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Análisis multitemporal de la dinámica de cobertura= /uso de suelo de la cuenca del río Esmeraldas

 

Multi-temporal analysis of the land cover/use dynamics in the Esmeraldas River basin

 

= 1=

Jesmar Jandry Corozo Hurta= do                                        =     

 <= /span>

https://orcid.org/0009-0003-0908-129X

 <= /span>

Universidad Técnica Luis Vargas Torres, Estación Experimental Mutile, Esmeraldas, Ecuador.

j= esmar.corozo@utelvt.edu.ec

= 2=

Patricio Alejan= dro Merino Córdova

 <= /span>

https://orcid.org/0000-0001-5068-8673

 <= /span>

Universidad Técnica Luis Vargas Torres, Estación Experimental Mutile, Esmeraldas, Ecuador.

patricio.merino@utelvt.edu.ec=

= 3=

Byron Fabricio Estupiñán Cox

 <= /span>

https://orcid.org/0000-0001-6523-667X

 <= /span>

Universidad Técnica Luis Vargas Torres, Estación Experimental Mutile, Esmeraldas, Ecuador. byron.estu= pinan@utelvt.edu.ec

= 4=

Joel <= span class=3DSpellE>Darvin Velasco Quiñónez

 <= /span>

https://orcid.org/0000-0001-88= 64-9557

 <= /span>

Universidad Técnica Luis Vargas Torres, Estación Experimental Mutile, Esmeraldas, Ecuador.

jo= el.velasco@utelvt.edu.ec   

&n= bsp;

 

 

 

 

 

Artículo = de Investigación Científica y Tecnológica

Enviado: = 20/01/2024

Revisado: 22/02/2024

Aceptado:= 15/03/2024

Publicado= :25/04/2024

DOI: https://doi.org/10.33262/concienciadigi= tal.v7i2.3021     

 

&= nbsp;

 

Cítese:

 

 

Corozo Hurtado, J. J., Meri= no Córdova, P. A., Estupiñán Cox, B. F., & V= elasco Quiñónez , J. D. (2024). Análisis multitemporal de la dinámica de cobertura/uso de su= elo de la cuenca del río Esmeraldas. ConcienciaDigital, 7(2), 178-195. https://doi.org/10.33262/concienciadigital.v7i2.3021<= /span>

 

 

 

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La revista es editada por la Editorial Ciencia Digital (Editorial de prestigio registrada en la Cámara Ecuatoriana de Li= bro con No de Afiliación 663) www.c= elibro.org.ec

 <= /u>

 

 

Esta revista está protegida bajo una licencia Creative Commons AttributionNonCommercialNoDerivatives 4.0 International. Copia de la licencia: http://creativecommons.org/licenses/by-nc-nd/4.0/

 

Palabras claves: Cuenca hidrográfica del río Esmeraldas, uso de suelo, zona antrópic= a, análisis multitemporal, proyección.

 

Resumen

Introducción: El análisis multitemporal de la cobertura y uso de suelo= de la cuenca del río Esmeraldas se realizó para el periodo del año 2000 al <= /span>2022, junto con una proyección para = el año 2044 que fue elaborada en el software Idrisi Selva v.17 y ArcGIS 10.8. Objetivo: Analizar los cambios de cobertura y el uso del suelo de la cuenca del río Esmeraldas para el periodo del año 2000 al 2022 con proyección para el año 2044. Metodología: Para esta investigación se establecieron 2 etapas: Delimitación del área de estudio, seguido de la obtención de la información cartográfica de las coberturas y uso de suelo, las que fueron adquiridas del portal del ministerio de ambiente, agua y transición ecológica. Resultados: La tasa de cambio de cobertura y uso de suelo fue= la siguiente: Bosque -73.94%, tierra agropecuaria 12.= 68%, zona antrópica 100= .00%, Vegetación Arb y Herb -98.70%, Otras Tierras -82.48%, Cuerpo de Agua -89.21%. Conclus= ión: El análisis multitemporal demostró los cambios que tuvieron las coberturas de la cuenca del río Esmeraldas en un periodo de 22 años con el fin de dar a conocer como las actividades humanas influyen en los cambios de cobertura y el uso del sue= lo. Área de estudio general: Ecología y medio ambiente. Área de estudio específica: Hidrología.

 =

 

Keywords:Esmeraldas River watershed, land use, anthropic zone, multitemporal analysis, proje= ction.<= /o:p>

 

Abstract

Introduction: The multitempora= l analysis of the land cover and land use of the Esmeraldas River basin was conducted for the period from = 2000 to 2022, along with a projection for the year 2044 that was prepared in the Idrisi Selva v.17 and ArcGIS 10.8 software. Objective: To analyze changes in land cover and land use= in the Esmeraldas River basin for the period from 2000 to 2022 with a projec= tion for 2044. Methodology: For this research, 2 stages were established: Delimitation of the study area, followed by obtaining cartographic information on land cover and use, which were acquired from the portal of= the Ministry of Environment, Water and Ecological Transition. Results: The rate of change in = land cover and land use was as follows: Forest -73.94%, Agricultural Land 12.68%, Anthropic Zone 100.00%, Arb and Herb Vegetation -98.70%, Other Land -82.48%, Water Body -89.21%. Conclusion: The multitemporal an= alysis demonstrated the changes in the coverage of the Esmeraldas River basin ov= er a period of 22 years to show how human activities influence changes in land cover and land use. General area= of study: Ecology and environment. Specific area of study: Hydrology.

