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Artículo científico / Research= paper

Evaluación de la calidad del agua de los ríos de la ciud= ad de Cuenca, Ecuador

Water quality assessment of the rivers of Cuenca city in Ecuador

Guillermina Pauta¹, María Velasco¹, Daniela Gutiérrez¹, Gabriela Vázquez¹, Santiago Rivera², Óscar Morales², Andrea Abr= il¹

¹= Laboratorio de Sanitaria, Departamento de Ingeniería Civil, Universidad de Cuenca, Cuenca, Ecuador.=

²= Integrated Water Quality Management = Project, VLIR, Universidad de Cuenca, Cuenca, Ecuador.

Autor para correspondencia: guillermina.pauta@uc= uenca.edu.ec

Fecha de recepción: 10 de abri= l de 2019 - Fecha de aceptación: 12 de diciembre de 2019

RESUMEN

Se evaluó la calidad del agua de los ríos Tarqui, = Yanuncay, Machángara y Tomebamba, afluentes del río Paute. En línea con la necesidad de incorporar nuevos enfoques en la vigilancia de la calidad del = agua, este estudio aplicó el ampliamente conocido Water Quality Index (QWI) pero,= en lugar de utilizar los nueve parámetros originalmente requeridos por el méto= do, utilizamos 18 parámetros fisicoquímicos y microbiológicos. Para cada río, se llevaron a cabo nueve campańas de monitoreo, cubriendo períodos hidrológicos representativos y midiendo descargas de flujo. Los resultados muestran que,= en general, en las áreas de captación de los ríos, el recurso hídrico es adecu= ado para casi todo tipo de uso, pero gradualmente, a medida que avanza aguas ab= ajo, la calidad disminuye debido a las descargas de aguas residuales sanitarias, industriales y a factores naturales como escorrentía o sedimentos por erosi= ón. La condición más crítica de calidad de las aguas evaluadas se presentó dura= nte las condiciones de sequía, principalmente debido a la disminución del oxíge= no disuelto y al aumento de la temperatura, la salinidad, la materia orgánica = y las bacterias coliformes. Por otro lado, durante los períodos lluviosos, los parámetros indicadores de una disminución en la cal= idad del agua fueron el color, la turbidez, y el contenido de nutrientes como fósforo y nitrógeno. En general, los ríos tienen mejor calidad para condici= ones de flujo medio, que prevalecen durante la mayor parte del ańo. Los presentes resultados se analizaron de acuerdo con los objetivos de calidad establecid= os en estudios anteriores, permitiendo una evaluación cualitativa del sistema = de intercepción y tratamiento de aguas residuales de la ciudad de Cuenca, Ecua= dor.

Palabras clave: Índice de cali= dad del agua, contaminación, usos del agua, ICA, Paute

ABSTRACT

The water quality of the Tarqui, Yanuncay, Machángara and = Tomebamba rivers, tributaries of the Paute river was evaluated. Due to the need to incorpor= ate new approaches in the water quality monitoring, this study applied the wide= ly known water quality index (WQI) but, instead of using the 9 parameters originally required by the method, we used 18 physicochemical and microbiological parameters. For each river, nine monitoring campaigns were carried out, covering representative hydrological periods and measuring flow discharges. The results show that, in general, in the areas of river catchm= ent, the water resource is suitable for almost all types of use, but gradually, = as it progresses downstream, the quality decreases due to sanitary or industri= al wastewater and to natural factors such as runoff or erosion sediments. The = most critical condition of the evaluated river’s water quality was presented dur= ing drought conditions, mainly due to the decrease in dissolved oxygen and the increase in temperature, salinity, organic matter and coliform bacteria. On= the other hand, during rainy periods, parameters indicating a decrease of water quality were color, turbidity, and nutrient content such as phosphorus and nitrogen. In general, rivers have better quality for medium flow conditions, which prevail during most of the year. The present results were analyzed in accordance with the quality objectives established in previous studies, allowing a qualitative evaluation of the wastewater interception and treatm= ent system of the city of Cuenca, Ecuador.

