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Evaluación del impacto ambiental de los sistemas de alcantarillado sanitario y planta = de tratamiento de aguas residuales en Ecuador

 Environmental impact assessment of sanitary sewer systems and <= span class=3DSpellE>wastewater treatment plant in Ecuador

 

Gabriela Cecilia Guerra Herrera. [1], = Santiago Israel Logrońo Naranjo. [2= ]

 

Recibido: 10-= 05-2019 / Revisado: 19-06-2019 /Aceptado: 06-07-2019/ Publicado: 28-07-2019

 

 Abstract. =                                 DOI: https://doi.o= rg/10.33262/cienciadigital.v3i3.2.1.783

 

The satisfaction degree of a society is generally based on the benefits that it possesses, being one of the most essential the provision of basic services = such as sanitary sewer and wastewater treatment plants, which not only improve t= he quality of life but also seeks to preserve the water quality of the water bodies where the wastewater generated is discharged.

Although it= is true, these systems provide wellness to the population, however, during the construction of the same, a series of activities that can generate potential risks to human health and environmental factors occur, these risks called Environmental Impacts when measured, they provide a clear idea of ​​the level of incidence that construction, maintenance, closure and abandonment operations produce.

It is for t= his reason, that in this article the evaluation of the impacts that are expecte= d to be generated by the construction, operation, maintenance, closure and abandonment of a Sanitary Sewer System and typical Wastewater Treatment Pla= nt, based to the methodology of Conesa et al (1997), obtaining as a result, that this type of project generates a moderate and temporary negative impact; Therefore, positive impacts are also generated that mostly cover the genera= tion of employment in each of its activities.

Of 152 impa= cts identified, 59% corresponded to those of a positive nature, while the negat= ive ones represented 41%, indicating in this way that the provision of basic services generates inconveniences in its first stage of construction, howev= er from this, it presents benefits for the population by providing better wastewater evacuation systems, controlled and directed towards treatment plants, where sewage can recover its quality and be discharged complying wi= th the permissible discharge limits.

Keywords: Environmental impact, sewer, sanitary, wastewater.=

 

Resumen.

 

El grado de satisfacción de una sociedad generalme= nte se basa en los beneficios que posee, siendo uno de los más imprescindibles = la dotación de servicios básicos como el alcantarillado sanitario y las planta= s de tratamiento de aguas residuales, que no sólo mejoran la calidad de vida, si= no que busca preservar la calidad de agua de los cuerpos hídricos donde se descarga las aguas residuales generadas.

Si bien es cierto, estos sistemas proporcionan bienestar a la población, no obstante, durante la construcción de estos se producen una serie de actividades que por su propia naturaleza pueden gener= ar potenciales riesgos a la salud humana y a los factores ambientales, estos riesgos llamados Impactos Ambientales al ser medidos proporcionan una idea clara del nivel de incidencia que las operaciones de construcción, mantenimiento, cierre y abandono producen.<= /p>

Es por esta razón, que en = el presente artículo se realizó la evaluación de los impactos que se prevé se generen por la construcción, operación, mantenimiento, cierre y abandono de= un Sistema de Alcantarillado Sanitario y Planta de Tratamiento de Aguas Residu= ales típicos, en base a la metodología de Conesa et al (1997), obteniendo como resultado, que este tipo de proyectos generan un impacto negativo moderado y temporal; por lo que también se generan impactos positivos que abarcan en su mayoría la generación de empleo en cada una de sus actividades.<= /span>

De 152 impactos identificados, el 59% correspondie= ron a los de carácter positivo, mientras que los negativos representaron el 41%, indicando de esta manera, que la dotación de servicios básicos genera inconvenientes en su primera etapa de construcción, sin embargo a partir de esta, presenta beneficios para la población proporcionando mejores sistemas= de evacuación de aguas servidas, controlados y dirigidas hacia plantas de tratamiento, donde las aguas negras podrán recuperar su calidad y ser verti= das cumpliendo los límites permisibles de descarga.

Palabras claves: Impacto ambiental, alcantarillado sanitario, aguas residuales.=

Introducción.

El ser humano en= su propia esencia utiliza los diversos recursos naturales para satisfacer sus necesidades primordiales, es así como el uso de las fuentes hídricas en las diversas actividades: domésticas, industriales, recreativas o agrícolas gen= eran un posible deterioro de estas.