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&n= bsp;

Introdu= cción

En Ecuador por medio de la agricultura y la expansión de zonas urbanas se han experimentado intensos cambios de cobertura y el uso del suelo, el aumento demográfico está actuan= do directamente sobre estas áreas, porque cada vez se tienen que sacrificar más área para establecer cultivos y zonas urbanas (Pinos, 2016).

la cobertura y el uso del suelo de la cuenca hidrográfica del río Esmeraldas es un asunto de interés común debido al crecimiento demográfico que ha tenido la sociedad en los últimos años y como resultado de esto se ha producido variaciones entre las coberturas y uso del suelo (García, 2022).

El análisis multitemporal = es un proceso que nos permite predecir futuros escenarios y determinar como el avance de la sociedad está relacionada con la perdida de áreas naturales, E= n la actualidad con las herramientas SIG podemos realizar análisis de las cobert= uras y obtener información de los usos que tiene el suelo, al mismo tiempo se bu= sca demostrar a la sociedad que la degradación del suelo y la contaminación del= agua es un problema irreversible (Pesantez, 2015).

Según Harbaugh (1972 citado en Vásconez et al., 2019), la cuenca hidrográfica es= un área definida topográficamente, drenada por un curso de agua o un sistema conectado de cursos de agua, que dispone de una salida simple para que todo= el caudal efluente sea descargado.

La cuenca del río Esmerald= as corresponde a la vertiente del Pacífico, está formada por tres grandes afluentes como son: el río Guayllabamba, el río Blanco y el río Quinindé, c= on una superficie de 21.669 km².  En e= sta unidad territorial drenan aproximadamente 70 ríos y numerosas quebradas. Su= cauce es navegable desde la confluencia con el río Guayllabamba hasta su desembocadura en el océano Pacífico (Reyes et al., 2022).                               

El presente trabajo tiene = como objetivo realizar el análisis multitemporal de la cobertura y uso de suelo = de la cuenca hidrográfica del rio Esmeraldas en el periodo de los años 2000 al 2022 con una proyección para el año 2044 utilizando los sistemas de informa= ción geográfica, a través de las herramientas Idrisi= Selva v.17 y ArcGIS 10.8, al mismo tiempo esta investigación busca dar a conocer = a la ciudadanía como las influyen actividades humanas al cambio y uso de suelo.<= o:p>

Metodología

Área de estudio

La cuenca hidrográfica del= río Esmeraldas está ubicada al noroeste de la Provincia de Esmeraldas abarca territorio de Pichincha, Santo Domingo, Imbabura, Manabí y Cotopaxi,  la topografía de la cuenca hidrográfica = va desde 0 Hasta 5896 m s.n.m, ocupa el 5to lugar = en las cuencas nacionales, esta unidad territorial posee una área de 21 658.4 Km2 donde se encuentran las fuentes hídricas: el Blanco, Guayllabamba, Toachi, Pilatón y Esmeraldas, cabe destacar que el rio Esmeraldas desemboca en el o= céano Pacífico (Dorigo, 2012).                                                =                         

Figura 1=

Localización de área de trabajo

 

= Obtención de información cartográfica

La información cartográfica de la cobertura y uso = de suelo se obtuvo del portal del ministerio de ambiente, agua y transición ecológica (MAATE), La selección de la cobertura se realizó en el mapa inter= activo del (MAATE) Procediendo a escoger la capa de cobertura y uso de suelo del a= ño 2000 y 2022 considerando que estas coberturas están en escala 1:100 000 para luego descargarlas en formato Shapefile = para procesar la información en el software ArcGIS 1= 0.8, Una vez cargada la información en ArcGIS se pro= cedió a recortar la cobertura general con base a Shapefil= e de la cuenca del río Esmeraldas, continuando con el procesamiento de la información  seleccionamos las cobe= rturas y nos dirigimos a propiedades de capa en la opción  en simbología   para luego  en categorías colocar las coberturas que en este caso son: bosque , tierra agropecuaria, otras tierras , vegetación arbustiva y herbácea, zona antrópicas y  cuerpo de agua, una  vez categorizada y simbolizadas las cap= as se elaboró el mapa de coberturas y usos de suelo para el años 2000 y 2022.

La proyección de cobertura para el año 2044 se rea= lizó con las de cobertura y uso de suelo del año 2000 y 2022 convirtiendo los archivos de formato Shapefile a ráster para reclasificarlos y convertirlos en archivo= s de formato ASCII para procesarlos en software Idrisi selva v.17.

