Chi cuadrado

  		
  
  
  
  
 








 



            Fuente:
Elaboración propia.



Resultados y Discusión.=




 



Resultados de selección de los servicios
mediante las entrevistas realizadas 



Para el proceso de evaluación de los serv=
icios
ecosistémicos se modificaron los términos con los que se usó en las entrevi=
stas
y encuestas por un lenguaje técnico ambiental para nuestro estudio.



 



Tabla 5: Resultado del proceso de entrevista hacia los usuarios con nivel de
decisión







 

  
  
Categorías

  		
  
  
Servicios
  Ecosistémicos<=
/span>

  		
  
  
Calificación=
 De
  Los Servicios Seleccionados (%)<=
o:p>

  		
 

 

  
  
 

  
 

  
Servicios de aprovisionamiento 

  		
  
  
Alimentación
  humana 

  		
  
  
100

  		
 

 

  
  
Alime=
ntación
  animal

  		
  
  
100

  		
 

 

  
  
Madera
  para construcción

  		
  
  
60

  		
 

 

  
  
Plant=
as
  medicinales

  		
  
  
60

  		
 

 

  
  
Polinización

  		
  
  
80

  		
 

 

  
  
Leña =
            

  		
  
  
45

  		
 

 

  
  
 

  
 

  
 

  
Servicios de regulación

  		
  
  
Regulación
  del ciclo hidrológico 

  		
  
  
100

  		
 

 

  
  
Incre=
mento
  de filtración

  		
  
  
80

  		
 

 

  
  
Conservación
  de agua por los bosques

  		
  
  
100

  		
 

 

  
  
Regul=
ación
  del microclima

  		
  
  
80

  		
 

 

  
  
Prevención
  de deslizamientos de tierra 

  		
  
  
80

  		
 

 

  
  
Preve=
nción
  de inundaciones

  		
  
  
80

  		
 

 

  
  
Control
  biológico 

  		
  
  
80

  		
 

 

  
  
 

  
Servicios de soporte

  		
  
  
Veget=
ación
  que ayuda a mantener los niveles de agua

  		
  
  
100

  		
 

 

  
  
Ciclo
  de nutrientes en el suelo

  		
  
  
100

  		
 

 

  
  
Resid=
uos
  orgánicos que mejoran el suelo

  		
  
  
80

  		
 

 

  
  
 

  
Servicios culturales

  		
  
  
Descanso, relajación

  		
  
  
=
80

  		
 

 

  
  
Recreación
  

  		
  
  
70

  		
 

 

  
  
Paisaje

  		
  
  
=
100

  		
 

 

  
  
Prácticas
  ancestrales

  		
  
  
50

  		
 








Fuente: Elaboración propia.



 



En vista de los altos valores porcentuales
registrados durante las entrevistas realizadas se obtuvo que la mayor parte=
 de
los servicios ecosistémicos enlistados son de suma preferencia en la parroq=
uia
San Juan, donde fueron supervisados y aprobados para realizar las evaluacio=
nes,
sin embargo, es notorio que los usuarios reconocen y valoran los beneficios
ambientales prestados por la vegetación.



Los servicios que tienen un valor menor c=
omo
por ejemplo la madera o los productos forestales maderables, se debe a la
diferencia de criterio de las personas entrevistadas debido a que una parte=
 lo
usan como combustible y para ambientar sus casas con calor por las bajas
temperaturas de la zona; pero, en otros casos se considera como un recurso =
que
está en déficit y que no se debería usar.



