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Indicadores sostenibles urbanos= para la ciudad de Cuenca: la gestión de aguas residuales

Urban sustainable indicators for the city=
 of Cuenca: wastewater management

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= ¹	Christian Paúl Peláez Ochoa	https://orcid.org/0000-0003-4977-4106
	Maestría en Construcciones con mención en Administración de la Construcción Sustentable, Universidad Católica de Cuenca, Cuenca, Ecuador.<= /span> christian.pelaez.45@est.ucacue.edu.ec
= ²	Juan Felipe Quesada Molina	https://orcid.org/0000-0002-6931-0192
	Maestría en Construcciones con mención en Administración de la Construcción Sustentable, Universidad Católica de Cuenca, Cuenca, Ecuador.<= /span> felipe.quesada@ucacue.edu.ec

	Artículo de Investigación Científica y Tecnológica Enviado: 10/12/2022 Revisado: 25/01/2023 Aceptado: 27/02/2023 Publicado:28/03/2023 DOI: = https://doi.org/10.33262/ap.v5i1.2.335<= /span>
=
Cítese:		Peláez Ochoa, C. P., & Quesada Molina, J. F. (2023). Indicadores sostenibles urbanos para la ciudad de Cuenca: la gestión de aguas residuales. AlfaPublicaciones, 5(1.2), 59–86. https://doi.org/10.33262/= ap.v5i1.2.335
		ALFA PUBLICACIONES, es una revista mul= tidisciplinar, trimestral, que se publicará en soporte electrónico tiene como = misión contribuir a la formación de profesionales competentes con visión humanística y crítica que sean capaces de exponer sus resultados investigativos y científicos en la misma medida que se promueva mediante = su intervención cambios positivos en la sociedad. https://alfapublicaci= ones.com <= span style=3D'font-size:8.0pt;line-height:115%;mso-fareast-font-family:Calibri= '>La revista es editada por la Editorial Ciencia Digital (Editorial de prestig= io registrada en la Cámara Ecuatoriana de Libro con No de Afiliación 663) www.celibro.org.ec
		Esta revista está protegida bajo una licencia Creative Commons Attribution Non Commercial No Derivatives 4.0 International. Copia de la licencia: http://creativecommons.org/licenses/by-nc-nd/4.0/
Palabras claves: aguas residuales, indicadores, cuidado, sostenibilidad		Resumen<= /b> Introducción: Actualmente la ciudad de Cuenca atraviesa por un continuo crecimiento demográfico que ha incrementado la demanda de infraestructura de servicios básicos, consider= ando este antecedente es importante conocer qué indicadores intervienen en la gestión de aguas residuales, ello considerando la importancia del cuidado= de los ríos. El objetivo principal de este trabajo fue: crear indicadores sostenibles para la gestión de aguas residuales en la ciudad = de Cuenca. El estudio fue de tipo exploratoria-descriptiva de nivel exploratorio, con enfoque mixto; en lo cualitativo se realizó una búsqueda bibliográfica, para ello se recurrió a las bibliotecas y documentos tanto físicos como digitales de literatura científica existente, con énfasis en: Guía Metodológica-Iniciativa Ciudad= es Emergentes y Sostenibles (BID), ISO 37120 Desarrollo sostenible de las comunidades, Objetivo 6 = de Desarrollo Sostenible, LEED v4.1 Ciudades y comunidades, Comunidades BREE= AM Manual Técnico, Indicadores y Metas Oficiales del ODM7; en lo cuantitativ= o se aplicó un modelo matemático y estadístico para la construcción de indicadores, mismos que fueron sometidos a un juicio de expertos, para su validez se consideró valores mayores a 0.70 de aceptación de acuerdo a lo= s niveles de referencia internacionales. Los resultados del estudio dieron a conocer que los indicadores sostenibles fueron: porcentaje de hogares con conexión domiciliaria al sistema de alcantarillado que obtuvo una calificación de 0.90, porcentaje de aguas residuales tratadas de conformi= dad con las normas nacionales con una calificación de 0.80.=
Keywords:		Abstract Currently, the ci= ty of Cuenca is going through a continuous demographic growth that has incre= ased the demand for basic services infrastructure, considering this background= it is important to know what indicators engage in wastewater management, considering the importance of caring for rivers. The main objective of th= is work was: to create sustainable indicators for wastewater management in t= he city of Cuenca. The study was of an exploratory-descriptive type of exploratory level, with a mixed approach; In the qualitative field, a bibliographic search was carried out, for which both physical and digital libraries and documents of existing scientific literature were used, with emphasis on: Methodological Guide-Emerging and Sustainable Cities Initiat= ive (IDB), ISO 37120 Sustainable development of communities , Sustainable Development Goal 6, LEED v4.1 Cities and communities, BREEAM Communities Technical Manual, Indicators and Official Goals of MDG7; Quantitatively, a mathematical and statistical model was applied for the construction of indicators, which were subjected to expert judgment. For their validity, values greater than 0.70 of acceptance were considered according to international reference levels. The results of the study rev= ealed that the sustainable indicators were percentage of households with home connection to the sewage system that obtained a score of 0.90, percentage= of wastewater treated in accordance with national standards with a score of 0.80. =

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Introducción

Los ecosistemas refieren a un conjunto de sistemas biológicos dentro de los cuales interactúan seres vivos entre sí, alcanzando condiciones óptimas, especialmente su capacidad para regular la cantidad y calidad de agua y aire que hace posible la continuidad de la vid= a tanto humana, vegetal y animal; este trabajo centrará su análisis en los recursos hídricos sobre todo en su regulación y conservación, esto es indispensable = para mantener la vida de todos los seres vivos (Martínez, 2019)<= !--[if supportFields]>.

Los ríos según lo indica Rodríguez (2017), = se enfrentan a una compleja realidad, puesto que en los centros urbanos y periurbanos son mayormente contaminados, a esto se lo denomina síndrome de = ríos urbanos, el cual describe la regularidad en la degradación ecológica y físi= ca dando como resultado una alta concentración de nutrientes y sustancias tóxi= cas, alterando la morfología fluvial. Una de las principales afectaciones a los = ríos es, el inadecuado manejo de aguas residuales, éstas son el resultado de las actividades antropogénicas generadas en su mayoría dentro de los hogares, de igual manera la actividad industrial y agrícola ocasiona que el agua sea co= ntaminada con sustancias químicas, los constituyentes que son encontrados en éstas so= nes generalmente clasificados como físicos, químicos y biológicos (Cedeńo, 2017).

Las aguas residuales procedentes de la agricultura= , la industria y las zonas urbanas en los países en desarrollo, son una de las principales causas de contaminación de los ríos. Sobre estadísticas del tratamiento de aguas residuales, el 70% de los países desarrollados, maneja= n un adecuado tratamiento de estas, mientras que los países en vías de desarroll= o lo hacen en un 38% y aquellos con un alto nivel de pobreza lo hacen en un 8%, = de acuerdo con un informe de la ONU-Agua y la UNESCO. Mientras que en América Latina y el Caribe entre el 70% y 80% son tratadas adecuadamente (Organizac= ión de las Naciones Unidas [ONU], 2017).