En el software Idrisi = selva v.17 se cargaron las capas de formato ASCII del año 2000 y 2022, para convertirlas archivos de formato (RST), para utilizarlas con la cadena de Márkov para realizar la predicción del cambio a futuro que puede tener la cobertura y el uso del suelo para el año 2044.

El análisis multitemporal se realizó comparando las coberturas del año 2000-2022 y la proyección del año 2044 con el fin de comparar los cambios de coberturas y el uso del suelo que han ocurrido en e= stos periodos de tiempo. con los resultados del procesamiento de los datos se realizó la matriz de transición con el software Excel (tabla 1), para la ma= triz de transición se asignará un código para cada cobertura teniendo en cuenta = que las filas corresponden a las coberturas del primer periodo (tiempo 1), y las columnas corresponden al segundo periodo (tiempo 2), al completar la matriz= de transición los valores de cobertura que se muestran diagonales son que no h= an sufrido cambios en este periodo de tiempo (Niño, 2020).

Tabla 1

Matr= iz de códigos de la tabulación cruzada entre los años 2000-2022

Cobertura/Uso de suelo

Código

Año 2

Bosque

Tierra Agropecuaria

Vegetación Arb y Herb

Zona Antrópica <= /o:p>

Otras Tierras

Cuerpo de Agua

10<= /i>

20<= /i>

30<= /i>

40<= /i>

50<= /i>

60<= /i>

Año 1

Bosque

1

11<= /i>

21<= /i>

31<= /i>

41<= /i>

51<= /i>

61<= /i>

Tierra Agropecuaria

2

12<= /i>

22<= /i>

32<= /i>

42<= /i>

52<= /i>

62<= /i>

Tabla 1

Matriz de códigos de la tabulación cruzada entre los años 2000-2022 (continuación)

Cobertura/Uso de suel= o

Código<= /i>

Año 2

Bosque =

Tierra Agropecuaria

Vegetación Arb y Herb

Zona Antrópica

Otras Tierras

Cuerpo de Agua

10<= /i>

20<= /i>

30<= /i>

40<= /i>

50<= /i>

60<= /i>

Año 1

Vegetación Arb y Herb

3

13<= /i>

23<= /i>

33<= /i>

43<= /i>

53<= /i>

63<= /i>

Zona Antrópica <= /o:p>

4

14<= /i>

24<= /i>

34<= /i>

44<= /i>

54<= /i>

64<= /i>

Otras Tierras

5

15<= /i>

25<= /i>

35<= /i>

45<= /i>

55<= /i>

65<= /i>

Cuerpo de Agua

6

16<= /i>

26<= /i>

36<= /i>

46<= /i>

56<= /i>

66<= /i>

&n= bsp;

Resultados

Cobertura vegetal y uso del suelo 2000 2022=

En la cobertura y uso de s= uelo del año 2000 (figura 2), se puede observar que la categoría de tierra agropecuaria fue la categoría que tenía mayor proporción para ese año con u= n área de 1163157.20 hectáreas, la que corresponde a 53.71% del área total de la cuenca. La segunda categoría con mayor superficie correspondió a bosque con 681048.22 hectárea, que sería el 31.45% de la superficie total, la categorí= a de vegetación arbustiva y herbácea ocupó el 3er lugar contando con 265309.25 hectáreas, que en porcentaje corresponde al 12.25% del área, la categoría z= ona antrópica en el año 2000 tenía 31480.92 hectáreas o 1.45% del área de la cuenca, otras tierras tuvieron un área de 11925.31 hectáreas, que en porcen= taje es el 0.55% y la categoría cuerpo de agua tuvo 0.60% del área total de la cuenca, que son 12900.76 hectáreas (tabla 2).

En la cobertura y uso de s= uelo del año 2022 (figura 3) se puede apreciar que la categoría de tierra agrope= cuaria continuó siendo la categoría con mayor superficie de la cuenca del río Esmeraldas, la categoría de tierra agropecuaria en 2022 tuvo una superficie= de 1310623.06 hectáreas, que corresponde a un 60.51% de las coberturas, la categoría de bosque cuenta con el 23,25% de la cobertura de la cuenca, que = son 503584.00 hectáreas, vegetación arbustiva y herbácea tuvo para el año 2022 261865,37 hectáreas, que seria 12.09 %. Estos datos se pueden comprobar en = la tabla 2. Siguiendo con las coberturas tenemos la zona antrópica con 68395.52 hectáreas, que corresponde al 3.16% de la superficie total, otras tierras t= ienen 9845.50 hectáreas que corresponde a 0,45% de la cuenca y la categoría de cuerpo de agua cuenta co= n 11508.21 hectáreas que es el 0.53% = del área de la cuenca.