Caracterización de la encuesta para el pr=
oceso
de evaluación de los servicios prestados se realizó del total de muestra a
encuestar dio 326 distribuidas en los 5 barrios de la cabecera parroquial
(Tabla 2) y en base a este número se realizaron los análisis estadísticos,
mismos que se resumen con los factores de mayor proporción que inciden en el
uso de los servicios ecosistémicos y se muestran a continuación:=




Tabla
6: Resultados del anális=
is
porcentual de los factores en estudio







 

  
  
Factores

  		
  
  
Distribución porcentual

  		
 

 

  
  
Etnia

  		
  
  
Indígena

  		
  
  
62,90

  		
 

 

  
  
Mestiza

  		
  
  
36,20

  		
 

 

  
  
Blanco=


  		
  
  
9,00
  

 

 

  
  
Género

  		
  
  
Femenino

  		
  
  
48,80

  		
 

 

  
  
Masculino

  		
  
  
51,20

  		
 

 

  
  
Edad

  		
  
  
30-45 años

  		
  
  
31,30

  		
 

 

  
  
18-29 años

  		
  
  
29,40<=
/p>
  

 

 

  
  
Nivel de instrucción

  		
  
  
Primaria

  		
  
  
43,30

  		
 

 

  
  
Secundaria

  		
  
  
30,10

  		
 

 

  
  
Tercer nivel

  		
  
  
16,60

  		
 

 

  
  
Cuarto nivel<=
/span>

  
Ninguna

  		
  
  
9,20
  

 

 

  
  
Ocupación

  		
  
  
Agricultura

  		
  
  
45,10

  		
 

 

  
  
Otros (quehaceres
  doméstico, chofer, guardián)

  		
  
  
21,70<=
/p>
  

 

 

  
  
Ganadería

  		
  
  
10,10

  		
 








Fuente: Statistical Package for the Social Scienc=
es.



 



Importancia y frecuencia de uso de los
servicios provistos por los ecosistemas.



Se fijaron 20 servicios ecosistémicos en =
este
estudio para los análisis de forma independiente, en base a su importancia =
y a
su frecuencia, lo que representó un total de 40 repeticiones por análisis p=
ara
cada servicio.



 



Tabla 7: Evaluación de los servicios ecosistémicos
mediante los valores medios (VM) obtenidos en el análisis estadístico de
acuerdo a la IMPORTANCIA (*I) y FRECUENCIA DE USO (*F)<=
span
style=3D'mso-spacerun:yes'>  de los mismos







 

  
  
EC.

  		
  
  
VEGETAL<=
/span>

  		
  
  
ACUÁTICO=


  		
  
  
VEGETAL<=
/span>

  		
  
 

 

 

  
  
 
  SERVICIOS E.

  		
  
  
Al=
imentación humana=


  		
  
  
Al=
imento de animales<=
/o:p>

  		
  
  
Madera para construcción

  		
  
  
Pl=
antas medicinales<=
/o:p>

  		
  
  
Po=
linización

  		
  
  
Le=
ña

  		
  
  
Ag=
uas superficiales

  		
  
  
Ag=
uas subterráneas=


  		
  
  
Conservación
  hídrica por los bosques

  		
  
  
Regular el microclima

  		
  
  
De=
slizamiento de tierra

  		
  
  
Pr=
evención de inundaciones

  		
  
  
Control de plagas

  		
  
  
Mantener los
  niveles de agua

  		
  
  
Ci=
clo de nutrientes

  		
  
  
Residuos
  orgánicos que mejoran el suelo

  		
  
  
Descanso, relajación

  		
  
  
Re=
creación

  		
  
  
Pa=
isaje

  		
  
  
Pr=
acticas ancestrales<=
/o:p>

  		
 

 

  
  
APROVISIONAMIENTO
  

  
  
REGULACIÓN

  		
  
  
SOPORTE

  
 

  		
  
  
CULTURAL

  		
 

 

  
  
I*

  		
  
  
4,79

  		
  
  
4,40

  		
  
  
3,32

  		
  
  
4,34

  		
  
  
3,81

  		
  
  
3,87

  		
  
  
4,09

  		
  
  
4,06

  		
  
  
4,42

  		
  
  
4,08

  		
  
  
4,19

  		
  
  
4,22

  		
  
  
4,07

  		
  
  
4,41

  		
  
  
4,45

  		
  
  
4,50

  		
  
  
4,51

  		
  
  
4,20

  		
  
  
4,64

  		
  
  
3,32

  		
 

 

  
  
F*

  		
  
  
4,56

  		
  
  
4,10

  		
  
  
                    2,69

  		
  
  
3,90

  		
  
  
3,14

  		
  
  
3,40

  		
  
  
3,51

  		
  
  
3,52

  		
  
  
3,98

  		
  
  
3,75

  		
  
  
3,83

  		
  
  
3,81

  		
  
  
3,61

  		
  
  
4,02

  		
  
  
4,12

  		
  
  
4,10

  		
  
  
3,96

  		
  
  
3,47

  		
  
  
4,48

  		
  
  
2,75

  		
 

 
 

  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
 

 







Fuente: Elaboración propia.