En el Ecuador, la Constitución de la Repúbl= ica en su artículo 14, reconoce el derecho de la población a vivir dentro de un ambiente sano de acuerdo con los principios del Sumak Kawsay, ello ha marca= do un presente en el cuidado y preservación de los recursos. Por lo tanto, el sector público ha tomado acciones, enfocadas a la conservación de las fuent= es de agua, gestionando mecanismos para tratar las aguas residuales sobre todo= en las ciudades y que las mismas no desemboquen en los ríos evitando su contaminación (Soto & Ramírez, 2019).

En el Ecuador, el tratamiento de&= nbsp;residuos líquidos domésticos e industriales es casi inexistente (solo el 7%), en tanto que el ac= tual tratamiento se realiza en el sur del país, de= bido a que no se utilizan las normas ambientales establecidas por= el Ministerio del Medio Ambiente ya que el agua que ingresa a las alcantarillas desemboca directamente en los ríos. Este probl= ema se exacerba a medida que las ciudades crecen y&nbs= p;los desechos sólidos a menudo se acumulan en vertederos, arroyos y cursos de agua, causando una grave degradación ambiental y de = ;la salud humana (Guerra & Logrońo, 2019).

La ciudad de Cuenca, de acuerdo con la información de la Empresa Pública Municipal de Telecomunicaciones, Agua Potable, Alcantarillado y Saneamiento–ETAPA EP cue= nta con una Planta de Tratamiento de Aguas Residuales, la misma que trata el 95= % de estas aguas, así también hay otras plantas pequeńas dispuestas en diferentes áreas. La Planta de tratamiento de aguas residuales cuenta con una estructu= ra cuya finalidad es regular la presión y la caída de agua que ingresa a la planta, así como remover sólidos principalmente los lodos residuales, es as= í como diariamente se remueven 4,30 m3 para un caudal medio de 1300 l/s (ETAPA, 20= 21).

Es importante mencionar qu= e, pese a que la ciudad de Cuenca posee una planta de tratamiento para aguas residuales que gracias a los sistemas de alcantarillado ha permitido minimi= zar el impacto ambiental en los ríos, sin embargo se requiere de la implementac= ión de métodos de minimización de volúmenes de aguas residuales, esto para dism= inuir el caudal que durante el invierno llega a la planta de tratamiento, siendo necesaria, la ejecución de un sistema de alcantarillado pluvial; de esta manera, los costos del tratamie= nto serán menores. Es necesario enfatizar que el agua potable y el saneamiento = es un derecho reconocido en la Constitución de la República del Ecuador, pues dotar de infraestructura a la población mejora significativamente su calida= d de vida (Siguencia et al., 2022).

En materia ambiental es necesario citar las leyes propuestas en el Código Orgánico de Organización Territorial (2019), = en su Art. 136 establece que, corresponde a los Gobiernos Autónomos Descentral= izados provinciales, gobernar, dirigir, ordenar, disponer, u organizar la gestión ambiental, la defensoría del ambiente y la naturaleza; en el ámbito de su territorio; estas acciones se realizarán en el marco del sistema nacional descentralizado de gestión ambiental y en concordancia con las políticas emitidas por la autoridad ambiental nacional.

De la misma forma la Ley Orgánica de Recurs= os Hídricos, Usos y Aprovechamiento del Agua (2018), establece en su Art. 63.- Zonas de Protección Hídrica: Definición y Funcionalidad en su Art. 13 reite= ra la importancia del cuidado y la consideración de las aguas de los causes y = los ecosistemas que lo rodean, de igual forma se enfatiza la protección de aguas superficiales pues se ha considerado que forman parte de una zona de protec= ción hídrica, por tanto, también se preservara el suelo evitando realizar actividades que lo alteren tanto de forma directa o indirecta, de esta mane= ra se evitara el deterioro de los ecosistemas contribuyendo a su preservación.=

Considerando el contexto ambiental y jurídi= co en torno al manejo de aguas residuales en la ciudad de Cuenca, en la presen= te investigación se ha propuesto: construir indicadores sostenibles en la gest= ión de aguas residuales, los cuales serán un aporte para la sociedad entera mej= orando la toma de decisiones y la planificación urbana, con el afán de coadyuvar e= n el desarrollo sostenible.

Marco Teórico

La gestión de los ríos según Hernández (201= 8), se lleva a cabo de distintas maneras; por ejemplo, en los países desarrolla= dos se sustenta en la restauración ecológica, por otro lado, los países en desarrollo aún deben centrarse en el uso sostenible de la mayor p= arte de los cursos fluviales. Para Méndez & Valbuena (2021), es importante centrar la atención en deterioro ambiental en los ríos, puesto que, en estas zonas se ha evidenciado un mayor menoscabo ambiental, ello principalmente p= or el uso del suelo y el crecimiento demográfico, puesto que el espacio fluvial ha sido afectado por las actividades antropogénicas, ello ha traído como consecuencia una alteración medioambiental agravado = por el cambio climático, las principales afectaciones son: temperatura del aire, la alteración de las precipitaciones y los patrones de escorrentía, entre otro= s.

Los autores Elizalde & Escobar (2017), = dan a conocer que los ríos urbanos se enfrentan a una constante fragmentación y pérdida de hábitat, es importante tomar en cuenta la ubicación y extensión = de los parques nacionales en la cuenca, puesto que las normativas ofrecen la protección únicamente a las cuencas altas y las especies que ahí habitan, l= as cuales pueden mostrar una mayor susceptibilidad frente a los cambios en la precipitación, caudales y temperatura que obedecen al cambio climático.

Para Herrero (2017), el tratamiento de agua residual ti= ene como finalidad garantizar el cumplimiento mínimo de características biológi= cas, físicas y químicas, tales como: dureza, DBO, DQO, color, pH, alcalinidad, acidez, solidos suspendidos, entre otros, de manera que se pueda garantizar= la calidad de los vertimientos sobre el cuerpo de agua receptor.

Es importante conocer la caracterización del agua residual, pues a partir de la misma se determinará la concentración y tipo = de contaminantes presentes en ella, además están los indicadores como pH y conductividad que forman parte de la materia orgánica, los nutrientes (nitrógeno y fósforo), sólidos en suspensión, que permiten conocer el nivel= de toxicidad, de la misma manera están aquellos relacionados con la procedenci= a de las aguas (metales, tensioactivos, sulfatos, cianuros, etc.) (Tuset, 2014).

= Durante el desarrollo de tratar las aguas residuales se forman biosólidos según Aco= sta et al. (2019), éstos son nutrientes que se forman a partir del tratamiento = de aguas residuales, durante el proceso de separación de los desperdicios de t= ipo industrial, doméstico, agrícola, las aguas son separadas en sólidos y líqui= dos efluentes. El proceso de tratamiento permite desinfectar y eliminar el olor= y las bacterias nocivas. A partir de ello se obtiene formas orgánicas parecid= as al humus que podrá servir como abono orgánico.

= El tratamiento de aguas residuales sin duda representa una estrategia para el cuidado y preservación de las cuencas de los ríos, además de manera directa= , la preservación del agua aportará al cuidado de la vida humana, en este contex= to, se han planteado indicadores para evaluar la sostenibilidad, los cuales refier= en a un conjunto de herramientas que permiten diagnosticar la situación de las ciudades y su entorno inmediato, a partir de la cual se obtendrá una línea = base para el establecimiento de estrategias y acciones en el marco de la agenda = de políticas públicas (Rodríguez et al., 2021).

= Del mismo modo Rodríguez et al. (2021), considera que los indicadores de desarr= ollo sostenible deben cumplir los siguientes criterios: contar con una estructura causal, estructura por temas o sectores, y, una estructura espacial o ecosistémica.