 

Figura 2                                                  =                   Figura 3

Cobertura y uso de suelo del año 2000         Cobertura y uso de suelo del año 2022

 

= Cambio de cobertura vegetal y uso del suelo 2000 2022 

El cambio de cobertura par= a el periodo 2000-2022 (tabla 2), se observa que la categoría de tierra agropecu= aria tiene un cambio neto de 147465.86 hectáreas y una tasa de cambio de 12.68%,= la cobertura de bosque en 2000-2022 tuvo un cambio neto de 177464.22 hectáreas= con una tasa de cambio -73.94%, la categoría de veget= ación arbustiva y herbácea tuvo un cambio neto de 3443.88 hectáreas, con una tasa= de cambio de -98.70%, la categoría de zona antrópica tiene un cambio neto de 36914.60 hectáreas y una tasa de cambio  <= /span>>100%, la cobertura de otras tierras en tiene un cambio neto de superficie 2079.81 hectáreas con una tasa de cambio de -82.56 %, cuerpo de agua tiene un cambi= o de 1392.55 hectáreas con una tasa de -89.21% (tabla 2 y figura 4).

Tabla 2<= /b>

Cambio de cobertura y uso de suelo año 2000-2022=

Categoría=

Bosque

Tierra Agropecuaria

Vegetació= n Arb y Herb

Zona Antrópica

Otras Tie= rras

Cuerpo de Agua

Cobertura= y uso de suelo año 2000 (Ha)

681048.22=

1163157.2= 0

265309.25=

31480.92<= o:p>

11925.31<= o:p>

12900.76<= o:p>

Cobertura= y uso de suelo año 2022 (Ha)

503584.00=

1310623.0= 6

261865.37=

68395.52<= o:p>

9845.50

11508.21<= o:p>

 

Tabla 2<= /b>

Cambio de cobertura y uso de suelo año 2000-2022= (continuación)

Categoría=

Bosque

Tierra Agropecuaria

Vegetació= n Arb y Herb

Zona Antrópica

Otras Tie= rras

Cuerpo de Agua

Cambio neto entre 2000-2022 (Ha)

177464.22=

147465.86=

3443.88

36914.60<= o:p>

2079.81

1392.55

Tasa de cambio (%)

-73.94%

12.68%

-98.70%

100.00%

-82.56%

-89.21%

 

Figura 4                                                  =                               Figura 5

Tasa de cambio 2000-2022 =                                       Cambio o persistencia 2000-2022    

Perdida y ganancia de cobertura y uso de suelo 2000-2022

Los resultados de la tabla 3, corresponde a la mat= riz de transición del año 2000-2022, Las superficies que se muestran en la fila= de tiempo 1 (2000), corresponde perdida superficie de las siguientes categoría= s: Bosque ha perdido en 22 años 221570.10 hectáreas, la categoría de tierra agropecua= ria ha perdido 106354.80 hectáreas, vegetación arbustiva y herbácea 48680.50 hectáreas, la categoría de zona antrópica  no ha perdido superficie 0.00 hectáreas, la  categoría de Otras tierras perdió una superficies de 5288.90 hectáreas y cuerpos de agua perdió una superficie de 4020.20 hectáreas. Las superficies de la columna tiempo 2 (2022) correspond= en las Ganancia que han tenido las siguientes categorías: Bosque ha ganado 441= 13.20 hectáreas, Tierra agropecuaria 253822.30 hectáreas, vegetación arbustiva y herbácea, 47103.76 hectáreas, zona antrópica 36914.60 hectáreas, otras tier= ras 1332.96 hectáreas y cuerpo de agua gano 2667.64 hectáreas.

Tabla 3<= /b>

Matriz de códigos de la tabulación cruzada entre los años 2000-2022

Cobertura / Uso suelo

Tiempo 2 (2022)

Bosque

Tierra Agropecuaria

Vegetació= n Arb y Herb

Zona Antrópica

Otras Tie= rras

Cuerpo de agua

Tiempo 1 (2000)

Bosque

459478.10

208204.20=

11094.20<= o:p>

1836.60

223.30

211.90

Tierra Agropecuaria

40460.90<= o:p>

1056802.40

31419.60<= o:p>

31621.70<= o:p>

551.30

2301.40

Vegetació= n   Arb y Herb

3507.30

41249.50<= o:p>

214761.60

3283.70

551.30

88.80

Zona Antrópica

0.00=

0.00=

0.00=

31480.90

0.00=

0.00=

Otras Tie= rras

92.50

683.50

4452.10

35.20

6636.50

25.60

Cuerpos de Agua

52.60

3685.20

137.80

137.50

7.10=

8880.60

Total 200= 0

681048.20=

1163157.2= 0

263442.10=

31480.90<= o:p>

11925.30<= o:p>

12900.80<= o:p>

Total 202= 2

503591.30=

1310624.7= 0

261865.40=

68395.50<= o:p>

7969.40

11508.20<= o:p>

 

Perdida

221570.10=

106354.80=

48680.50<= o:p>

0.00=

5288.90

4020.20

 

Ganancia =

44113.20<= o:p>

253822.30=

47103.76<= o:p>

36914.60<= o:p>

1332.96

2627.60

 