Keywords: Index of water quality, pollution, water uses, WQI, Paute

= 1. = INTROD= UCCIÓN

Los cuatro ríos que discurren por la ciudad de Cuenca (Tar= qui, Yanuncay, Machángara y Tomebamba), capital de la provincia del Azuay, consti= tuyen una arteria vital y de desarrollo de esta población. Además, estos ríos son afluentes importantes del río Paute, en cuya cuenca de captación inferior o= pera el proyecto hidroeléctrico Paute, de ámbito de <= /span>influencia nacional. En este = sentido, información actualizada y periódica sobre la calidad de las aguas de los mencionados recursos hídricos, constituye una herramienta fundamental para = la toma de decisiones en términos del buen uso y conservación de estos recurso= s.

Aun cuando la ciudad de Cuenca dispone de un sistema de depuración en base a lagunas de estabilización, operativo desde el ańo 1998, una de las principa= les formas de contaminación de las aguas de los ríos que atraviesan esta ciudad, ocurre por la disposición final, por dilución, de los sistemas de alcantarillado de varios de sus numerosos asentamientos menores como cabece= ras parroquiales, caseríos y una amplia población dispersa, además de vertidos ilegales, que no se encuentran conectados al sistema de colectores marginal= es del sistema de depuración de aguas. Este tipo de contaminación, por aguas residuales domésticas y/o industriales, limitan los usos del recurso tanto = para fines agrícolas, así como para abastecimiento de agua.

Los suministros de agua generalmente provienen de dos fuentes principales: aguas superficiales y subterráneas, procedencias totalmente interrelacionadas; co= mo el agua se mueve a través del sistema de vías superficiales y subterráneas = su calidad se altera frecuentemente en forma significativa, así el agua que sa= le de la zona de captación será diferente del agua que ha caído en ella como precipitación; por lo que el aporte continuo de contaminación a los ríos de= la ciudad, no afecta solamente la calidad de los cuerpos receptores, sino tamb= ién de los suministros subterráneos.

El= agua destinada a consumo humano debe cumplir requisitos de calidad, los mismos q= ue cada vez son más difíciles de alcanzar, debido a la presencia de sustancias= de muy diverso origen en las corrientes receptoras, lo que exige la implementa= ción de tratamientos costosos y difíciles de aplicar sobre todo en comunidades c= on bajo nivel técnico y escasos recursos económicos; así, la selección cuidado= sa de la fuente de abastecimiento, como la protección de los ríos, son temas r= elevantes, mientras más limpia sea el agua de la fuente o agua cruda, más barata será = el agua tratada y más sana para beber.

La calidad del agua tal como la encontramos en la naturaleza depende fundamentalmente de las características de la cuenca hidrográfica, especialmente de los suelos y de la geología, pero la actividad antropológi= ca es la más influyente en la polución de los ríos; la intensa actividad agríc= ola, ganadera y la urbanización presentes a lo largo de las subcuencas de los ríos estudiados, constituyen la principal fuente de contaminación, p= or lo que disponer de agua para bebida con requisitos de calidad es muy difícil para algunos sectores de la población que utilizan estas fuentes de abastecimiento.