 



Se visualiza principalmente que el valor =
de
mayor importancia que los usuarios le dan a los bienes generados por la
naturaleza, son los servicios de aprovisionamiento entorno a la alimentación
humana.



Los de menor valor son la madera para
construcción debido a la escasez en el sector, mientras que las practicas
ancestrales relacionadas a los servicios culturales tienen una importancia
media, ya que, a pesar de ser una parroquia rural con predominancia del sec=
tor
indígena, sus tradiciones van siendo modificadas por el mestizaje.



En cuanto a la frecuencia de uso de los
servicios, los usuarios otorgaron una alta importancia en lo que respecta a=
 la
alimentación humana, esto se debe a que la actividad que más desarrollan en=
 el
sector es la agricultura y es el sustento para sus familias. Además, se
calificaron con valores altos los servicios de regulación donde está el agu=
a,
ya que es el medio que permite el desarrollo de la producción agrícola.



La variación del uso de las prácticas
ancestrales es un servicio que aún tiene apogeo, sin embargo, con el pasar =
de
los años estas prácticas religiosas se irán desapareciendo por la asimilaci=
ón y
adaptación de otras costumbres que debilitan el fortalecimiento espiritual<=
/span> (Rengifo, Rios, Fachín, & Vargas, 2=
017). 



Los servicios de regulación tienen un val=
or
alto, ya que existe una relación cercana entre los recursos (agua-vegetació=
n) y
cierta dependencia entre ellos (Orellana & Espadas, 2008). Aquellos servicios tangibles son los qu=
e la
población mayoritariamente asigna unas valoraciones más altas (Affek & Kowalska, 2017). Cabe mencionar además que los beneficio=
s de
los servicios ambientales permiten proveer y abastecer las necesidades de l=
os
usuarios<=
!--[if supportFields]> CITATION Aff17 \l 12298  (Affek & Kowalska, 2017).



 



Tabla 8: Dispersión de los datos (desviación estándar)=
 en cuanto
a la importancia (*I) y frecuencia (*F) de uso de los servicios ecosistémic=
os.







 

  
  
EC.

  		
  
  
VEGETAL<=
/span>

  		
  
  
ACUÁTICO=


  		
  
  
VEGETAL<=
/span>

  		
 

 

  SERVICIOS ECOSISTÉMICOS

  		
  
  
Al=
imentación humana=


  		
  
  
Al=
imento de animales<=
/o:p>

  		
  
  
Madera para construcción

  		
  
  
Pl=
antas medicinales<=
/o:p>

  		
  
  
Po=
linización

  		
  
  
Le=
ña

  		
  
  
Ag=
uas superficiales

  		
  
  
Ag=
uas subterráneas=


  		
  
  
Conservación
  hídrica por los bosques

  		
  
  
Regular el microclima

  		
  
  
De=
slizamiento de tierra

  		
  
  
Pr=
evención de inundaciones

  		
  
  
Control de plagas

  		
  
  
Mantener los
  niveles de agua

  		
  
  
Ci=
clo de nutrientes

  		
  
  
Residuos
  orgánicos que mejoran el suelo

  		
  
  
Descanso, relajación

  		
  
  
Re=
creación

  		
  
  
Pa=
isaje

  		
  
  
Pr=
acticas ancestrales<=
/o:p>

  		
  
 

 

 

  
  
APROVISIONAMIENTO
  

  
  
REGULACIÓN

  		
  
  
SOPORTE

  		
  
  
CULTURAL

  		
 