En sus hogares, = la población usa el agua principalmente para la cocción, limpieza o aseo, de manera que una vez satisfecha sus necesidades básicas se presenta el proble= ma de evacuar las aguas residuales generadas. Para esto, se requiere de la construcción e implementación de un sistema de alcantarillado sanitario que elimine o conduzca estas aguas negras hacia una planta de tratamiento, que proporcione las alternativas adecuadas para el tratamiento de estas, que modifiquen las características del recurso hídrico, y así cumplan con las normativas de descarga y a su vez no generen un riesgo para la vida acuátic= a de los cuerpos hídricos donde se descargan. (SIAPA, 2014).

Carmona (2013) define los sistemas de alcantarillado sanitario como un conjunto de conduct= os y estructuras destinados a recibir, evacuar, conducir y disponer las aguas domésticas, que por lo general son aguas negras.

Estos sistemas de tuberías constituyen la red principal de conducción de las aguas residuales desde los hogares hacia las plantas de tratamiento ya sea municipales o privadas, donde se someterán a los procesos necesarios para su regeneración= .

Es entonces, que= las plantas de tratamiento son un conjunto de procesos u operaciones de carácter físico, químico, biológico o una combinación de todos estos, con la finalid= ad de eliminar los materiales, sustancias o microorganismos patógenos para el = ser humano, animales o vegetales, evitando por lo tanto la contaminación de los cuerpos receptores (Aldás, 2011).

El grado de trat= amiento al que se someterá una determinada agua depende fundamentalmente de los lím= ites de vertido para el efluente, sea alcantarillado, río o mar; y de los contaminantes que ésta contenga, desde sólidos suspendidos hasta metales pesados o contaminantes biológicos. (Ramalho, 1990). Existiendo diversos tratamientos: primarios, secundarios y terciarios.

Según el TULSMA = del Ministerio del Ambiente (2002), el tratamiento primario y secundario incluy= endo la desinfección constituye un tratamiento de tipo convencional, mientras qu= e el terciario es aquel proceso adicional, que permite remover sustancias suspendidas y disueltas que no se han podido eliminar en los tratamientos previos.

Toda actividad encaminada a la construcción, operación y mantenimiento de los sistemas de alcantarillado y plantas de tratamiento de aguas residuales generan posibles afectaciones a los componentes ambientales o a la salud humana; es por esta razón que es necesario una evaluación de éstos, para conocer su grado de incidencia, sea positivo o negativo. Es así como, Orea & Villarino (201= 3), definen al impacto como la alteración que produce una actividad humana en su entorno y que afecta a la calidad de vida de la población; por lo tanto, el Impacto Ambiental será aquellas actividades antrópicas que originen una modificación de alguno de los factores ambientales o del sistema en conjunt= o.

Metcalf y Eddy (1995) recalcan la importancia que tienen los servicios básicos en una comunidad, tal como lo es el alcantarillado sanitario y las plantas de tratamiento de aguas residuales, mismos que proporcionan bienestar físico a= la población acompańado, sin embargo, de la potencialidad de generar o produci= r un fuerte impacto en el medio ambiente si no es ejecutado adecuadamente. =

El presente trabajo, tiene por lo tanto como enfoque principal el ev= aluar de manera general los impactos ambientales causados por las operaciones de construcción, operación y abandono de un Sistema de Alcantarillado Sanitari= o y Planta de Tratamiento de Aguas Residuales en Ecuador, mediante la metodolog= ía establecida por Conesa et al (1997) con su matriz de Leopold, modificada a = la investigación detallada en el presente artículo.

Metodología.

A. Identificación de los procesos de construcción, operación, mantenimiento, cierre y abandono del Sistema de Alcantarillado Sanitario y Planta de Tratamiento de Aguas Residuales.

La iden= tificación de los procesos de construcción y operación del Sistema de Alcantarillado se basa en los trabajos realizados previamente por los diferentes municipios y prefecturas del Ecuador, regidos por los “Términos de Referencia para Estud= io de Impacto Ambiental de Proyectos de Alcantarillado y Aguas Residuales” de = la Guía Metodológica Saneamiento – DNPCA del Ministerio del Ambiente (2015).

Esta gu= ía, divide los procesos tanto para alcantarillado sanitario como para plantas de tratamiento en:

ˇ      =    Etapa de construcción

ˇ      =    Etapa de operación y mantenimiento

Para el presente estudio, además de las etapas propuestas por el Ministerio de Ambiente, se ha considerado importante incluir además la etapa de cierre y abandono y así abarcar a todas las actividades que suceden en este tipo de obras que proporcionan bienestar a la sociedad.