Objetivo

El objetivo de la presente investigación es la construcción de indicadores sostenibles para la gestión de aguas residuales= en la ciudad de Cuenca.

Metodología

En el presente estudio, se realiza una investiga= ción exploratoria-descriptiva; en el nivel exploratorio se ejecuta una indagació= n y análisis exhaustivo en bibliotecas y documentos tanto físicos como digitale= s de literatura científica existente; en el nivel descriptivo se mide los indicadores de sostenibilidad para aguas residuales, con la respectiva homologación se obtienen indicadores sostenibles que se ajustan a la realid= ad de Cuenca, para posteriormente ser sometidos a una validación mediante un juicio de expertos en el área, con lo cual se alcanza a plantear su aplicac= ión verificando si la ciudad de Cuenca es sostenible o no.

Tipos de investigación

La presente investigación tiene el enfoque siguiente: como se muestra en la tabla 1.

Tabla= 1

Tipo y Nivel de Investigación

Según su finalidad

Básica

Se mejo= ra la comprensión y conocimiento del significado de los indicadores de sostenibilidad para la ciudad de Cuenca, en cuanto a las aguas residuales= .

Según su alcance temporal

Prospectiva

Con los= datos recolectados cercanos al presente que serán evaluados y servirán para la = toma de decisiones en el futuro en la ciudad de Cuenca.

Según su profundidad

Exploratoria

Descriptiva

Llegar a poder determinar uno o más indicadores sostenibles de aguas residuales pa= ra la ciudad de Cuenca, con base en la búsqueda y análisis de bibliotecas y documentos tanto físicos como digitales de literatura científica existent= e.

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Evaluac= ión de uno de los indicadores obtenidos.

Según las fuentes

Mixtas

Se util= izarán fuentes primarias y secundarias.

Según el carácter

Cualitativa

Cuantitativa

De la revisión y análisis de fuentes bibliográficas, se obtiene resultados cualitativos.

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Se eval= uarán estadísticamente los resultados obtenidos.

Según su naturaleza

Documentales

El anál= isis se hará de fuentes secundarias para seleccionar indicadores y luego ser validados por fuentes primarias.

Proceso metodológico=

Partiendo del tipo y nivel de investigación, nue= stro estudio contempla las siguientes etapas:

Etapa 1:<= /p>
Revis= ión Bibliográfica: se realiza una investigación exhaustiva en bibliotecas y documentos tanto físicos como digitales de literatura científica existente, mediante un análisis de la bibliografía de= las guías metodológicas y de las herramientas para evaluación nacionales y/o extranjeras, que en nuestro caso son fuentes secundarias como se muestra en= la figura 1, y se crea una base de datos de indicadores sostenibles para aguas residuales.

Figur= a 1

Revis= ión de marco bibliográfico de indicadores

=

=

=

Etapa 2:<= /p>
Homologación de los indicadores= : se analiza uno a uno los indicadores basados en similitudes o sus equivalencias, verificando coherencia entre ellos, al final se obtiene un m= arco de indicadores para aguas residuales, los cuales pueden ser aplicables para= la ciudad de Cuenca.

Etapa 3:<= /p>
Validación de contenido: para validar se utiliza un juicio de expertos conformado por un grupo de personas especialistas en el tema, de esta manera se obtuvo la validez y confiabilid= ad de la información. Los jueces fueron seleccionados por su nivel de experien= cia y conocimiento en el área, así como en indicadores de sostenibilidad ambien= tal. Para determinar el número de jueces, los tratadistas tienen diferente óptica sobre la cantidad de expertos, tenemos que en el ańo 1993 Gable y Wolf, en = el ańo 1997 Grant y Davis, en el ańo 1986 Lynn, autores citados en McGatland et al., 2003, proponen considerar desde dos hasta 20 jueces expertos (Escob= ar-Pérez & Cuervo-Martínez, 2008)= .

ADDIN CSL_CITAT= ION {"citationItems":[{"id":"ITEM-1","itemDa= ta":{"DOI":"https://doi.org/10.13042/brp.2013.65202&quo= t;,"abstract":"INTRODUCCIÓN. En este trabajo se analiza la evolución de los enfoques de aprendizaje de d= os grupos de estudiantes, excelentes y medios, de once titulaciones y nueve centros de la Universi- dad Politécnica de Valencia, en su primer ańo universitario. Los alumnos fueron seleccionados como excelentes y medios por las notas de acceso a la universidad. MÉTODO. La investigación utilizó un diseńo longitudinal con metodología cuantitativa. Los alumnos contestaron el cues- tionario CPE, de evaluación de enfoques de aprendizaje (Biggs, Kember= y Leung, 2001), en tres momentos a lo largo del curso, al inicio, a la mitad = del curso y al final. RESULTADOS. Los resul- tados confirmaron que el enfoque superficial era mayor en los estudiantes medios que en los excelentes y que= el enfoque profundo era superior en los estudiantes excelentes. Corroboramos, también, la existencia de unos patrones evolutivos que comportaban ligero incremento del enfo- que superficial en los dos grupos de alumnos y también= del enfoque profundo a lo largo del ańo. DISCUSIÓN. El hecho de que se incremen= te el enfoque superficial durante el primer ańo en la universidad es relevante= y requiere medidas contextuales. Parece que el estudiante no satisface sus expectativas en el proceso de adaptación al nuevo contexto y ahí los profes= ores tienen res- ponsabilidades ineludibles en el modo de gestionar la docencia = y la evaluación.","author":[{"dropping-particle":"= ","family":"Cabero Julio","given":"Barroso Julio","non-dropping-= particle":"","parse-names":false,"suffix"= ;:""}],"container-title":"BORDON, Revista de Pedagogía","id":"ITEM-1","issued&q= uot;:{"date-parts":[["2013"]]},"title":"= LA UTILIZACIÓN DEL JUICIO DE EXPERTO PARA LA EVALUACIÓN DE TIC: EL COEFICIENTE= DE COMPETENCIA EXPERTA","type":"article-journal",&quo= t;volume":"65"},"uris":["http://www.mendeley.= com/documents/?uuid=3D44268686-a885-4372-a043-07a23b1beb6c"]}],"m= endeley":{"formattedCitation":"(Cabero Julio, 2013)","plainTextFormattedCitation":"(Cabero Jul= io, 2013)","previouslyFormattedCitation":"(Cabero Julio, 2013)"},"properties":{"noteIndex":0},"schema&= quot;:"https://github.com/citation-style-language/schema/raw/master/cs= l-citation.json"}(Cabero, 2013)(Escob= ar-Pérez & Cuervo-Martínez, 2008)= :

La planilla dispone de t= res partes:

-      =     La primera parte: es la introducción conformada por una frase que conduce hacia el tema a evaluarse, nombres y apellidos del experto, formación académica, experiencia profesion= al, cargo actual, objetivo de la investigación.

-          La segunda parte: con= tiene las cuatro categorías para evaluar a los indicadores, como se muestra en la tabla 2.