 

  
  
I*

  		
  
  
0,62

  		
  
  
1,12

  		
  
  
1,53

  		
  
  
1,03

  		
  
  
1,40

  		
  
  
1,46

  		
  
  
1,33

  		
  
  
1,36

  		
  
  
1,00

  		
  
  
1,22

  		
  
  
1,24

  		
  
  
1,23

  		
  
  
1,30

  		
  
  
0,99

  		
  
  
1,01

  		
  
  
0,91

  		
  
  
0,90

  		
  
  
1,31

  		
  
  
0,78

  		
  
  
1,67

  		
  
 

 

 

  
  
F*

  		
  
  
0,89

  		
  
  
1,33

  		
  
  
1,49

  		
  
  
1,25

  		
  
  
1,50

  		
  
  
1,53

  		
  
  
1,49

  		
  
  
1,52

  		
  
  
1,25

  		
  
  
1,26

  		
  
  
1,34

  		
  
  
1,35

  		
  
  
1,43

  		
  
  
1,21

  		
  
  
1,15

  		
  
  
1,18

  		
  
  
1,18

  		
  
  
1,46

  		
  
  
0,95

  		
  
  
1,61

  		
  
 

 

 
 

  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
  
 

 







Fuente: =
Elaboración pro=
pia.



 



Las celadas marcadas en la Tabla 8, muest=
ran
los servicios de mayor impacto que tuvieron sobre población de la parroquia=
. La
dispersión de los datos respecto al valor promedio obtenido de la encuesta =
referida
a la importancia de los servicios provistos por los ecosistemas tanto veget=
al y
acuático, por lo que, existe baja variabilidad en las respuestas de los
usuarios para la alimentación humana considerada como servicio de
aprovisionamiento y al paisaje como servicio cultural. A su vez, el de mayor
dispersión es la madera utilizada para construcción y en el caso de los
servicios culturales son las prácticas ancestrales.



Para la frecuencia de uso ocurre lo mismo=
 que
la importancia con la diferencia que existe variabilidad en las preferencia=
s de
uso de madera como combustible (leña). Finalmente, los datos no normales
ocurren por el desconocimiento del usuario acerca de los beneficios que pre=
stan
los bienes y servicios ambientales.



Resultados del análisis mediante pruebas =
no
paramétricas de los factores que modifican la percepción en cuanto a la
importancia (I) y frecuencia (F) de uso de los servicios ecosistémicos.



Se aplicaron pruebas no paramétricas para=
 cada
factor en relación a los servicios ecosistémicos=
, para
determinar cuál de ellos depende de las condiciones sociodemográficas (etni=
a,
género, nivel de instrucción y barrio). Si el valor obtenido es menor al 0,=
05
de significancia, se considera que ese servicio ecosistémico es modificado =
por
el factor.



 



Tabla 9: Factores que modifican la percepción en c=
uanto
a la importancia (I) y frecuencia (F) de uso de los servicios ecosistémicos=
.







 
  

   
   
=
 

   		
   
   
 

   		
   
   
ETNIA

   		
   
   
GÉNERO

   		
   
   
N. INSTRUCCIÓN

   		
   
   
BARRIO

   		
  

  

   
   
CATEG.

   		
   
   
SERVICIO ECOSISTÉMICO=


   		
   
   
I

   		
   
   
F

   		
   
   
I

   		
   
   
F

   		
   
   
I

   		
   
   
F

   		
   
   
I

   		
   
   
F

   		
  

 
 

  
  
APRO=
VISIONAMIENTO

  		
  
  
Alim=
entación humana<=
/span>

  		
  
  
0,528

  		
  
  
0,980

  		
  
  
0,109

  		
  
  
0,161

  		
  
  
0,141

  		
  
  
0,039

  		
  
  
0,074

  		
  
  
0,032

  		
 

 

  
  
Alimentación animal=


  		
  
  
0,162

  		
  
  
0,047

  		
  
  
0,528

  		
  
  
0,019

  		
  
  
0,597

  		
  
  
0,635

  		
  