B. Identificación y Evaluación de Impactos Ambientales

Se basa= en la metodología establecida por la “Guía Metodológica para la evaluación del impacto ambiental de Conesa et al (1997), basada en la diferenciación cualitativa y cuantitativa de las causas que producen los impactos ambienta= les.

Se util= iza para esto, la matriz de Leopold modificada, junto con las matrices causa – efecto (seminumérica) que consiste en un cuadro= de doble entada, disponiendo como filas a los componentes ambientales y como columnas aquellas actividades que podrían generar impactos potenciales.

Inicial= mente, se realiza una matriz de identificación, igualmente con un cuadro de doble entrada, en las abscisas las actividades y en el eje de las ordenadas los componentes ambientales, dónde en cada celda se evalúa si existe o no una p= osible afectación marcándola con una X.

Posteri= ormente se procede a evaluar las actividades identificadas como aquellas que genera= n un impacto. Esta valoración se basa en la calificación del grado de magnitud e importancia del impacto identificado, que sigue los siguientes criterios: <= o:p>

Tabla 1. C= arácter del impacto

&n= bsp;

 

Positivo (+)<= /p>

El componente presenta una mejo= ra con respecto a su estado previo a la ejecución del proyecto

Negativo (-)<= /p>

El componente presenta deterioro con respecto a su estado previo a la ejecución del proyecto.

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

Fuente: Co= nesa et al (1997)

 

La Tabla 1 muestra el criterio para identificar si un impacto es negativo o positivo con respecto al estado pre operacional de la actividad.=

            Tabla 2. Intensidad del impacto

 

Alta

Alteración muy notoria y extens= iva, de recuperación a corto o mediano plazo mediante la intervención humana, = lo cual conlleva costos de recuperación

Moderada

Alteración notoria producida por una determinada actividad, el impacto es reducido y se puede mitigar medi= ante técnicas sencillas para su recuperación.

Baja

Impactos que se pueden recuperar naturalmente o mediante la intervención humana.

 

Fuente: Co= nesa et al (1997)

&n= bsp;

La Tabl= a 2 representa el grado con el que un impacto alterará a un determinado compone= nte ambiental.

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

Tabla 3. Extensión del impacto

 

Regional

Área o región geográfica donde = se desarrolla el proyecto.

Local

Aproximadamente hasta 3 km dond= e se realizan las actividades del proyecto.

Puntual

Específicamente en el lugar don= de se realizan las actividades del proyecto, considera el área de influencia directa.

 

Fuente: Co= nesa et al (1997)

 

La exte= nsión del impacto, detallado en la Tabla 3 hace referencia a la extensión especial que un efecto tendrá sobre los componentes ambientales.

Tabla 4. Duración del impacto

 

Permanente

La permanencia del efecto perma= nece o continua a pesar que ya ha finalizado la actividad.

Temporal

El efecto se presenta durante la ejecución de las actividades y finaliza junto con estas.

Periódica

El efecto se presenta de forma intermitente durante la duración de la actividad.

 

Fuente: Co= nesa et al (1997)

 

Es de recalcar, que la duración del impacto se refiere específicamente a la acción sobre los componentes mas no al detalle de los efectos que las actividades puedan causar.

Tabla 5. Reversibilidad del impacto

Irrecuperable=

El componente ambiental afectad= o no podrá ser recuperado.

Poco recuperable

La recuperación es posible únicamente con la ayuda humana.

Recuperable

El componente ambiental se recu= pera de forma natural a un estado similar al inicial previo las actividades del proyecto.

 

Fuente: Co= nesa et al (1997)

 

La tabl= a 5. indica los criterios para la selección de la ponderación en base a la reversibilidad del impacto, es decir, a la dificultad o imposibilidad que tendrá un componente ambiental afectado de que vuelva a sus características= o condiciones originales previo a las actividades del proyecto.

Tabla 6. Riesgo del impacto

 

Alto

El impacto se produce en forma real.

Medio

Existe la duda de que el impact= o se produzca o no.

Bajo

El pacto es probable de que se produzca, no existe una certeza.

 

Fuente: Co= nesa et al (1997)

El ries= go del impacto expresa la probabilidad de que pueda ocurrir el impacto y los crite= rios de selección se detallan en la Tabla 6.