Tabla= 2

Crit= erios de evaluación de las categorías en la planilla de juicio de expertos

Categoría

Definición

Calificación e indicador

Descripción

1 SUFICIENCIA

El indicador basta para obtener un criterio claro

1 NO CUMPLE CON EL CRITE= RIO

El indicador no es suficiente para medir la dimensión

2 BAJO NIVEL<= /span>

El indicador mide algún aspecto de la dimensión, pero no corresponde con la dimensión total

3 MODERADO NIVEL

Se d= ebe incrementar algo en el indicador para poder evaluar la dimensión completamente

4 ALTO NIVEL<= /span>

El indicador es suficiente

2 CLARIDAD

El indicador se comprende fácilmente, es decir, su sintáctica y semántica son adecuadas

=

1 NO CUMPLE CON EL CRITE= RIO

El indicador no es claro

2 BAJO NIVEL<= /span>

Es menester hacerle al indicador grandes cambios o modificarle en el uso de = las palabras

3 MODERADO NIVEL

Hay = que hacerle un cambio puntual de algún término del indicador

4 ALTO NIVEL<= /span>

El indicador es claro, tiene semántica y sintaxis adecuada=

Tabla= 2

Crit= erios de evaluación de las categorías en la planilla de juicio de expertos (conti= nuación)

Categoría

Definición

Calificación e indicador

Descripción

3 COHERENCIA

El indicador tiene relación lógica con la dimensión que está midiendo

1 NO CUMPLE CON EL CRITE= RIO

el indicador no tiene relación lógica con la dimensión

2 BAJO NIVEL<= /span>

El indicador tiene una relación tangencial con la dimensión

3 MODERADO NIVEL

El indicador tiene una relación moderada con la dimensión que está midiendo<= o:p>

4 ALTO NIVEL<= /span>

El indicador se encuentra completamente relacionado con la dimensión que está midiendo

4 RELEVANCIA

El indicador es esencial o importante, es decir debe ser incluido=

1 NO CUMPLE CON EL CRITE= RIO

El indicador puede ser eliminado sin que se vea afectada la medición

2 BAJO NIVEL<= /span>

El indicador tiene alguna relevancia, pero otro indicador puede estar incluy= endo lo que mide éste

3 MODERADO NIVEL

El indicador es relativamente importante

4 ALTO NIVEL<= /span>

el indicador es muy relevante y debe ser incluido

-          La tercera parte: en l= a cual los indicadores aplicables para la ciudad de Cuenca son evaluados por los expertos, utilizando los criterios de valoración de la tabla 2.<= /span>

Etapa 4:

Evaluación: la validez del contenido dependerá directamente del criterio de los expertos, es preferible hacer uso del coeficiente V. de Aiken, para nuestro caso las valoraciones asignadas s= on politómicas (Escurra, 1988)ADD= IN CSL_CITATION {"citationItems":[{"id":"ITEM-1","itemDa= ta":{"abstract":"Resumen: El presente artículo presenta un programa informático en el lenguaje Visual Basic para el cálculo del coeficiente V de Aiken, usado para cuantificar la validez de contenido, y su intervalo de confianza en niveles de tasa de err= or tipo I previamente seleccionados. La construcción de los intervalos de confianza se hizo por la derivación del método score y publi-cado en Penfie= ld y Giacobbi (2004). El creciente uso de este método y del enfoque de intervalo= s de confianza se ajusta a las demandas actuales mejo-ramiento de los resultados estadísticos inferenciales en la investigación psicológica. Se discute su u= so en contextos aplicados. Palabras clave: Validez de contenido; V de Aiken; intervalos de confian-za; psicometría; validez. Title: Confidence intervals= for the content validity: A Visual Basic computer program for the Aiken's V. Abstract: The present document reporting a Visual Basic computer program for compute the Aiken's V coefficient, this used for quantification of the cont= ent validity, and their confidence interval in specified levels of previously T= ype I error rate. The construction of confidence intervals is performed using t= he score method, and it was published in Penfield and Giacobbi (2004). The gro= wing use of this method and of the confidence interval approach is fitted to the request of improving the results in infer-ential statistic procedures for t= he psychological research. It is discussed their use in applied context. Particularmente, los intervalos de confianza es forma más informativa y úti= l de expresar el grado de imprecisión o in-certidumbre asociada con los resultad= os cuantitativos de una investigación o algún cálculo en general; eso sería una conse-cuencia apropiada de la situación muy común de utilizar una muestra de limitado tamańo. Actualmente, la construcción de intervalos de confianza pa= ra los puntajes obtenidos es una práctica recomendada y a veces es referida co= mo un elemento esencial para la interpretación del reporte de resul-tados de un sujeto (Charter, 2003). En el presente artículo presentamos un programa inf= or-mático para calcular intervalos de confianza para el índice de validez de contenid= o, V, propuesto por Aiken (1980, 1985). El procedimiento para obtener el inter= valo de confianza es por medio del método score, que recientemente fue derivado = en Penfield y Giacobbi (2004) para este coeficiente. Hay pocos precedentes sob= re el uso del coeficiente V de Aiken en publicaciones científicas hispanas, excepto la s…","author":[{"dropping-particle":"",&q= uot;family":"Soto","given":"César Merino","non-dropping-particle":"","parse-nam= es":false,"suffix":""},{"dropping-particle&qu= ot;:"","family":"Segovia","given":&= quot;José Livia","non-dropping-particle":"","parse-name= s":false,"suffix":""}],"container-title"= :"Anales de Psicología","id":"ITEM-1","issue":"= 1","issued":{"date-parts":[["2009"]]},&q= uot;page":"169-171","title":"Intervalos de confianza asimétricos para el índice la validez de contenido: un programa Visual Basic para la V de Aiken.","type":"article-journal","volume"= ;:"25"},"uris":["http://www.mendeley.com/documents= /?uuid=3D5b9ea2fb-cee9-4da2-95c3-5316743fedda"]}],"mendeley"= :{"formattedCitation":"(Soto & Segovia, 2009)","plainTextFormattedCitation":"(So= to & Segovia, 2009)","previouslyFormattedCitation":"(S= oto & Segovia, 2009)"},"properties":{"noteIndex":0},"schema&= quot;:"https://github.com/citation-style-language/schema/raw/master/cs= l-citation.json"}(Soto & Segovia, 2009). Se utiliza el programa abierto jamovi para efectuar las evaluaciones cuantitativas estadísticas.

Realizada la evaluación, se obtienen los indicad= ores de aguas residuales que se ajustan a la ciudad de Cuenca y se escoge aleatoriamente uno de ellos para evaluarlo.

Población y muestra

Partiendo del hecho que nuestra unidad de estudio son los indicadores sostenibles para aguas residuales, la población son tod= as las publicaciones a nivel mundial que sean más relevantes en el tratamiento= s de indicadores sostenibles, con énfasis en bibliografía que trate sobre guías metodológicas y herramientas de evaluación en lo que se refiera a sostenibilidad, y son: Guías Metodológicas: Guía Metodológica-Iniciativa Ciudades Emergentes y Sostenibles (BID), ISO 37120 Desarrollo sostenible de= las comunidades, Objetivo 6 de Desarrollo Sostenible; Herramientas de evaluació= n: LEED v4.1 Ciudades y comunidades, Comunidades BREEAM Manual Técnico, Indicadores y Metas Oficiales del ODM7.

La muestra seleccionada en este estudio son los indicadores que tratan sobre aguas residuales, para lo cual= se consideró lo que propone las guías metodológicas y las herramientas de evaluación.