  
0,000

  		
  
  
0,009

  		
 

 

  
  
Madera para construcción

  		
  
  
0,354

  		
  
  
0,668

  		
  
  
0,329

  		
  
  
0,411

  		
  
  
0,180

  		
  
  
0,203

  		
  
  
0,000

  		
  
  
0,002

  		
 

 

  
  
Plantas medicin=
ales

  		
  
  
0,104

  		
  
  
0,103

  		
  
  
0,076

  		
  
  
0,010

  		
  
  
0,094

  		
  
  
0,379

  		
  
  
0,000

  		
  
  
0,239

  		
 

 

  
  
Poli=
nización

  		
  
  
0,063

  		
  
  
0,402

  		
  
  
0,438

  		
  
  
0,548

  		
  
  
0,205

  		
  
  
0,554

  		
  
  
0,032

  		
  
  
0,007

  		
 

 

  
  
Leña=


  		
  
  
0,000

  		
  
  
0,000

  		
  
  
0,007

  		
  
  
0,007

  		
  
  
0,000

  		
  
  
0,000

  		
  
  
0,009

  		
  
  
0,008

  		
 

 

  
  
REGULACIÓN

  		
  
  
Regu=
lación del cic=
lo
  hidrológico

  		
  
  
0,494

  		
  
  
0,564

  		
  
  
0,431

  		
  
  
0,924

  		
  
  
0,086

  		
  
  
0,002

  		
  
  
0,000

  		
  
  
0,207

  		
 

 

  
  
Incremento de filt=
ración

  		
  
  
0,347

  		
  
  
0,804

  		
  
  
0,890

  		
  
  
0,876

  		
  
  
0,151

  		
  
  
0,019

  		
  
  
0,000

  		
  
  
0,120

  		
 

 

  
  
Conservación de agua por=
 los
  bosques

  		
  
  
0,244

  		
  
  
0,035

  		
  
  
0,364

  		
  
  
0,686

  		
  
  
0,051

  		
  
  
0,016

  		
  
  
0,000

  		
  
  
0,002

  		
 

 

  
  
Regulación del mic=
roclima

  		
  
  
0,483

  		
  
  
0,249

  		
  
  
0,631

  		
  
  
0,921

  		
  
  
0,073

  		
  
  
0,022

  		
  
  
0,000

  		
  
  
0,000

  		
 

 

  
  
Prevención de deslizamie=
ntos
  de tierra

  		
  
  
0,018

  		
  
  
0,003

  		
  
  
0,465

  		
  
  
0,786

  		
  
  
0,130

  		
  
  
0,181

  		
  
  
0,003

  		
  
  
0,136

  		
 

 

  
  
Prevención de inun=
daciones

  		
  
  
0,488

  		
  
  
0,133

  		
  
  
0,054

  		
  
  
0,155

  		
  
  
0,369

  		
  
  
0,247

  		
  
  
0,000

  		
  
  
0,008

  		
 

 

  
  
Control =
biológico
  de plagas

  		
  
  
0,452

  		
  
  
0,758

  		
  
  
0,213

  		
  
  
0,975

  		
  
  
0,127

  		
  
  
0,055

  		
  
  
0,000

  		
  
  
0,026

  		
 

 

  
  
SOPORTE

  		
  
  
Vegetación que ayuda a mantener los niveles=
 de
  agua

  		
  
  
0,137

  		
  
  
0,512

  		
  
  
0,587

  		
  
  
0,604

  		
  
  
0,251

  		
  
  
0,001

  		
  
  
0,004

  		
  
  
0,014

  		
 

 

  
  
Ciclo de nutrientes en el
  suelo

  		
  
  
0,995

  		
  
  
0,702

  		
  
  
0,003

  		
  
  
0,081

  		
  
  
0,326

  		
  
  
0,350

  		
  
  
0,000

  		
  
  
0,024

  		
 

 

  
  
Residuos orgánicos que mejoran el suelo

  		
  
  
0,484

  		
  
  
0,588

  		
  
  
0,699

  		
  
  
0,501

  		
  