A continuación, se presenta en la Tabla 7 los criterios de ponderación de tod= as las consideraciones vistas anteriormente.

Tabla 7. Criterios de valoración de impactos ambientales

 

Varia= ble

Símbo= logía

Carác= ter

Valor=

Magnitud

        M

Intensidad

i

Alta

3

Moderada

2

Baja

1

Extensión

e

Regional

3

Local

2

Puntual

1

Duración

d

Permanente

3

Temporal

2

Periódica

1

Importancia

         I

Reversibilidad

R

Irrecuperable=

3

Poco recuperable

2

Recuperable

1

Riesgo

g

Alto

3

Medio

2

Bajo

1

Extensión

e

Regional

3

Local

2

Puntual

1

Fuente: Conesa et al (1997)

Cálculo= de Magnitud de Impactos

Constit= uye una valoración del efecto de una acción, se basa en la sumatoria de las variables intensidad, extensión y duración con sus respectivos pesos:<= /o:p>

ˇ      =    Intensidad: 0.40

ˇ      =    Extensión: 0.40

ˇ      =    Duración: 0.20

 

     M =3D (0.40i) + (0.40e) + (0.40d)                                                                                       (1)

 

Cálculo= de Importancia de Impactos

Se basa= en la sumatoria de las variables extensión, reversibilidad y riesgo con sus respectivos pesos:

ˇ      =    Extensión: 0.30

ˇ      =    Reversibilidad: 0.20

ˇ      =    Riesgo: 0.50

I =3D (0.30e) + (0.40r) + (0.40g)=                                                  =                                         (2)

Una vez realizados todos los cálculos mediante las ecuaciones de magnitud e importa= ncia se procede a la interpretación de éstos mediante la “Escala de Valoración d= e la Magnitud e Importancia del Impacto” detallada en la Tabla 8.

Tabla 8. Escala de valoración de la magnitud e importancia del impacto

&n= bsp;

Escala valores estimados

Valor= ación del impacto

1.0 –= 1.6

Bajo<= o:p>

1.7 –= 2.3

Medio=

2.4 -= 3.0

Alto<= o:p>

> = 3.1

Muy A= lto

Fuente: Co= nesa et al (1997)

&n= bsp;

Signifi= cación de Impactos

Consist= e en la realización de una matriz resumen, donde se detallen cuantos impactos ba= jos, medios, altos o muy altos se han identificado.

 

Resultados.

A. Identificación de los procesos de construcción, operación, mantenimiento, cierre y abandono del Sistema de Alcantarillado Sanitario y Planta de Tratamiento de Aguas Residuales.

En base= a la metodología previamente revisada, se clasificó los procesos o actividades en construcción, operación y mantenimiento y finalmente la etapa de cierre y abandono, que se detallan en las Tablas 9, 10 y 11.

Tabla 9. Actividades de la etapa de construcción

 

Alcantarillado

Planta de Tratamiento de Aguas Residuales

Trans= porte de tuberías y accesorios

Desbr= oce de vegetación

Almac= enamiento de materiales

Limpi= eza del terreno

Excav= ación de zanjas

Desal= ojo de material sin valor de aprovechamiento

Elimi= nación de fluidos procedentes de las excavaciones

Nivel= ación de los terrenos

Desal= ojo de material sin valor de aprovechamiento

Muros= y cimientos

Resan= teo

Const= rucción de canales y reactores

Insta= lación de tuberías y accesorios

Insta= lación de tuberías y accesorios

Relle= no y compactación de zanjas

=  

Limpi= eza y desalojo de material

=  

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

Fuente: Gr= upo de investigación

 

Tabla 10. Actividades de la etapa de operación

 

Alcantarillado

Planta de Tratamiento de Aguas Residuales

Limpieza y mantenimiento de tuberías y accesorios

Entrada del afluente a la planta

Limpieza y mantenimiento de pozos

Retención de sólidos gruesos en la cámara de rejas

Limpieza y mantenimiento de cajas de revisión

Degradación de materia orgánica dentro del reactor

Mantenimiento de conexiones domiciliarias

Separación y retención de sólidos flotantes

 

Infiltración del afluente en las zanjas de infiltración=

 

Remoción de lodos

 

Descarga del efluente

Mantenimiento de conexiones domiciliarias

Limpieza y mantenimiento de canales y accesorios=

Limpieza y desalojo de material

Limpieza y mantenimiento de la cámara de rejas

 

Limpieza y mantenimiento del reactor

 

Fuente: Gr= upo de investigación

 

Tabla 11. Actividades de la etapa de cierre y abandono

 

Planta de Tratamiento de Aguas Residuales

Desma= ntelamiento de equipamiento

Demol= ición de infraestructura

Retir= o de escombros y desechos

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

Fuente: Gr= upo de investigación

La etapa de cierre y abandono considerada hace referencia a las instalaciones de la planta de tratamiento de aguas residua= les, por lo que se consideró de manera general 3 actividades principales.