Resultado= s

De la revisión bibliográfica realizada en la eta= pa 1 se obtuvieron 20 indicadores para aguas residuales, divididos en: 14 de las guías metodológicas y 6 de las herramientas de evaluación, los cuales se describen a continuación: como se muestra en la figura 2.=

=

=

=

=

=

=

=

=

=

=

=

=

Figur= a 2

Indicadores para aguas residuales

=

=

=

=

=

=

=

=

=

=

=

=

=

=

=

=

=

=

=

=

=

Dentro del universo bibliográfi= co analizado, visualizamos cuales predominan en cuanto a los indicadores de ag= uas residuales: como se muestra en la figura 3.

Figur= a 3

Aportaciones de indicadores de la bibliografía analizada

Presentación de los datos

Del total de veinte indicadores obtenidos, se realiza en la etapa 2 la homologación, dando como resultado c= inco indicadores finales como se muestra en la tabla 3, los cuales se detallan a continuación con su objetivo, unidad, método de evaluación y niveles de exigencias:

=

=

=

=

=

=

=

=

Tabla= 3

Indicadores sostenibles homologados para aguas residuales

<= o:p>

Niveles de Exigencias: Descripción

Calificación, Puntaje

Indicador

Objetivo

Unidad

Método de

Evaluación

Sostenible (verde)

Medianamente

Sostenible (amarillo)

No

sostenible (rojo)

Porc= entaje de hogares con conexión domiciliaria al sistema de alcantarillado

Cono= cer el número de hogares que tienen acceso al sistema de alcantarillado

Porc= entaje

(núm= ero de instalaciones urbanas de alcantarillado / porcentaje de hogares urbanos d= e la ciudad) *100

>75%

75%-60%

<60%

Porc= entaje de aguas residuales tratadas de conformidad con las normas nacionales

Cono= cer el volumen de aguas residuales tratadas de conformidad con las normas nacion= ales pertinentes

Porc= entaje

(vol= umen de agua residual tratada / volumen total de agua residual generada) *100<= o:p>

>60%

40%-60%

<40%

Porc= entaje de viviendas afectadas por las inundaciones más intensas de los últimos 10 ańos

Porc= entaje de viviendas que tuvieron problemas por las inundaciones en los últimos 10 ańos

Porc= entaje

(núm= ero de viviendas afectadas / número total de viviendas existentes) *100

<0,5%

0,5%-3%

>3%

Porc= entaje de la población de la ciudad con servicio de recogida de aguas residuales=

Cono= cer el número de la población servida por una recolección de aguas residuales es= un indicador de la salud, la limpieza y la calidad de vida de la ciudad. Recolección de aguas residuales y el tratamiento es un componente significativo.

Porc= entaje

(núm= ero de personas dentro de la ciudad con servicio urbano de alcantarillado / población urbana total de la ciudad) *100

>75%

75%-60%

<60%

Tabla= 3

Indicadores sostenibles homologados para aguas residuales = (continuación)

Niveles de Exigencias: Descripción

Calificación, Puntaje

Indi= cador

Obje= tivo

Unid= ad

Método de

Eval= uación

Sostenible (verde)

Medianamente

Sostenible (amarillo)

No

Proporción de la población que utiliza servic= ios de saneamiento mejorados

El a= cceso a instalaciones de saneamiento mejoradas se referirá al porcentaje de la<= br> población de la ciudad con al menos acceso adecuado a instalaciones de
eliminación de excretas que puedan prevenir efectivamente el contacto hum= ano,
animal e insecto con las excretas. Las instalaciones mejoradas van desde letrinas
de pozo sencillas, pero protegidas, hasta retretes con descarga de agua y= una
conexión de alcantarillado. Para que sean eficaces, las instalaciones deb= en estar correctamente construidas y mantenidas adecuadamente.

Porc= entaje

el número total de personas que utilizan instalaciones de saneamiento mejoradas
(numerador) dividido por la población total de la ciudad (denominador). E= l
resultado será entonces multiplicado por 100 y expresado en porcentaje.

>75%

75%-60%

<60%

Los indicadores:El indicador: porcentaje de la población de la ciudad con servicio de recogida de aguas residuales; pertenece a ISO 37120 Desarrollo sostenible de las comunidades.

El indicador: proporción de la población que utiliza servicios de saneamiento mejorados; pertenece a Indicadores y Metas Oficiales del ODM7.

Para la etapa 3 de validación de contenido, se seleccionaron los perfiles profesionales que se describen: co= mo se muestra en la tabla 4.

Tabla= 4

Perf= iles de expertos seleccionados

Experto

Formación

académica

Experiencia profesional

Actividad presente

Experto uno=

Cuarto nivel posgrado

Gerencia en empresas = de agua potable y aguas residuales en gobiernos seccionales, Gerencia en entidades gubernamentales, Gerencia de proyectos hidrosanitarios

Consultor independien= te

Experto dos=

Cuarto nivel posgrado

Docencia Universitari= a, Manejo de ordenamiento territorial, Dirección técnica en empresa de gobie= rno seccional

Docencia Universitari= a, Investigación a nivel de pre y post grado

Experto tre= s

Cuarto nivel posgrado

Administración a nive= l de jefatura de Planta de Tratamiento de Aguas Residuales en empresas municipales, Técnico en área de sistemas de alcantarillado, supervisión en planes maestros de aguas residuales, gerencia de proyectos en plantas de tratamiento de aguas residuales, gerencia en empresas de agua y saneamien= to en gobiernos seccionales, consultor internacional en plantas de tratamien= to de aguas residuales

Supervisor en plantas de aguas residua= les

Experto cua= tro

Ingeniero c= ivil, Prevención de riesgos laborales - Prevención de riesgos laborales: construcción y obras públicas

En la construcción de= obras hidrosanitarias, alcantarillados sanitarios, alcantarillados pluviales y colectores de aguas residuales

Empleado contratado p= ara administrador en diferentes obras en Gobierno seccional=

Experto cin= co

Ingeniero c= ivil, consultor

Diseńo, construcción y fiscalización de obras: hidrosanitarias, alcantarillados sanitarios, alcantarillados combinados

Ingeniero en libre ejercicio: diseńo, planificación, fiscalización, construcción<= /span>

Los cinco expertos fueron instruidos de todos los pormenores que se llevan adelante en la presente investigación, y, voluntariamente con motivación, disponibilidad, imparcialidad, decidieron participar.

Al aplicar el método de agregad= os individuales utilizando la planilla respectiva descrita en la tabla 2, obtenemos los resultados acumulados para cada indicador homologado como se muestra en la figura 4, en la cual podemos verificar los niveles de aceptac= ión por parte del panel encuestado.