Lo= s ríos tienen características propias de calidad, y ésta es variable con el tiempo= (Rauch et al., 1998). La calidad en un río, se refiere a la naturaleza y concentración de las sustancias que pueden estar presentes en = un momento determinado; algunas son de origen natural, pero otras son introduc= idas por el hombre al utilizar el cuerpo receptor como el lugar idóneo para arro= jar residuos (Carretero & Pozo-Rodriguez, 2007); los contaminan= tes en general pueden ser conservativos y no conservativos (Tebb= utt, 1998a); es útil la siguiente clasificación: i) compuestos tóxicos, que causan inhibición y destrucción de la actividad biológica, tales como: metales pesados, hidrocarburos aromáticos = policíclicos, plaguicidas, etc.; algunos de éstos hoy reciben el nombre de compuestos refractarios, porque resisten los procesos convencionales de tratamiento (Metcalf & Eddy, 2003); ii) materiales= que afectan el balance de oxígeno en el agua, como: materia orgánica, agentes químicos reductores, grasas, aceites y detergentes, etc.; iii) sólidos iner= tes en suspensión o disueltos, que a elevadas concentraciones limitan los usos = del agua. Sin embargo, el río como todo cuerpo acuático posee una capacidad de autodepuración a través de varios mecanismos como: el transporte y depósito (sedimentación) de materiales contaminantes, posiblemente alentada por la floculación bacteriana; reacciones químicas y bioquímicas que se realizan e= n la masa del agua y en la superficie de la materia suspendida (pH, sorción, ácido-base, redox, complejación, catabolismo, asimilación-desasimilación, etc.); intercambio de compuestos volátiles entre la masa de agua y la atmós= fera (pérdida o entrada de oxígeno, anhídrido carbónico, nitrógeno, etc.); reacciones redox en los sedimentos, y finalment= e la descomposición bacteriana debida a un ambiente generalmente inhóspito para bacterias entéricas y patógenas (Catalán-La Fuente & Catalán-Alonso, 1992). Todos estos mecanismos confieren al río la facultad de incorporar = en sus circuitos biológicos estos materiales y energía extrańos, recuperando su funcionalidad.

En= el agua existen dos tipos de interacciones soluto-disolvente: la inducida por aquellos solutos que “refuerzan” la estructura del agua, y la producida por solutos que la “rompen” o la distorsionan drásticamente. Los primeros suelen ser compuestos no iónicos como los hidrocarburos y en general, moléculas no polares, las cuales se sitúan en el límite del enlace del hidrógeno, reforz= ando los puentes de hidrógeno entre las moléculas de agua; los otros son sustanc= ias de carácter polar, provocan en el líquido reacciones complejas, por interacciones eléctricas que modifican la estructura tridimensional “normal” del agua (Marín-Galvín, 2019)<= span style=3D'mso-bidi-font-size:9.0pt;mso-ansi-language:ES-EC'>.

La presencia o ausencia de todas estas sustancias y en un momento dado, define= n la calidad del agua; la información que proporcionan los análisis para referir= se a la calidad, normalmente se evalúa empleando un índice (WQI o ICA) el cual, basado en un determinado modelo de cálculo, permite resumir una gran cantid= ad de información en un sólo número que, comparado luego con una escala preestablecida, define la calidad del recurso y por la tanto los usos del m= ismo (Torres, Cruz, Patińo, Escobar, & Pérez, 2010).

La conformación de un ICA, asocia parámetros de interés dependiendo del objeti= vo de la evaluación y de la zona de estudio; estos índices constituyen herramientas de mucha utilidad para los técnicos, los expertos, las autorid= ades y/o organismos encargados del manejo y control = del recurso. Literatura especializada que informa sobre los índices de calidad = más usados a nivel mundial, las bases para su conceptualización y su evolución = en el tiempo son el Oregon Wa= ter Quality Index (Cude, 2001) o el propuesto por el Departamento de Calidad Ambiental de Idaho (DEQ State Office, s. f.).

La mayoría de autores recomiendan incluir en el índice, parámetros de las cinco categorías consideradas como las más importantes: i) nivel de oxígeno, por = su importancia en la capacidad de autodepuración de las corrientes; ii) eutrofización, por constituir un problema del ecosistema con efectos en los usos del agua; iii) aspectos de sa= lud, por el riesgo sanitario; iv) características físicas, de importancia en la estética del agua; y v) sustancias disueltas, relacionadas con la presencia= de iones (Sierra-Ramírez, 2011).