B. Identificación y Evaluación de Impactos Ambientales

La identificación de los impactos se realizó de manera general para todas las actividades, es decir de manera conjunta para un Sistema de Alcantarillado Sanitario y para la Planta de Tratamiento de Aguas Residuales, de manera qu= e se pueda evaluar a un proyecto de manera integral.

Se iden= tificaron un total de 152 impactos entre positivos y negativos, dónde se destacan mayoritariamente los impactos bajos (57) seguidos de los medios (50), lo que refleja que un Sistema de alcantarillado Sanitario y Planta de Tratamiento = de Aguas residuales generan impactos moderados. De los impactos identificados,= 89 son de carácter positivo, mientras que los negativos se encuentran en un to= tal de 63, concluyendo de esta manera, que este tipo de proyectos representan un mayor beneficio para la población, en comparación con otro tipo de activida= des, tal como se puede apreciar en la tabla 12 y 13.

De los impactos positivos generados, aproximadamente el 90% se asocian a los beneficios propios que obtiene la sociedad al contar con un Sistema de alcantarillado sanitario y planta de tratamiento de aguas residuales que mejoran la calidad de vida, salud, bienestar y seguridad al estar dotados de servicios básicos salubres que aportan al desarrollo local y regional.=

Tabla 12. Matriz de Evaluación de Impactos etapa de construcción

 

 

CONSTRUCCIÓN

 

ALCANTARILLADO

PLANTA

PLANTA Y ALC

 

1

2

3

4

5

6

7

8

1

2

3

4

5

6

1

2

FACTORES AMBIENTALES<= span lang=3DES style=3D'font-size:10.0pt;font-family:"Times New Roman",serif; mso-fareast-font-family:"Times New Roman"'>

FÍSICO

Aire

Calidad del Aire

2,7

2,4

2,1

2,1

2,2

1,2

1,2

Nivel Sonoro

2,7

3,0

2,7

2,2

1,7

1,7

1,7

1,7

Suelo

Calidad de Suelo

5,3

4,2

4,2

4,2

4,2

Uso de Suelo

1,2

1,2

1,2

2,6

1,6

1,2

4,8

3,1

1,2

4,2

4,2

4,2

4,2

Agua

Calidad del Agua

Aguas Superficiales

1,2

Aguas Subterráneas

1,6

1,2

BIÓTICO

Flora

Cubierta vegetal

5,3

Cultivos

5,3

Fauna

Ictiofauna

Mastofauna

3,1

Microfauna

1,6

1,6

1,6

5,3

4,2

4,2

4,2

Avifauna

4,8

S. ECONÓMICO

M. Perceptual

Vistas y Paisaje

2,1

1,2

2,1

2,1

1,2

4,8

2,2

1,6

2,7

Uso de recursos

Abastecimiento de agua

2,9

1,2

Energía eléctrica

2,0

2,2

1,2

1,2

Humano

Bienestar

1,2

Salud

2,9

1,2

Seguridad

3,0

1,2

1,2

1,2

1,2

1,2

1,2

1,2

1,6

2,4

2,4

1,2

1,2

Empleo

+

+

+

+

+

+

+

+

+

+

+

+

+

+

+

+

Fuente: Gr= upo de investigación

 

Tabla 12. Matriz de Evaluación de Impactos etapa de operación, cierre y abandono=

 

ACTIVIDADES

 

OPERACIÓN Y MANTENIMIENTO

CIERRE Y ABANDONO

 

ALCANTARILLADO

PLANTA

PLANTA

 

1

2

3

4

1

2

3

4

5

6

7

8

9

10

1

2

3

FACTORES AMBIENTALES<= /o:p>

FÍSICO

Aire

Calidad del Aire

1,2

1,2

1,2

1,8

1,8

1,2

1,2

1,2

 