Figur= a 4

Resul= tados de la calificación por los expertos por cada indicador homologado en base a criterios de suficiencia, claridad, coherencia y relevancia

=

=

=

=

=

Tabla= 5

Resu= ltados y evaluación de juicio de expertos

Indicador

Experto 1

Experto 2

Experto 3

Experto 4

Experto 5



        V. Aiken

Intervalos = de confianza 95%

Suficiencia=

Claridad

Coherencia<= o:p>

Relevancia<= o:p>

Suficiencia=

Claridad

Coherencia<= o:p>

Relevancia<= o:p>

Suficiencia=

Claridad

Coherencia<= o:p>

Relevancia<= o:p>

Suficiencia=

Claridad

Coherencia<= o:p>

Relevancia<= o:p>

Suficiencia=

Claridad

Coherencia<= o:p>

Relevancia<= o:p>

L (límite inferior)

U (límite superior)

Porcentaje de hogares= con conexión domiciliaria al sistema de alcantarillado

4

4

4

4

4

3

3

3

2

4

4

3

4

4

4

4

4

4

4

4

0.90

66.03<= /o:p>

97.66<= /o:p>

Porcentaje de aguas residuales tratadas de conformidad con las normas nacionales

4

4

4

4

3

3

3

3

1

3

2

2

4

4

4

4

4

4

4

4

0.80

54.81<= /o:p>

92.95<= /o:p>

Porcentaje de viviend= as afectadas por las inundaciones más intensas de los últimos 10 ańos

2

3

2

2

3

3

3

3

1

1

1

1

1

1

1

1

3

3

3

3

0.35

16.31<= /o:p>

59.81<= /o:p>

Porcentaje de la pobl= ación de la ciudad con servicio de recogida de aguas residuales

2

3

2

2

2

2

2

2

1

1

1

1

2

1

2

2

4

4

4

4

0.40

19.82<= /o:p>

64.25<= /o:p>

Proporción de la población que utiliza servicios de saneamiento mejorados

4

4

4

4

2

2

2

2

1

1

2

2

3

3

3

3

3

4

3

4

0.60

35.75<= /o:p>

80.18<= /o:p>

En la tabla 5 se aprecia el coeficiente V. de Ai= ken en los 2 indicadores: porcentaje de hogares con conexión domiciliaria al sistema de alcantarillado y porcentaje de aguas residuales tratadas de conformidad con las normas nacionales; que éstos presentan validez de contenido, ya que son superiores a 0.70 y cumplen con los criterios de evaluación.

El coeficiente V. de Aiken en los 3 indicadores: porcentaje de viviendas afectadas por las inundaciones más intensas de los últimos 10 ańos, porcentaje de la població= n de la ciudad con servicio de recogida de aguas residuales y proporción de la población que utiliza servicios de saneamiento mejorados; obtiene valores inferiores a 0.70, por lo que no presentan validez de contenido.

Finalmente se procede a evaluar uno de los indicadores de aguas residuales que cumplen con los criterios de evaluación según la tabla 5 que se ajustan a la ciudad de Cuenca. Para ello escogemos aleatoriamente uno de los indicadores y verificamos su sustentabilidad.

Nombre del indicador escogido:<= /span> porcentaje de hogares con conexión domiciliaria al sistema de alcantarillado. Lo denominamos: A y lo representamos en porcentaje (A%).

Métod= o de evaluación: para este indicador el método de evaluación está definido en la tabla 3, cuya fórmula de cálculo es la siguiente:<= /o:p>

Datos:

·         El dato de la población del ańo 2010 así como los porcentajes de poblac= ión urbana y rural fueron obtenidos del censo del ańo 2010 ( Instituto Nacional de Estadíst= icas y Censos [INEC], 2= 022).

·         La población del ańo 2020 fue obtenida de la proyección cantonal 2010-2020 (INEC, 2022).

·         El dato de población del ańo 2021 fue obtenido con la utilización de la tasa de crecimiento anual 2001-2010 aplicada a la ciudad de Cuenca (INEC, 2022).

·         El dato de personas por hogar fue tomado de Promedio de Personas por Hogar seg= ún Parroquia (INEC, 2022).

·&nb= sp;        Los datos de número de instalaciones urbanas de alcantarillado fueron obtenidos= de la empresa pública municipal de telecomunicaciones, agua potable, alcantarillado y saneamiento (ETAPA EP), de Cuenca.

Realizamos los cálculos respectivos y tenemos, para el ańo 2021:

Los datos y resultados se prese= ntan a continuación: como se muestra en la tabla 6.

=

Tabla= 6

Dato= s y resultados del cálculo del porcentaje urbano de hogares de la ciudad de Cue= nca con conexión domiciliaria al sistema de alcantarillado

Ańo

Población

Población u= rbana 65,6%

Población <= o:p>

rural 34,4%=

Personas

por hogar

Número de instalaciones urbanas de

alcantarill= ado

A= (%)

2010

505,585

331,664

173,921

3.64

2020

636,996

417,869

219,127

3.64

104,680

91.19<= /o:p>

2021

649,290

425,934

223,356

3.64

106,331

90.87<= /o:p>

Para el indicador verificado se= gún los niveles de exigencia, referidos en la tabla 3, el valor (A) obte= nido para el ańo 2020 es de 91.19 %, por lo que se encuentra con una calificación (verde) ya que es mayor a 75%.

Para el indicador verificado se= gún los niveles de exigencia, referidos en la tabla 3, el valor (A) obte= nido para el ańo 2021 es de 90.87 %, por lo que se encuentra con una calificación (verde) ya que es mayor a 75%.

Conclusiones <= o:p>

·         Es importante reflexionar sobre los retos que implica la sostenibilid= ad en el manejo de las aguas residuales, los gobiernos locales tienen la obligación de garantizar el acceso al agua potable y saneamiento, pues los mismos son un derecho humano. Ello requiere de la implementación de modelos basados en una normativa jurídica enfocada en la protección de los ríos.

·         Se requiere tomar las experiencias de los países desarrollados e implementarlos en el Ecuador, la adopción de medidas de carácter jurídico, administrativo y de gestión que permitan recuperar el espacio fluvial. El principal reto sería potenciar el río, recuperando su identidad natural apegados a los principios de la eco-hidrología y la eco-geomorfología.=

·         Luego del análisis realizado a toda la bibliografía que trata de indicadores sostenibles para aguas residuales y de la respectiva validez de contenidos, proveyó como resultado que los indicadores: porcentaje de hogar= es con conexión domiciliaria al sistema de alcantarillado y porcentaje de aguas residuales tratadas de conformidad con las normas nacionales, responden a l= os Objetivos 6 de Desarrollo Sostenible y a la Guía Metodológica – Iniciativa Ciudades Emergentes y Sostenibles del Banco Interamericano de Desarrollo, p= or lo tanto, estos pueden ser aplicados a la ciudad de Cuenca como indicadores= de sostenibilidad para la gestión de aguas residuales por su alta viabilidad y= el impacto para el cuidado del medio ambiente.

·         Luego del análisis y evaluación del indicador: porcentaje de hogares = con conexión domiciliaria al sistema de alcantarillado, este presenta un valor = muy por encima de las exigencias internacionales, lo cual nos permite concluir = que la empresa pública= municipal de telecomunicaciones, agua potable, alcantarillado y saneamiento (ETAPA EP= ) de Cuenca, tiene una adecuada gestión en el manejo del sistema de alcantarilla= do.

·         La ciudad de Cuenca por intermedio de su empresa pública municipal (ETAPA EP), cumple con las normas nacionales para el tratamiento de las aguas residuale= s, ya que luego de la valoración del respectivo indicador este cumple con la validez de su contenido, concluyendo que las aguas residuales de la ciudad = de Cuenca se tratan de una manera adecuada.

·         Con la obtención de los indicadores sostenibles en este estudio se concluye que= ayudan a mejorar la toma de decisiones y la planificación urbana en la ciudad de Cuenca para lograr un desarrollo sostenible que satisfaga las necesidades d= e la ciudad en el presente sin poner en peligro la capacidad de las generaciones futuras para satisfacer sus necesidades.

Discusión =

Los resultados de este estudio dieron a conocer que, de los cinco indicadores homologados y evaluados por = el panel de expertos, 2 cumple los criterios de sostenibilidad de acuerdo con = V. de Aiken éstos son: porcentaje de hogares con conexión domiciliaria al sist= ema de alcantarillado con un valor de 0.90; porcentaje de aguas residuales trat= adas de conformidad con las normas nacionales con un valor de 0.80.