Figura 6

Perdida - ganancia cobertu= ra y uso de suelo 2000-2022

Cobertura vegetal y uso del suelo 2022 -2044

En la cobertura y uso de s= uelo del año 2022 se puede observar que la categoría de tierra agropecuaria es l= a superficie que se encuentra en mayor proporción con un área de 1310623,06 hectáreas, q= ue corresponde al 60.51 % del área de la cuenca. La segunda categoría con mayor área son los bosques con 503584.00 hectárea que corresponde a un 23.25% de = la superficie total. En 3er lugar está la categoría de vegetación arbustiva y herbácea con 261865.37 hectáreas, que en porcentaje corresponde al 12.09% d= el área.                 En 4to lugar = está la categoría zona antrópica con 68395.52 hectáreas o 3.16% del área total d= e la cuenca, categoría de otras tierras tiene un área de 9845.50 hectáreas que s= ería 0.45% del área total, y la cobertura de cuerpo de agua tiene el 0.53% de ár= ea total que en hectáreas sería de 11508= .21 (tabla 4).

En la cobertura y uso de suelo del año 2044 se  puede apreciar que el 1er lugar lo tend= rá la categoría de tierra agropecuaria con una superficie  para el 2044 de 1294589.49 hectáreas, q= ue corresponderá al 59.77 % del área; el 2do lugar lo tendrá la categoría de bosque que contará con 411372.71 hectáreas, que corresponde al  18.99%; 3er lugar lo tendrá la categorí= a de vegetación arbustiva y herbácea que  contará p= ara el año 2044 con 288465.83 hectáreas, que en porcentaje seria 13.31%, datos que= se pueden comprobar en la tabla 4. En 4to lugar esta las coberturas de zona antrópica con 147758.47 hectáreas, que corresponde al 6.92 % del área de la cuenca, la categoría de otras tierras tendrá 9672.86 hectáreas, esta superf= icie corresponde a 0.44 % del área de la cuenca, la categoría de cuerpo de agua tendrá 13962.30 hectáreas, que en porcentajes es 0.64% del área total de la cuenca del río Esmeraldas para el año 2044.

Figura 7                                                          Figura 8

Cobertura y uso de suelo del año = 2022         Cobertura y uso de suelo del año = 2044

  =

Cambio de cobertura vege= tal y uso del suelo 2022 2044

El cambio de cobertura para el periodo 2022-2044 (= tabla 4),  se observa que la categoría de tierra agropecuaria tendrá un cambio neto de 16033= .57  hectáreas y una tasa de cambio de -98.7= 8%, en la cobertura de bosque se logra apreciar que del 2022-2044 disminuirá 92211= .28 hectáreas con una tasa de cambio -81.69%,  la categoría de vegetación arbustiva y herbácea reducirá 26600.46 hectáreas con una tasa de cambio de 10.16%, en la categoría de zona antrópica tiene un cambio de 79362.95 hectáreas  y una tasa de cambio del 100%, la cober= tura de otras tierra hará un cambio de superficie para 2044 de 172,64 hectáreas = con una tasa de cambio de -98.25%, cuerpo de agua tendrá un cambio de 2454.09 hectáreas con una tasa de 21.32% (figura 9 y 10).

Tabla 4<= /b>

Cambio de cobertura y uso = de suelo año 2022-2044

Cat= egoría

Bos= que

Tie= rra Agropecuaria

Veg= etación Arb y Herb

Zona Antrópica

Otr= as Tierras

Cue= rpo de Agua

Cob= ertura y uso de suelo año 2022 (Ha)

503584,00<= /span>

1310623,06=

261865,37<= /span>

68395,52

9845,50

11508,21

Cob= ertura y uso de suelo año 2044 (Ha)

411372,71<= /span>

1294589,49=

288465,83<= /span>

147758,47<= /span>

9672,86

13962,30

Cam= bio neto entre 2022-2044 (Ha)

92211,28

16033,57

26600,46

79362,95

172,64

2454,09

Tas= a de cambio

-81,69%

-98,78%

10,16%

100,00%

-98,25%

21,32%

 

Figura 9          =                                                Figura 10

Tasa de cambio (%) 2022-2044                    Cambio o persistencia 2022-204= 4

  

 

Perdida y ganancia de cobertura y uso de suelo 2022-2044

Los resultados que se observan en el (tabla 5), corresponde a la matriz de transición del año 2022-2044, las superficies qu= e se muestran en la fila de tiempo 1 (2022), corresponde a la superficie de la siguientes categorías: bosque perderá en 22 años 156973.98 hectáreas, la categoría de tierra agropecuaria perderá en 2044 187852.35 hectáreas, vegetación arbustiva y herbácea perderá 35052.43 hectáreas, zona antrópica perderá 11360.99 hectáreas, la categoría de otras tierras perderá una super= ficies 4753.13 hectáreas, cuerpos de agua perderá una superficie de 8498.17 hectár= eas. Las superficies que se observa en la columna de tiempo 2 (2044) corresponde= n las ganancias que han tenido las siguientes categorías: bosque ganara en 22 años 65442.26 hectáreas, tierra agropecuaria ganara 171617.48 hectáreas, vegetac= ión arbustiva y herbácea 61447.89 hectáreas, zona antrópica ganara 90525.45 hectáreas, otras tierras ganara 4640.75 hectáreas y cuerpo de agua ganara 10817.21 hectáreas. Con base a la proyección realizado de la perdida y gana= ncia de cobertura y uso de suelo para el año 2044, teniendo en cuenta que los resultados obtenidos del cambio de uso de suelo son escenarios son preocupa= ntes porque en 22 años desaparecerá una gran superficie de los bosques por los aumentos demográficos. Según Mieles & Jaramillo (2020), un descontrolado aumento demográfico lleva a la desforestación del bosque con el objetivo de obtener madera para construcciones, áreas para tierras de pastoreo o actividades agrícolas.