Nivel Sonoro

1,2

1,2

1,2

1,2

1,2

1,2

1,7

3,0

1,7

Suelo

Calidad de Suelo

3,3

1,8

2,7

1,9

Uso de Suelo

1,2

1,2

1,2

3,3

2,7

1,4

1,4

1,4

2,7

1,7

Agua

Calidad del Agua

1,8

1,8

1,8

1,8

1,8

1,8

1,8

1,6

2,7

1,2

 

Aguas Superficiales

1,8

1,8

1,8

2,7

 

Aguas Subterráneas

2,7

2,7

 

BIÓTICO

Flora

Cubierta vegetal

 

Cultivos

 

Fauna

Ictiofauna

3,7

 

Mastofauna

 

Microfauna

1,8

 

Avifauna

 

SOCIO ECONÓMICO

M. Perceptual

Vistas y Paisaje

1,6

1,2

Uso de recursos

Abastecimiento de agua

2,2

2,2

2,2

2,2

 

Energía eléctrica

1,8

 

Humano

Bienestar

2,2

2,2

2,2

2,2

 

Salud

2,2

2,2

2,2

2,2

 

Seguridad

1,8

1,8

1,8

1,8

1,4

1,4

1,4

2,4

3,0

2,4

Empleo

+

+

+

+

+

+

+

+

+

+

+

      

       Fuen= te: Grupo de investigación

 

El empleo figura como el componente al cual, todas= las actividades producen un impacto positivo, dado que durante la construcción genera puestos de trabajo, que, a pesar de ser temporal, constituye una fue= nte de ingreso para los pobladores de la región dónde se construya ya sea el alcantarillado o la planta. La operación y mantenimiento genera trabajo constante tanto para personal técnico como operario, mientras que la etapa = de cierre y abandono tiene un comportamiento igual al de la construcción, es decir, la generación de puestos de trabajo temporales o mientras dure la actividad.

Los imp= actos negativos generados son aquellos asociados a las afectaciones a la calidad = del aire, nivel sonoro, calidad de suelo, uso de suelo o a la vegetación y faun= a en general.

Entre l= as actividades que mayor impacto negativo generan se encuentran el desbroce y remoción de vegetación, nivelación de terreno, construcción de muros y cimi= entos, de canales, reactores o instalación de tuberías, que afectan principalmente= al suelo, perdiendo éste su calidad, productividad, estructura y forma; igualm= ente al realizar diversos trabajos que modifican el suelo, existe la generación = de material particulado, el mismo que afecta a la calidad del aire que respira tanto la población beneficiaria como el personal que labora en el proyecto,= no obstante es importante recalcar, que este tipo de actividad es temporal, da= do que se presenta únicamente durante las actividades de construcción o desmantelamiento.

Otro de= los impactos negativos a ser considerados en cualquier programa de mitigación o prevención, es la descarga del efluente, el cual debe cumplir con los límit= es permisibles de descarga a los diferentes cuerpos de agua, de presentarse el caso contrario, representaría un grave peligro para la calidad del agua y d= e la vida acuática que en éstos se desarrollen, y de manera indirecta a las comunidades que hagan uso de las fuentes hídricas involucradas. =

Según M= oscoso (2014) en su tesis “Impacto ambiental del Sistema de alcantarillado de la b= ase naval de San Eduardo y propuesta de intervención para su reducción al aplic= ar la metodología propuesta por Leopold obtuvo como resultado que la construcc= ión de un Sistema de alcantarillado genera impactos negativos moderados, de la misma manera Osejos, Merino y Merino (2018) en su investigación realizada e= n la ciudadela 3 de Mayo que también obtuvo como resultado que el Sistema de alcantarillado generó impactos cuya importancia y magnitud fueron de caráct= er moderado

De mane= ra similar Ortiz (2014) en su investigación en el cantón Colta “Simulación del impacto ambiental generado por la construcción y operación del Sistema de alcantarillado mixto y tratamiento de aguas residuales en la ciudadela de V= illa la Unión y sectores aledańos a la Laguna de Colta dio como resultado que el proyecto generaba impactos negativos cuando no se realizaba una adecuada y correcta planificación y administración; investigaciones que concuerdan con= el presente  estudio al arrojar result= ados similares, dado que en todos los casos citados los impactos generados son moderados y por un periodo temporal durante las actividades de construcción= .

 

Conclusiones.

ˇ   &nb= sp;     Los Sistemas de Alcantarillado Sanitario en conjunto con las Plantas= de Tratamiento de Aguas Residuales proporcionan una mejor calidad de vida para= la población en términos de salud, salubridad y empleo.