  
0,245

  		
  
  
0,372

  		
  
  
0,001

  		
  
  
0,571

  		
 

 

  
  
CULTURAL

  		
  
  
Descanso, rela=
jación

  		
  
  
=
0,285

  		
  
  
=
0,732

  		
  
  
=
0,649

  		
  
  
=
0,983

  		
  
  
=
0,592

  		
  
  
=
0,730

  		
  
  
0,029

  		
  
  
=
0,285

  		
 

 

  
  
Recreación

  		
  
  
0,091

  		
  
  
0,428

  		
  
  
0,002<=
/b>

  		
  
  
0,000<=
/b>

  		
  
  
0,023<=
/b>

  		
  
  
0,002<=
/b>

  		
  
  
0,001<=
/b>

  		
  
  
0,000<=
/b>

  		
 

 

  
  
Paisaje=


  		
  
  
=
0,128

  		
  
  
=
0,083

  		
  
  
=
0,436

  		
  
  
=
0,080

  		
  
  
=
0,309

  		
  
  
=
0,166

  		
  
  
0,000

  		
  
  
0,000

  		
 

 

  
  
Prácticas ancestrales

  		
  
  
0,002<=
/b>

  		
  
  
0,031<=
/b>

  		
  
  
0,307

  		
  
  
0,252

  		
  
  
0,001<=
/b>

  		
  
  
0,000<=
/b>

  		
  
  
0,000<=
/b>

  		
  
  
0,010<=
/b>

  		
 








Fuente: Elaboración propia.



Los factores de mayor incidencia que modi=
fican
la percepción en torno a la importancia de los servicios ecosistémicos y su
frecuencia de uso fueron: etnia, género y nivel de instrucción.<=
/span>



La edad cambia la percepción de la import=
ancia
de los servicios provistos (Affek & Kowalska, 2017), va además, en base a la formación educa=
tiva y
al conocimiento ambiental (Allendorf & Yang, =
2013); este último factor no fue considerado e=
n este
estudio. 



Las variaciones que provienen de los dife=
rentes
factores analizados mediante el valor medio de frecuencia e importancia se
resumen en la siguiente tabla:



 



Tabla 10: Resulta=
dos
del análisis del valor medio (VM) de la importancia y frecuencia de uso de =
los
servicios ecosistémicos en función de los factores sociales y el factor
geográfico.



 







 

  
  
FA=
CTORES

  		
  
  
  IMPORTANCIA

  		
  
  
FRECUENCIA

  		
 

 

  
  
 

  
Etnia

  
 

  		
  
  
Indígena<=
/b>

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Mestiza

  		
  
  
Alimentación humana

  		
  
  
Paisaje

  		
 

 

  
  
Blanco

  		
  
  
Plantas
  medicinales

  		
  
  
Plantas
  medicinales

  		
 

 

  
  
 

  
Sexo

  		
  
  
Femenino<=
/b>

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Masculino<=
/b>

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Nivel de instrucción

  		
  
  
Ninguna<=
/b>

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Primaria

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Secundaria<=
/b>

  		
  
  
Alimentación humana

  		
  
  
Paisaje

  		
 

 

  
  
Tercer nivel

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Cuarto nivel<=
/b>

  		
  
  
Aguas
  subterráneas

  
Regular
  el microclima

  
Deslizamiento
  de tierra

  
Prevención
  de inundaciones

  
Control
  biológico

  
Mantener
  los niveles del agua

  
 Descanso 

  
Paisaje

  		
  
  
Deslizamiento de tierra<=
/span>

  		
 

 

  
  
 

  
Barrio

  		
  
  
San Francisco<=
/b>

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
San Vicente

  		
  
  
Alimentación humana

  		
  
  
Paisaje

  		
 

 

  
  
Central

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Santa Marianita<=
/b>

  		
  
  
Alimentación humana

  		
  
  
Alimentación humana

  		
 

 

  
  
Rumipamba<=
/b>

  		
  
  
Paisaje

  		
  
  
Paisaje

  		
 








Fuente: Elaboración pro=
pia.