Tabla 5

Matriz de transición de las categorías de uso de suelo entre 2022- 2044

Tiempo 2 (2044)

Cobertura / Uso suelo

Bosque

Tierra Agropecuaria

Vegetació= n Arb y Herb

Zona Antrópica

Otras Tie= rras

Cuerpo de agua

Tiempo 1 (2022)

Bosque

343675,58<= /span>

138906,56

11856,04

4879,03

125,48

1206,88

Tierra Agropecuaria

59275,96

1119268,24=

42746,29

77486,17

1033,13

7310,79

Vegetació= n Arb y Herb

4487,00

20740,45

224194,54<= /span>

7545,50

1949,95

329,53

Zona Antrópica

1050,33

4107,85

2711,36

56756,52

1532,19

1959,26

Otras Tie= rras

85,81

1031,12

3610,67

14,78

4819,90=

10,75

Cuerpos de Agua

543,16

6831,51

523,54

599,96

0,00

3000,19=

Total 200= 0

500649,56

1307120,59

259246,97

68117,51

9573,03

11498,36

Total 202= 2

409117,84

1290885,72

285642,44

147281,96

9460,65

13817,40

Perdida

156973,98

187852,35

35052,43

11360,99

4753,13

8498,17

Ganancia =

65442,26

171617,48

61447,89

90525,45

4640,75

10817,21

 

Figura 11

Perdida o ganancia cobertura y us= o de suelo 2022-2044

=

= Discusión

El análisis multitemporal de la cobertura y uso de suelo de la cuenca del río Esmeraldas permitió conocer, que la cuenca del r= ío Esmeraldas en el año 2000 tuvo una superficie de 681048.22 hectáreas de bos= que, que para el 2022 fue de 503584.00 hectáreas, por lo tanto tuvo un cambio ne= to de 177464.22 hectáreas, estos resultados representan un caso preocupante po= r la pérdida de bosque  teniendo en cuen= ta los que mencionó García (2016), los bosques tienen gran importancia en la segur= idad alimentaria, por el motivo que son parte esencial para reservar alimentos p= ara cubrir las necesidades alimentarias  en el futuro,  al afectar nuestros  bosques en consecuencia tendremos que m= igrar a otras tierras fértiles y con disponibilidad de agua con el fin de  cubrir nuestras necesidades esenciales =  pero debemos recordar que la búsqueda de= otras tierras por causa de las desforestación y desertificación son situaciones c= ada vez más comunes a la que nos enfrentamos si no tomamos las debidas precauci= ones al manejar los bosques (Falc= ón, 2014).  

La categoría de tierra agropecuaria al contrario d= el bosque ha aumento la superficie de 1163157.20 hectáreas en el año 2000 a 1310623.06 hectáreas para el año 2022. Cuando nos referimos al uso de la tierra se con= oce que cada vez se necesita más superficie para la producción agropecuaria, pe= ro debemos tener en cuenta que el sector agropecuario en Ecuador es esencial p= ara la economía del país por el motivo de que representa el 29,4% la población económicamente activa (Pino et al. 2018).

La categoría zona antrópica en 22 años pasaron a t= ener 31480.92 hectáreas a 68395.52 hectáreas, por tanto dentro de las categorías= de coberturas y usos de suelo considero que estas tres son las que tienen mayor influencia en los cambio de coberturas y uso de suelo que se dan en la cuen= ca del Río Esmeraldas, por el motivo que los porcentajes de desforestación de bosq= ue que se han dado el Ecuador están ligados en un 99,4% a la transformación de bosque en áreas agropecuaria, 0,37% a la creación de infraestructuras, zonas urbanas, zonas rurales y 0,37% a otros (Sierra, 2013). A medida que la soci= edad aumenta los bosques pierdan superficie y las tierras agropecuarias y antróp= icas aumenta su área, por otra parte considero que las categorías analizadas como son: vegetación arbustiva y herbácea, otras tierras y cuerpos de agua no ti= ene gran influencia en los cambios de categoría y uso de suelo de la cuenca del= río Esmeraldas.