 <= /o:p>

ˇ&nb= sp;        Los posibles impactos generados por las actividade= s de construcción, operación, mantenimiento y abandono de un Sistema de Alcantarillado Sanitario y Planta de Tratamiento de Aguas Residuales son ta= nto positivos como negativos, siendo un 59% positivos y 41% impactos negativos.=

&n= bsp;

ˇ&nb= sp;        Tanto en estudios e investigaciones previas, como = en la descrita en el presente artículo los Sistemas de Alcantarillado Sanitari= o y Planta de Tratamiento de Aguas Residuales representan un riesgo negativo moderado y temporal, mientras se lleve a cabo las actividades de construcci= ón.

&n= bsp;

ˇ&nb= sp;        Se concluye, por lo tanto, que los Sistemas de Alcantarillado Sanitario y Planta de Tratamiento de Aguas Residuales no representan un riesgo potencial para el medio ambiente, pudiendo controlar = y prever sus actividades mediante planes de manejo adecuado, por lo contrario, representan bienestar para la población al ser dotados de servicios básicos= de sanidad que eviten posibles enfermedades y contaminación a cuerpos hídricos= .

 

Referencias Bibliográficas.<= /p>

Aldás, J. C. (2011). Diseńo de alcantarillado sanitario y pluvial y tratamiento de aguas servidas de 4 lotizaciones unidas (varios propietarios), del cantón El Carmen. Pontificia Universidad Católica del Ecuador.

Carmona, = R. P. (2013). Diseńo y construcción de alcantarillados sanitario, pluvial y drenaje en carreteras. Ecoe Ediciones.

Conesa Fernández-Vitora, V., Conesa Ripoll, L. A., Conesa Ripoll, V., Bolea, E., Teresa, M., & Ros Garo, V. (1997). Guía metodológica para la evaluac= ión del impacto ambiental. Espańa: Mundi-Prensa.

Metcalf, & Eddy. (1995). Ingeniería de aguas residuales, redes de alcantarill= ado y bombeo (Segunda ed.). Espańa: McGraw Hill.

Ministerio del Ambiente. (2002). Texto Unificado de Legislación Ambiental Secundaria d= el Ecuador (TULSMA). Ecuador.

Ministerio del Ambiente. (2015). Guía metodológica saneamiento. Ecuador.

Moscoso, = W. E. (2014). Impacto ambiental del sistema de alcantarillado de la base naval= de San Eduardo y propuesta de intervención para su reducción. Ecuador: Univers= idad de Guayaquil.

Orea, D. = G., & Villarino, M. T. (2013). Evaluación de impacto ambiental. Mundi-Prensa Libros.

Ortiz, D.= M. (2014). Simulación del impacto ambiental generado por la construcción y operación del proyecto. Sistema de alcantarillado mixto y tratamiento de ag= uas residuales en la ciudad de Villa la Unión y sectores aledańos a la laguna de Colta. Ecuador: Municipio del Cantón Colta.

Osejos, M. A., Merino , M. V., & Merino , M. C. (2018). Impacto ambiental del sist= ema de alcantarillado en la ciudadela 3 de mato de la ciudad de Jipijapa. Re= vista de Investigación FIGMMG-UNMSM, 21(41), 61-74.

Ramalho, = R. S. (1990). Tratamiento de aguas residuales. Reverté.

SIAPA. (2014). Criterios y lineamientos técnicos para factibilidades en la Z.M.= G. México.

 

 

PARA CITAR EL ARTÍCULO INDEXADO.=

 

 

Guerra Herrera, G., & Logrońo Naranjo, S. (2019). Evaluación del impacto ambie= ntal de los sistemas de alcantarillado sanitario y planta de tratamiento de aguas residuales en Ecuador. Ciencia Digital, 3(3.2.1), 73-87. https://doi.o= rg/10.33262/cienciadigital.v3i3.2.1.783

 

 


 

 

 

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

 

El artículo queda 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 Ciencia Dig= ital.

 

 

&nbs= p;

 



[1] Escuela Super= ior Politécnica de Chimborazo, Extensión Norte Amazónica, Orellana, Ecuador. gabriela.guerra@espoch.edu.ec

[2] Escuela Superior Politécnica de Chimborazo, Exten= sión Norte Amazónica, Orellana, Ecuador. israel.logronio@espoch.edu.ec

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