Como se observa en la Tabla 10, los servi=
cios
de mayor importancia se destacan la alimentación humana para los factores
analizados, la etnia blanca reconoce la importancia de las plantas medicina=
les,
y la población mestiza el uso frecuente del paisaje como servicio cultural.=




La etnia es un factor que incide en las
preferencias de servicios ambientales, por lo tanto, se debe considerar esta
variable para establecer planes de desarrollo (Cuni, Pfeifer, Marchant, & Burgess,
 2016). Asimismo, las prioridades de conservaci=
ón
pueden ser establecidas según las tendencias sociodemográficas (Graves, Pearson, & Turnera, 2017)<=
/span>.



La variable género no presenta diferencia=
s en
lo referente a labores tanto hombres como mujeres realizan actividades
semejantes. Asimismo, para esta variable género se estable que el servicio
ecosistémico alimentación humana en importancia y frecuencia de uso se
considerado como un regulador entre el ambiente y la potencialidad del recursos (Garcia, Spence, & McGannon, 2005)<=
/span>.



Basados en estudios realizados por (Affek & Kowalska, =
2017) que indica que en determinados  casos los roles realizados por el género
masculino se orientan a actividades de 
manejo de los bosques y cultivos mientras que a la mujer se encarga =
el
cuidado del hogar y  quehaceres
doméstico; se puede inferir que el análisis de este factor es variable ya q=
ue
en estudios subsiguientes se observa la equidad del género que se da en alg=
unos
sectores y por ende las labores igualitarias.



La mayor cantidad de servicios favorecido=
s con
puntuaciones altas son realizados por personas con título de cuarto nivel (Allendorf & Yang, 2013). Se debe al conocimiento en temas de
conservación y desarrollo que dicha población posee. El valor medio de los
servicios varía en función del factor barrio, esto es en consecuencia de qu=
e la
percepción depende del pensamiento social que no es similar de un barrio a =
otro
por la distinción de criterios, necesidades y accesibilidad.



Resultados del análisis estadístico de las
preguntas vinculadas al DAP.



Tabla 11: Depende=
ncia
de la DAP con relación a las variables utilizadas




 

  
  
Variables independientes

  		
  
  
Significancia

  		
  
  
Dependencia

  		
 

 

  
  
Género

  		
  
  
0,176

  		
  
  
NO

  		
 

 

  
  
Etnia

  		
  
  
0,159

  		
  
  
NO

  		
 

 

  
  
Edad

  		
  
  
0,125

  		
  
  
NO

  		
 

 

  
  
Estado civil

  		
  
  
0,494

  		
  
  
NO

  		
 

 

  
  
Nivel de instrucción

  		
  
  
0,003

  		
  
  
SI

  		
 

 

  
  
Conservación bosque

  		
  
  
0,874

  		
  
  
NO

  		
 

 

  
  
Desaparición sino =
se cuida

  		
  
  
0,828

  		
  
  
NO

  		
 

 

  
  
Ingresos<=
/span> económicos

  		
  
  
0,004<=
/b>

  		
  
  
SI<=
/b>

  		
 





 <=
/span>



 <=
/span>



 <=
/span>



 <=
/span>



 



 



Fuente: Elaboración pro=
pia.



La variable dependiente disposición a pag=
ar
(DAP) se encuentra relacionada a las variables (socio económicas) nivel de
instrucción e ingresos económicos según los establece el análisis inferenci=
al (Moreta, 2019). Dicha dependencia se debe a la relación
existente entre el  índice económic=
o y la
preparación académica que éstos tengan (Peixer, Giacomini, & Petrere, 2011=
); el vínculo personal denominado “estado =
civil”
también puede afectar esta variable dependiente (González & Valdivia, 2009)<=
!--[if supportFields]>.