La pérdida de superficie de la cobertura y uso de suelo se realizó comparando las coberturas del periodo 2000-2022, según el análisis multitemporal tenemos que los bosques perdieron 221570.13 hectárea= s, tierras agropecuarias 106354,82 hectáreas, vegetación arbustiva y herbácea 48680.46, zona antrópica no perdió superficie, la categoría otras tierras perdió 5288= .86 hectáreas y cuerpo de agua perdió 4020,19 hectáreas estos resultados se obtuvieron por medio de la matriz de transición dado que en un análisis de cobertura/ uso de suelo la matriz de transición identifica los cambios o la persistencia de cada una las coberturas considerando que es una metodología donde se comparan dos mapas o coberturas de diferentes periodos (García, 20= 16). Analizando las coberturas 2000 y 2022 donde se obtuvieron los resultados de perdida de suelo, considerando que el análisis está en un intervalo de 22 a= ños, la sociedad ha influido en las coberturas y el uso suelo se sabe que la población que se encuentra dentro de esta cuenca aprovecha los recursos que ofrece la cuenca, pero al mismo tiempo  la población está produciendo afectacion= es que pueden ser  irreversibles para la c= uenca hidrográfica como menciona Blacio (2015), la contaminación de las cuencas hidrográficas = se produce por la gestión inadecuada de los desechos humanos, acumulación de aguas residuales, agroquímicos, el sector minero, falta de un sistema de potabilización del agua para el consumo humano y falta de progra= mas de educación ambiental para mitigar la contaminación cuencas hidrográficas.=

Las ganancias de superfici= e de la cobertura para el periodo 2000-2022 según el análisis multitemporal tene= mos que los bosques ganaron 44113.19 hectáreas, tierras agropecuarias 253822.30 hectáreas, veg= etación arbustiva y herbácea 47103.76, zona antrópica gano 36914= .60, la categoría otras tierras gano 1332.96 hectáreas y cu= erpo de agua 2627.64 hectáreas. En = este caso se puede notar que la cobertura de bosque, vegetación arbustiva y herbácea, otras tierra y cuerpo de agua han perdido más área de la que gana= ron, pero en el caso de tierra agropecuaria y zonas antrópica ganaron más área d= e lo que perdieron considerando que los asentamientos humanos han provocado afectaciones en el uso del suelo, los habitantes de las cuencas hidrográfic= as al construir sus viviendas cerca de los pozos de agua y los productores agrícolas que construyen en estas zonas sistemas de riego para los sembríos= por sus actividades pueden provocar degradación del suelo, a su vez afectacione= s a la flora y fauna (Pérez & Oviedo, 2019). Por lo tanto, tierra agropecua= ria y zona antrópica son las coberturas que más beneficiadas los cambio que se producen en la cuenca.

La proyección del 2044 se realizó con las cobertur= as del 2000 y 2022 proyectándolo  para= el 2044 las categorías y uso de suelo tendrán las siguientes superficies: tier= ra agropecuaria tendrá 1294589.49 hectáreas, los bosque tendrán 411372.71 hectáreas, vegetación arbustiva y herbácea contara para el año 2044 con 288= 465.83 hectáreas también tendremos la zona antrópica con 147758.465 hectáreas, “ot= ras tierras” tendrá 9672,858 hectáreas y cuerpo de agua tendrá  13962.299, esta proyección  para el 2044 es  preocupante porque en 22 años  según la proyección se  perderán 156973.98 hectáreas de bosque = por lo tanto tendremos problemas grabes con las áreas naturales, por este motivo e= n la actualidad el territorio es uno de elementos más importantes por esta razón= los recursos naturales que hay dentro de este territorio se pueden aprovechar c= on la condición de que no se afecte la sostenibilidad  de lo contrario se podría producir incr= emento descontrolado en el cambio y uso de suelo, crisis alimentarias, contaminaci= ón y desforestación (Vidal, 2023).

= Conclusión

·      =    En el estudio multitemporal se demostr= ó y se proyectó el cambio que tendrán la cobertura / uso de suelo de la cuenca = del rio Esmeraldas en periodos de 22 años, 2000-2022, 2022-2044 para comprobar = como las actividades influyen en los cambios de cobertura, esto se respaldaron c= on los mapas realizados en Arcgis y con la proyecc= ión con software Idrisi v17, lo cual permitió model= ar para el 2044 la cantidad de hectáreas que tendrá cada categoría de cobertura/uso de suelo.                   

·      =    El estudio se realizó con la ayuda de = los (SIG) sistemas de información geográficos que son herramientas que cada día= van teniendo mayor importancia para la ingeniería y otra área las cuales se encargan del estudio de la tierra.

·      =    Este estudio también tiene como objeti= vo para demostrarle a la sociedad como las cuencas hidrográficas puede cambiar= a medida que pasa el tiempo y por las actividades que realizan los habitantes= .

Conflicto de intereses

Los autores declaran que no existe conflicto de intereses en relación con el artículo presentado.