Lo= s ríos objeto de estudio en este trabajo, ya han sido evaluados por la Empresa Púb= lica de Telecomunicaciones, Agua Potable, Alcantarillado y Saneamiento de Cuenca (ETAPA EP), a través del índice WQI desarrollado por la Fundación Nacional = de Saneamiento (NSF por sus siglas en inglés) de los Estados Unidos de América, basado en nueve parámetros (Dinius, 1987): oxígeno disuel= to, turbiedad, sólidos totales, coliformes fecales, variación de temperatura, pH, nitratos, fosfatos, y DBO5, y define cinco ra= ngos de calidad; la presente investigación por su parte evalúa la calidad del ag= ua con un índice que si bien está basado en el WQI original, considera 18 parámetros fisicoquímicos y microbiológicos, la metodología utilizada permi= te detectar el tiempo en el que ocurrió la contaminación e incluye parámetros relacionados con la hidrogeoquímica del agua, aspectos importantes en la calidad del recurso y no considerados en el índi= ce WQI originalmente propuesto por la NSF. Variaciones del método propuesto po= r la NSF han sido utilizadas ya en estudios previos como el de = (León-Vizcaíno, 1992) o en documentos técnicos de la Secretaría de Medio Ambiente y Recursos Natura= les de México (SEMARNAT, s. f.)

Fi= nalmente, se debe considerar que un río es un reactor permanentemente mezclado y los aspectos que controlan la calidad del agua y explican su dinámica son: el paisaje de la cuenca, los factores constitutivos de un río, y el agua misma= (Catalán-La Fuente & Catalán-Alonso, 1992). Una evaluación integral requiere atención a todos estos factores. Conservar la calidad del agua de los ríos es de vital importancia pues de su calidad depende su uso; pero el aspecto que hoy prim= a es el efecto nocivo sobre la salud humana y el medio ambiente, debido a sustan= cias tóxicas que el río puede arrastrar (e.g., Jones, 2013).

El objetivo del presente trabajo fue determinar, mediante el índice de calidad ICA, el estado de los ríos: Tarqui, Yanuncay, Machángara y Tomebamba, y evaluar la variación de la calidad del a= gua frente a las diversas posibilidades de contaminación causada por la descarg= a de agua residual sanitaria y/o industrial. Además, se definirán los usos que pueden asignarse al recurso en las actuales condiciones y especificar metas= de calidad para objetivos específicos.

= 2. = MATERI= ALES Y MÉTODOS

1.1.= Descripción de la zona de estudio

El= área de estudio corresponde a cuatro subcuencas del = río Paute, ubicadas en el sur del Ecuador, Provincia del Azuay; dentro de las mismas se encuentra el cantón Cuenca cuya población al ańo 2010 fue de 505,= 585 habitantes (INEC, 2010) y para el ańo 2019 según proyecciones del INEC existirían 625,775 habitantes.= Las subcuencas de los ríos Yan= uncay (419 km²), Tomebamba (380 km^{2)
y Machángara (325 km²) nacen en el P=
arque
Nacional Cajas, mientras que el río Tarqui (476=
km²)
nace en los páramos de Cumbe y de la parte alta de la Victoria del Portete (Figura 1).}

Figura 1. Área de estudio y estaciones de monitoreo = en las subcuencas evaluadas. Los acrónimos se defi= nen en la Tabla 1

To= dos los ríos atraviesan la ciudad de Cuenca en sentido Este–Oeste; esta ciudad cuenta con una amplia red de interceptores marginales en los cuatro ríos; s= in embargo, la cobertura en servicios de alcantarillado no es del 100%, existi= endo a la fecha de monitoreo, varias descargas que no han sido interceptadas.