 



 



Conclusiones:



·&nb=
sp;     
La parroqu=
ia
rural de San Juan estableció para el recurso vegetación siete  (7) servicios de regulación que son:
regulación del ciclo hidrológico, incremento en la filtración, conservación=
 del
agua por los bosques, regulación del microclima, prevención de los deslizamientos de tierra, prevención de inundacio=
nes y
control biológico; seis (6) servicios de aprovisionamiento: alimentación
humana, alimentación animal, madera para construcción, plantas medicinales,
polinización y leña; cuatro (4) servicios culturales:
descanso, recreación, paisaje y prácticas ancestrales y tres (3) servicios =
de
soporte: mantener los niveles de agua, ciclo de nutrientes en el suelo, mej=
ora
del suelo; siendo los servicios ambientales más valorados tanto en importan=
cia
como en frecuencia de uso los aquellos servicios
tangibles Los factores sociodemográficos de con incidencia favorable en la
valoración fueron tres (3) etnia, género y nivel de instrucción. 



·&nb=
sp;     
Los factor=
es
nivel de instrucción y los ingresos económicos en los pobladores de la parroquia rural incidieron en la variable disposi=
ción a
pagar definiendo un excedente de pago por conservación de los bosques. Para
este caso particular la disposición a mantener el recurso vegetal con un ma=
nejo
técnico en coordinación con las autoridades
competentes, para un aprovechamiento sostenible se debe a que los participa=
ntes
del estudio poseen predios forestales.



Referencia=
s bibliográ=
ficas:



Affek, A., & Kowalsk=
a, A.
(7 de Julio de 2017). Ecosystem potentials to provide services in the view of
direct users. Ecosystem
services, 26(1),
184-185,188, 192, 193. doi:https://doi.org/10.1016/j.ecoser.2017.06.017



Aguilar, S. (enero-agosto de 2005). Fórmulas para el
cálculo de la muestra en investigaciones de salud. Salud en Tabaco, 11(1-2),
336. Recuperado el Agosto de 2018, de
http://www.redalyc.org/pdf/487/48711206.pdf



Aldana, S., Vereda, F., Hidalgo-Alvarez, R., & =
de
Vicente, J. (2016). Facile synthesis of magnetic agarose microfibers by direc=
ted
selfassembly. Polymer, 93, 61-64.



Allendorf, T., & Yan=
g, J.
(2013). The role of ecosystem services in park–people relationships: The
case of Gaoligongshan Nature Reserve in southwest China (Primera ed., V=
ol.
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PARA CITAR EL ARTÍCULO INDEXADO.=




 






 



Brito Mancero, M. Y., Moreta Escobar, M.=
 S.,
Alex Vinicio, A. V., & Tapia González, Z. V. (2020). Importancia de los
servicios ecosistémicos del recurso vegetal de la parroquia San Juan, cantón
Riobamba. Ciencia Digital, 4(3), 253-270. =
https://doi.org/10.33262/cie=
nciadigital.v4i3.1333



 






 



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



 



El
artículo queda en propiedad de la revista y, por tanto, su publicación parc=
ial
y/o total en otro medio tiene que ser autorizado por el director de la Revista Ciencia Digital.<=
/p>


 







 

  
 

 

  
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<=
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<= ![if !supportFootnotes]>[1] Docente Investigador, Facu= ltad de Ciencias, Escuela Superior Politécnica de Chimborazo, Riobamba, mybrito@espoch.edu.ec

= [2]= Investigador independien= te en el área ambiental, Riobamba, msilvanamoreta@yahoo.es

= [3]= Docente Investigador, Extensión Orellana, Escuela Superior Politécnica de Chimborazo, Puerto Francisco de Orellana, vinicio.gavilanes@espoch.edu.ec

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------=_NextPart_01D668FD.BEA94FF0 Content-Location: file:///C:/8E5AB2EF/16_importanciadelosserviciosecosistemicosl_vegetacion_MarcelaBrito_archivos/header.htm Content-Transfer-Encoding: quoted-printable Content-Type: text/html; charset="windows-1252"

                     =                                                                            =               ISSN: 2602-8085

                                                     =                  Vol. 4, N°3, p. 253-270, julio-septiembre, 2020

 

 Diseño & Evaluación                                                 =                                  =                                    Página 177

 

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