= Referencias Bibliográficas              

Blacio Vásquez, J. J. (2015). Factores que inciden en la contaminación de las cuencas de agua para consumo en las parroquias de huertas, Muluncay y Arcapamba, pertenecientes al cantón Zaruma, d= urante los meses de diciembre 2013 y enero 2014 [Tesis de pregrado, Universidad Técnica de Machala, Machala]. https://rraae.cedia.edu.ec/Record/UTMACH_cb5e62e0d7a19aba6a0141be10cef871

Dorigo<= /span> Bravo, L. (2012). Técnicas regionales hidrológicas para la estimación de caudales máximos aplicadas a = la cuenca del río Esmeraldas [Tesis de pregrado, Universidad Santia= go de Guayaquil, Guayaquil, Ecuador].

Falcón García, O. (2014). Diná= mica de cambio en la cobertura uso del suelo, en una región del estado de Quinta= na Roo, México: el impacto de las políticas gubernamentales sobre el manejo forestal comunitario [Tesis de maestría, Universidad Nacional Autónoma = de México, México]. http://132.248.9.195/ptd2014/enero/0707773/0707773.pdf

García Culqui, C. L. (2022). Análisis multitemp= oral de la dinámica de uso de suelo y cobertura vegetal en la microcuenca del rí= o Illangama [Tesis de Maestría, Universidad Técnica= de Ambato, Ambato, Ecuador]. 

García Marín, M. E. (2016). La deforestación: una práctica que agota nuestra biodiversidad. Revista Producción + Limpia, 11(2), 161-168. http://revistas.unilasallista.edu.co/index.php/pl/= article/view/1247/1038

            http://repositorio.ucsg.edu.ec/handle/3317/1194

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Mieles Giler, J. W. & Jaramillo Véliz, J. J. (2020). Crecimiento demográfico e impacto ambiental de la parroquia Andrés = de vera del cantón Portoviejo. Revista ALLPA, 3(6), 22-32 https://publicacionescd.uleam.edu.ec/index.php/all= pa/article/view/64/140

Niño Martínez, Y. M. (2020). Análisis multitemp= oral mediante imágenes de sensores remotos para la determinación de los cambios = de uso de suelo en el municipio de san francisco de sales, Cundinamarca (Colom= bia) entre los años 90’s y 2018 [Tesis de maestría, Universidad Nacional de = La Plata, Buenos Aires, Argentina].

Pérez Rodríguez, N. & Oviedo Álvarez, V. (2019= ). Medio ambiente, medio ambiente urbano y administración pública.  Revista Espacios Universidad de la H= abana, (287), 175-184. https://revistas.uh.cu/revuh/article/view/2742

Pesantez Pacheco, P. G. (2015). Clasificación y predicción de cambio de cobertura de suelo de la cuenca del rio Paute utilizando herramientas geo informáticas [Tesis de Maestría, Universidad Estatal de Cuenca, Cuenca, Ecuador].  https://dspace.ucuenca.edu.ec/bitstream/123456789/= 21445/1/tesis.pdf

Pino Peralta. S. L., Aguilar, H. R., Apolo Loaiza,= G. E., & Sisalema Morejón, L. A.  (2018). Aporte del sector agropecuario = a la economía del Ecuador. Análisis crítico de su evolución en el período de dolarización. Años 2000 – 2016. Revista Espacios, 39(32), 1-11. https://www.readbag.revistaespacios.com/a18v39n32/= a18v39n32p07.pdf

Pinos Arévalo, N. J. (2016). Prospectiva del us= o de suelo y cobertura vegetal en el ordenamiento territorial - Caso cantón Cuen= ca. Revista Estoa, 9(5), 7-19. https://publicaciones.ucuenca.edu.ec/ojs/index.php= /estoa/article/view/1019/887

Reyes Vera, C. H., González Quiñonez, L. A., Ceval= los Mina, M. G., Realpe Bolaños, K. R., Estrada Vásquez, E. L., & Delgado <= span class=3DSpellE>Rezavala, F. J. (2022). Fragmentación del paisaje en = la cuenca del Río Esmeraldas – Ecuador. Revista Sapien= za, 3(1), 1227-1238. file:///C:/Users/tcarr/Downloads/20.+FRAGMENTAC= I%C3%93N+DE+PAISAJE.pdf

Sierra, Rodrigo. (2013). Patrones y factores de deforestación en el Ecuador continental, 1990-2010. Y un acercamiento a los próximos 10 años. Editorial Conservación internacional Ecuador y Forest Trends. Quito, Ecu= ador.

Vásconez, M., Mancheno, A., Álvarez, C., Prehn, C., Cevallos, C., & Ortiz, L. (2019). C= uencas Hidrográficas. Editorial de la Universidad Politécnica Salesiana.
https://dspace.ups.edu.ec/handle/123456789/19038

Vidal Urrunaga, B. L. (2023). Análisis de los asentamientos humanos informales en el cantón La Libertad, provincia de San= ta Elena [Tesis de Maestría, Universidad = San Gregorio de Portoviejo, Portoviejo]. http://repositorio.sangregorio.edu.ec/handle/12345= 6789/3033

 

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ISSN: 2600-5859<= /span>

Vol. 7 No. 2, pp. 178 – 195, abril= - junio 2024

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www= .concienciadigital.org

 

                                      Estado del Arte                      Página 178 | 195

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