1.2.= Metodología del monitoreo

Se diseńó un programa de monitoreo de nueve campańas para cada río, con estaci= ones estratégicamente ubicadas desde la zona alta hasta el final de su recorrido como se muestran en la Figura 1. Los sitios de monitoreo fueron establecidos procurando la disponibilidad de una estructura transversal al río que permi= ta la medición del caudal y la influencia de los afluentes importantes a cada = río, como cuerpos de agua natural o la descarga de la PTAR. La Tabla 1 indica las denominaciones de cada sitio de muestreo en los diferentes ríos.=

Las estaciones TO6 y TO7, están ubicadas en el río Cuenca, arteria hidrográfica= que se conforma a partir de la unión del río Tomebamba con el Machángara. Cada río fue evaluado durant= e un ańo a partir del 2012 y concluyó en el 2015, considerando períodos hidrológ= icos representativos. En cada estación se midió el caudal y se consideró los tie= mpos de paso entre las estaciones. Las mediciones de caudal se realizaron en bas= e a las recomendaciones de (Te-Chow, Madiment, & Mays, 1994): se fraccionó la sección del río en intervalos regulares (aprox. 3m), dentro de cada intervalo se midió la profundidad y c= on un correntómetro o molinete se determinó la velocidad en cada tramo. Considerando la ecuación de la continuidad se calculó el caudal parcial por cada sección, multiplicando el área de esta por la velocidad medida y el ca= udal total se calcula con la suma de los caudales parciales. Para profundidades = del río inferiores a los 70 cm se realizó una sola medición, al 60% de profundi= dad, y cuando superaba los 70 cm se realizaron dos mediciones, al 20% y al 80% de profundidad, y se determinó un promedio de dichas velocidades para esa secc= ión.

Las muestras recolectadas para los análisis fueron compuestas a volúmenes fijos= , y se captaron en tres zonas de la sección del río (margen izquierda, derecha y centro); se conservaron a 4°C durante su traslado, y parámetros como el oxí= geno disuelto y la temperatura fueron medidos in situ.

1.3.= Determinación del Índice de Calidad de Agua (ICA)

El= modelo utilizado para la evaluación del índice ICA maneja 18 parámetros (Tabla 2; = SEMARNAT, s. f.) indicativos de aspectos importantes del agua como: la estética, presencia de nutrientes, materia orgánica, disponibilidad de oxígeno y contaminación bacteriana. El cálculo del ICA se realiza aplicando un método aditivo, medi= ante la Ecuación 1. En la fórmula, cada parámetro tiene un peso relativo de acue= rdo con su importancia, como se indica en la Tabla 2.

en donde: ICA=3Díndice de calidad del agua global; I_i=3D índice de = calidad i-ésimo parámetro; Wi=3Dcoeficiente de ponderación del i-ésimo parámetro; n=3Dnúmero total de parámetros.

Las ecuaciones definidas para el índice de calidad individual de cada uno de lo= s 18 parámetros son funciones de transformación, mediante las cuales las unidades heterogéneas de expresión de cada parámetro son convertidas en unidades homogéneas de calidad de agua (Chang-Gómez, 2009). Los métodos us= ados para la determinación de los parámetros referidos son los establecidos por = el Standard Methods para la evaluación del agua y = aguas residuales (American Public Health Association, 2005). El modelo de cálculo del ICA permite, en ausencia de un dato, considerar un coeficiente de ponderación nulo para el parámetro al que corresponda en la evaluación del ICA.

El resultado del cálculo realizado con las consideraciones citadas anteriormen= te corresponde a un valor entre 0 y 100. La clasificación se realiza en 5 grup= os con un criterio de calidad correspondiente. En la Tabla 3 se muestra el criterio para la clasificación de la calidad del agua. Los usos descritos e= n dicha Tabla son compatibles con los establecidos en la normativa ecuatoriana, seg= ún el Texto Unificado de la Legislación Secundaria del Ministerio del Ambiente= (Ministerio del Ambiente, 2015); por lo tanto, los criterios de calidad obtenidos con el índice ICA= son aplicables a los usos establecidos en la normativa ecuatoriana mencionada.<= o:p>

1.4.= Clasificación de los monitoreos de acuerdo con el caudal=

Co= n el objetivo de especificar el régimen de caudal de toda una campańa de monitor= eo, se realizó un análisis por estación determinando los quintiles para cada gr= upo de datos. Al quintil 1 (<20%) se lo cataloga como un caudal bajo, al qui= ntil 5 (>80%) se cataloga como un caudal alto, mientras que para los quintile= s 2, 3 y 4 (20%<Q<80%), como caudal medio.