Así como el estudio de Baudo (2= 021), obtuvo 5 indicadores para medir la sostenibil= idad ambiental de los cuales sobresalieron: continuidad del servicio de agua; conexión domiciliaria al sistema de alcantarillado; viviendas afectadas por= las inundaciones; y, como indicador final, la recolección regular de residuos sólidos municipales, sin embargo tam= bién se hallaron indicadores negativos como son: las recurrentes inundaciones de= la ciudad; el inadecuado manejo de los residuos; los desechos residenciales a una distancia superior a 800 metros, esto ha incrementado la implementación de medias y decisiones estatales para solucionar estas situaciones.

Por su parte Márquez et al. (2020), menci= onan que los indicadores en torno a la gestión de aguas residuales en Ecuador no= han respondido a la Agenda 21 Local en= lo que respecta en brindar a la población una buena calidad de vida, ello se p= odrá medir por su bienestar alcanzado, para lograrlo es necesario implementar un Plan de desarrollo local sostenible, que considere un enfoque multidimensio= nal y la estructuración de un sistema de indicadores específicamente en el ámbi= to rural, que ante un inadecuado tratamiento de aguas residenciales se ha evidenciado un alto índice de contaminación de los caudales, por tanto es necesario considerar los principios de una economía sostenible, un entorno, capital natural y cultural perdurab= le que permita mejorar la calidad de vida y bienestar de la comunidad rural.

Según la Guía Metodológica-Iniciativa Ciudades Emergentes y Sostenibles (BID), en sus val= ores de referencia tenemos: >75% Verde- la gestión es adecuada o buena, 75%-6= 0% amarillo- si el tema presenta algunas dificultades en su servicio o gestión, <60% rojo- si el servicio o gestión es deficiente y necesita atención. El indicador en estudio da un valor de 90.87% que es mayor al 75%, por lo que = se cataloga como verde- con la gestión adecuada o buena.

Los autores Hernández & Salvador (2016), reiteran la necesidad de adaptar mejoras a los sistemas de depuración, sin embargo, poc= o se han considerado en torno a las limitaciones de infraestructura para tratar = los procesos de tratamiento cuando incrementan los caudales en épocas de invier= no, puesto que ante una alta variabilidad en los volúmenes de tratamiento puede repercutir en el funcionamiento de la planta, además pondrá en riesgo la eficiencia de las instalaciones de esta.

La empresa pública municipal es= tudiada en esta investigación visualizó un valor de 95.40% para este indicador, que= es diferente al valor de 90.87% calculado. De la investigación realizada, esta diferencia radica en la forma de cálculo de la empresa: número de las instalaciones de alcantarillado sobre el número de claves catastrales (códi= go numérico que sirve para registrar un inmueble en la ciudad); lo cual deriva= en una constante variación en los valores.

Los indicadores: porcentaje de hogares con conexión domiciliaria al sistema de alcantarillado; porcentaje = de aguas residuales tratadas de conformidad con las normas nacionales, al cump= lir con las exigencias establecidas, se pueden aplicar para la ciudad de Cuenca puesto que responden a los principios de sostenibilidad. Así concuerda el estudio de Siguencia et al. (2022), quienes determinaron que la sostenibilidad de los indicadores más relevantes = en la gestión de aguas residuales depende del trabajo conjunto de las empresas públicas, puesto que dentro de las mismas también se incluye el sistema de eficiencia y control de actividades, así también de la gestión de tratamien= tos de aguas pluviales.

Por su parte Tapia (2021), seńa= la que el indicador porcentaje de h= ogares con conexión domiciliaria al sistema de alcantarillado depende directamente= de la infraestructura de la ciudad de Cuenca ante el crecimiento poblacional d= el cantón el sistema de alcantarillado ha incrementado su demanda, más no su vida útil, además sostienen que el éxito= del sistema de alcantarillado también depende de la sostenibilidad económica – financiera específicamente para cubrir costos operativos del proceso.

estudio de Cervera (2007), aguas residu= ales tratadas “en ciudad Juárez en México obtuvo un 87% de las aguas tratadas, sin embargo, se halló que el crecimiento = del caudal supera la capacidad del tratamiento actual, para lo cual se ha considerado mayores construcciones de plantas de tratamiento, en la ciudad donde se realizó el estudio existen buenos indicadores sobre uso sustentable del agua, de manera especial aquellos que están dentro del municipal de agua potable y saneamiento, a pesar de = ello, es necesario contar con indicadores de explotación sustentable que permita asegurar el suministro de agua a largo plazo por ende, se requiere de indicadores de extracción-recarga, además de indicadores sobre calidad del agua.

El autor Tiburcio & Perevochtchikova (2021), concuerdan que el porcentaje de gestión de aguas residuales representa una dimensión de seguridad del agua, la planificación= de este recurso o la evaluación de la resiliencia de los sistemas de agua, ade= más se requiere de una verdadera gobernanza que garantice la seguridad de este recurso en un contexto de cambio climático, la política pública en mate= ria hídrica aún es limitada debido a la incapacidad institucional para recolectar o evaluar datos.

En cuanto al indicador encontrado en este estudio, se obt= uvo que el porcentaje de hogares con conexión domiciliaria al sistema de alcantarillado responde a la sostenibilidad. El estudio de Illescas & Roca (2021), hallaron que los indicadores como: porc= entaje de cobertura de agua y porcentaje de sistema de alcantarillado están vincul= ados estrechamente a los sistemas de ed= ucación, salud y seguridad ciudadana, además para verificar si estos tuvieron un imp= acto positivo en la sostenibilidad se propuso una escala de rendimiento basados = en índices de Bienestar ecosistémico y humano, a partir de 3 categorías: desfavorable (0-30), medianamente favorable (30-60) y favorable (60-90), hallando que los mismos aportan a la sostenibilidad medianamente favorable o intermedia.

Queda abierta la posibilidad de emprender = con unas metodologías diferenciadas; implementando ciertas modificaciones en las evaluaciones de los indicadores sostenibles, para poderlas utilizar en zonas urbanas y rurales que permitan la línea de futuras investigaciones.

Agradecimientos

    de    Cuenca,    vinculados    al    Proyecto    de    Investigación:    INDICADORES    DE SOSTENIBILIDAD URBANA PARA LA CIUDAD DE CUENCA–ECUADOR, por ello agradecemos a todos y cada uno de los instructores pertenecient= es a los grupos de investigación; Ciudad, Ambiente y Tecnología (CAT), y Sistemas embebidos y visión artificial en ciencias, Arquitectónicas, Agropecuarias, Ambientales y Automática (SEVA4CA), por los conocimientos e información brindados para la elaboración del trabajo.=

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<= o:p>

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Tipo y Nivel de Investigación
Según su finalidad	Básica	Se mejo= ra la comprensión y conocimiento del significado de los indicadores de sostenibilidad para la ciudad de Cuenca, en cuanto a las aguas residuales= .
Según su alcance temporal	Prospectiva	Con los= datos recolectados cercanos al presente que serán evaluados y servirán para la = toma de decisiones en el futuro en la ciudad de Cuenca.
Según su profundidad	Exploratoria Descriptiva	Llegar a poder determinar uno o más indicadores sostenibles de aguas residuales pa= ra la ciudad de Cuenca, con base en la búsqueda y análisis de bibliotecas y documentos tanto físicos como digitales de literatura científica existent= e. &n= bsp; Evaluac= ión de uno de los indicadores obtenidos.
Según las fuentes	Mixtas	Se util= izarán fuentes primarias y secundarias.
Según el carácter	Cualitativa Cuantitativa	De la revisión y análisis de fuentes bibliográficas, se obtiene resultados cualitativos. &n= bsp; Se eval= uarán estadísticamente los resultados obtenidos.
Según su naturaleza	Documentales	El anál= isis se hará de fuentes secundarias para seleccionar indicadores y luego ser validados por fuentes primarias.

Categoría	Definición	Calificación e indicador	Descripción
1 SUFICIENCIA	El indicador basta para obtener un criterio claro	1 NO CUMPLE CON EL CRITE= RIO	El indicador no es suficiente para medir la dimensión
2 BAJO NIVEL<= /span>	El indicador mide algún aspecto de la dimensión, pero no corresponde con la dimensión total
3 MODERADO NIVEL	Se d= ebe incrementar algo en el indicador para poder evaluar la dimensión completamente
4 ALTO NIVEL<= /span>	El indicador es suficiente
2 CLARIDAD	El indicador se comprende fácilmente, es decir, su sintáctica y semántica son adecuadas	= 1 NO CUMPLE CON EL CRITE= RIO	El indicador no es claro
2 BAJO NIVEL<= /span>	Es menester hacerle al indicador grandes cambios o modificarle en el uso de = las palabras
3 MODERADO NIVEL	Hay = que hacerle un cambio puntual de algún término del indicador
4 ALTO NIVEL<= /span>	El indicador es claro, tiene semántica y sintaxis adecuada=

<= o:p>				Niveles de Exigencias: Descripción
				Calificación, Puntaje
Indicador	Objetivo	Unidad	Método de Evaluación	Sostenible (verde)	Medianamente Sostenible (amarillo)	No
sostenible (rojo)
Porc= entaje de hogares con conexión domiciliaria al sistema de alcantarillado	Cono= cer el número de hogares que tienen acceso al sistema de alcantarillado	Porc= entaje	(núm= ero de instalaciones urbanas de alcantarillado / porcentaje de hogares urbanos d= e la ciudad) *100	>75%	75%-60%	<60%
Porc= entaje de aguas residuales tratadas de conformidad con las normas nacionales	Cono= cer el volumen de aguas residuales tratadas de conformidad con las normas nacion= ales pertinentes	Porc= entaje	(vol= umen de agua residual tratada / volumen total de agua residual generada) *100<= o:p>	>60%	40%-60%	<40%
Porc= entaje de viviendas afectadas por las inundaciones más intensas de los últimos 10 ańos	Porc= entaje de viviendas que tuvieron problemas por las inundaciones en los últimos 10 ańos	Porc= entaje	(núm= ero de viviendas afectadas / número total de viviendas existentes) *100	<0,5%	0,5%-3%	>3%
Porc= entaje de la población de la ciudad con servicio de recogida de aguas residuales=	Cono= cer el número de la población servida por una recolección de aguas residuales es= un indicador de la salud, la limpieza y la calidad de vida de la ciudad. Recolección de aguas residuales y el tratamiento es un componente significativo.	Porc= entaje	(núm= ero de personas dentro de la ciudad con servicio urbano de alcantarillado / población urbana total de la ciudad) *100	>75%	75%-60%	<60%

Experto	Formación académica	Experiencia profesional	Actividad presente
Experto uno=	Cuarto nivel posgrado	Gerencia en empresas = de agua potable y aguas residuales en gobiernos seccionales, Gerencia en entidades gubernamentales, Gerencia de proyectos hidrosanitarios	Consultor independien= te
Experto dos=	Cuarto nivel posgrado	Docencia Universitari= a, Manejo de ordenamiento territorial, Dirección técnica en empresa de gobie= rno seccional	Docencia Universitari= a, Investigación a nivel de pre y post grado
Experto tre= s	Cuarto nivel posgrado	Administración a nive= l de jefatura de Planta de Tratamiento de Aguas Residuales en empresas municipales, Técnico en área de sistemas de alcantarillado, supervisión en planes maestros de aguas residuales, gerencia de proyectos en plantas de tratamiento de aguas residuales, gerencia en empresas de agua y saneamien= to en gobiernos seccionales, consultor internacional en plantas de tratamien= to de aguas residuales	Supervisor en plantas de aguas residua= les
Experto cua= tro	Ingeniero c= ivil, Prevención de riesgos laborales - Prevención de riesgos laborales: construcción y obras públicas	En la construcción de= obras hidrosanitarias, alcantarillados sanitarios, alcantarillados pluviales y colectores de aguas residuales	Empleado contratado p= ara administrador en diferentes obras en Gobierno seccional=
Experto cin= co	Ingeniero c= ivil, consultor	Diseńo, construcción y fiscalización de obras: hidrosanitarias, alcantarillados sanitarios, alcantarillados combinados	Ingeniero en libre ejercicio: diseńo, planificación, fiscalización, construcción<= /span>

Indicador	Experto 1	Experto 2	Experto 3	Experto 4	Experto 5	V. Aiken	Intervalos = de confianza 95%
Suficiencia=	Claridad	Coherencia<= o:p>	Relevancia<= o:p>	Suficiencia=	Claridad	Coherencia<= o:p>	Relevancia<= o:p>	Suficiencia=	Claridad	Coherencia<= o:p>	Relevancia<= o:p>	Suficiencia=	Claridad	Coherencia<= o:p>	Relevancia<= o:p>	Suficiencia=	Claridad	Coherencia<= o:p>	Relevancia<= o:p>	L (límite inferior)	U (límite superior)
Porcentaje de hogares= con conexión domiciliaria al sistema de alcantarillado	4	4	4	4	4	3	3	3	2	4	4	3	4	4	4	4	4	4	4	4	0.90	66.03<= /o:p>	97.66<= /o:p>
Porcentaje de aguas residuales tratadas de conformidad con las normas nacionales	4	4	4	4	3	3	3	3	1	3	2	2	4	4	4	4	4	4	4	4	0.80	54.81<= /o:p>	92.95<= /o:p>
Porcentaje de viviend= as afectadas por las inundaciones más intensas de los últimos 10 ańos	2	3	2	2	3	3	3	3	1	1	1	1	1	1	1	1	3	3	3	3	0.35	16.31<= /o:p>	59.81<= /o:p>
Porcentaje de la pobl= ación de la ciudad con servicio de recogida de aguas residuales	2	3	2	2	2	2	2	2	1	1	1	1	2	1	2	2	4	4	4	4	0.40	19.82<= /o:p>	64.25<= /o:p>
Proporción de la población que utiliza servicios de saneamiento mejorados	4	4	4	4	2	2	2	2	1	1	2	2	3	3	3	3	3	4	3	4	0.60	35.75<= /o:p>	80.18<= /o:p>

Ańo	Población	Población u= rbana 65,6%	Población <= o:p> rural 34,4%=	Personas por hogar	Número de instalaciones urbanas de alcantarill= ado	A= (%)
2010	505,585	331,664	173,921	3.64
2020	636,996	417,869	219,127	3.64	104,680	91.19<= /o:p>
2021	649,290	425,934	223,356	3.64	106,331	90.87<= /o:p>