3.&n= bsp; RESULT= ADOS

3.1.= Análisis de caudales y variación temporal de la calidad del agua

La Figura 2 muestra la representatividad del período de muestreo; de los nueve= monitoreos realizados en cada río, cinco son cataloga= dos como de caudal medio (M), dos de caudal alto (A) y dos de caudal bajo (B), variación similar a la que presenta el caudal de los ríos durante el ańo, c= on máximos y mínimos, predominando el caudal medio.

En= cada estación, y en todos los ríos, la calidad está relacionada con el período estacional (Fig. 3). En el río Tarqui la estaci= ón con menor variabilidad de la calidad fue Zona Franca TA4 con una desviación standard = 63; en sus ICAs de 2.76; mientras que la de mayor variabilidad f= ue Parque Inclusivo TA6 ( = 63;=3D5.18), debido= a la intensa actividad recreativa y poco contralada de la zona, sobre todo duran= te los fines de semana. Para el Yanuncay, la estac= ión de menor variabilidad fue Parque El Pa= raíso Y7 (σ=3D3.27); esta estación es antes de la junta con el río Tomebamba; en cambio, la estación de mayor variabilid= ad fue Tres Puentes Y5 (σ=3D6.74), debido a descargas puntuales e intermite= ntes de agua residual doméstica no interceptada procedente de la urbanización. E= n el río Machángara la estación de menor variabilida= d es Parque Industrial M4 (σ=3D2.13) y la de mayor variabilidad fue Feria de Ganado M3 ( = 63;=3D3.78), debido= a la influencia de esta actividad intermitente de feria que se realiza los jueve= s; sin embargo, la variación de la calidad en todas las estaciones es muy pequ= eńa, lo que indica que no hay influencia significativa del período climatológico, debido a la regulación del caudal efectuada aguas arriba para el aprovechamiento energético. En el río Tomebamba= , la estación de menor variabilidad fue Sayausí TO2 = ( = 63;=3D2.2) y la de = mayor variabilidad fue Puente del Vado TO= 3 (σ=3D4.42).

Las estaciones que presentan mayor variabilidad en su calidad deben prestar may= or atención en cuanto a los usos que pueden asignarse al recurso, los cuales d= ependerán del periodo climatológico. La calidad en todas las estaciones disminuye dur= ante condiciones de estiaje y, en menor grado, en periodos lluviosos (invierno);= esto significa que si, por ejemplo, el uso fuere para abastecimiento de agua pot= able, habrá mayor variación en las dosis de coagulantes, de ayudantes de floculac= ión, de desinfectantes, etc., es decir, la potabilización se hace más difícil. O= tro uso que puede verse afectado es el riego, debido a la probable presencia de huevos de parásitos; un aspecto importante a tener en consideración es la posibilidad de la presencia de sustancias tóxicas que en condiciones de bajo caudal pueden sobrepasar la capacidad de autodepuración de la corriente.

3.2.= Variación espacial de la calidad del agua

Durante su recorrido la corriente increm= enta el caudal por el aporte de afluentes que se incorporan al curso mayor, los = cuales agregan contaminación por descargas de aguas residuales domésticas no trata= das y no interceptadas, y por acciones naturales como la escorrentía pluvial ur= bana y no urbana que arrastra nutrientes de fósforo y nitrógeno, por lo que la calidad disminuye progresivamente en todos los ríos y en todas las condicio= nes climatológicas (Fig. 3).

En el río Tarqui la calidad en todo su recorrido desciende hasta 20 unidades en promedio; pero = los tramos de mayor descenso ocurren entre las dos primeras y entre las dos últ= imas estaciones; es decir la contaminación aportada por la población de la Parro= quia Cumbe, y la debida a la urbanización del Cantón Cuenca en el último tramo, = son significativas, tanto que en la última estación (AJ Yanuncay TA7) la calidad descien= de a la categoría de “contaminado” en t= res monitoreos. El río recupera la calidad en cinco unidades en promedio en DJ Zhucay = T5, lo que significa que el río Zhucay alivia la contaminación del Tarqui. Los resultados indica= n que la calidad en el río Tarqui es superior en los = monitoreos de caudal medio, y el mayor descenso se pr= esenta en estiaje.

Para el río Yanunca= y la calidad a lo largo de su recorrido, desciende en promedio 16 unidades, p= ero el tramo de mayor deterioro, con seis puntos de diferencia, ocurre entre Los Tres Puentes Y5 y la estación = UDA Y6, por la intensa urbanizació= n y descargas de aguas residuales industriales a pequeńa escala y clandestinas.= Entre las estaciones San Joaquín Y3 y= Avda. Loja Y4, hay un descenso de caudal en tres de los nueve monitoreos realizad= os; en este tramo probablemente hay extracción de agua, lo cual incide en el valor= del ICA sobre todo en estiaje, como se observa en el monitoreo nueve, en donde = hay un descenso de calidad de 17 puntos. La calidad del río es superior en caud= al medio y el mayor deterioro se registra en caudal bajo.

En el río Machángar= a la calidad disminuye en 16 puntos en promedio durante su recorrido. Es el cuerpo superficial más protegido en su zona alta, con un ICA promedio en Chiquintad M1 de 73.9 el más alto de todos l= os ríos. Calidad superior se presenta en caudal medio, y desmejora levemente en caudales altos o bajos.

En el río Tomebamba, entre la estación Sayausí TO2 y Puente del VadoT= O3, la calidad disminuye hasta en 13 puntos en algunos mon= itoreos; presumiblemente debido a la actividad agrícola y la intensa urbanización en= el tramo considerado; después, la calidad continúa disminuyendo, pero con menor variación entre estaciones, hasta alcanzar condiciones de contaminado en la última estación (Río Cuenca) en= casi todos los monitoreos; la calidad, en promedio, = disminuye cerca de 24 puntos. En las dos últimas estaciones (antes de la PTAR TO6, y en Challuabamba TO7), ya en el río Cuenca, la calidad ya no depende del período estacional, siempre está contaminado, presentando ICAs= por debajo de 50, ocurriendo la condición más crítica en estiaje, cuando el bajo caudal del río ya no puede depurar la carga contaminante y constante de agua residual no tratada ni interceptada de la urbanización existente en Challuabamba, obteniendo ICAs hasta de 41.9.

Figura 2. Evolución del caudal durante el periodo de monitoreo en los ríos evaluados (A, M y B =3D monitoreo en caudal alto, med= io y bajo, respectivamente).

Figura 3. Valores del índice de calidad de agua en l= os cuatros ríos monitoreados durante el periodo evaluado (A, M y B =3D monitor= eo en caudal alto, medio y bajo, respectivamente; zonas de color azul, verde, amarillo y rojo claros corresponden, respectivamente, a no contaminado, aceptable, poco contaminado y contaminado).

TARQUI=

YANUNCAY

MACHÁNGARA

TOMEBAMBA

Figura 4. Influencia del caudal sobre el Índice de Calidad del Agua para los ríos evaluados. (El tipo de símbolo utilizado corresponde a la condición de caudal durante el monitoreo: alto, medio o ba= jo; las zonas de color azul, verde, amarillo y rojo claros corresponden, respectivamente, a no contaminado, aceptable, po= co contaminado y contaminado).

3.3.=         Influencia del caudal sobre el ICA

Para an= alizar la influencia del caudal sobre el ICA se ha particionado cada río de la siguiente manera: (i) tramo alto: corresponde a zonas no urbanizadas, con escasa población circundante y actividades agropecuarias escasas, (ii) tramo medio: corresponde a un área previa al ingreso al casco urbano de la ciudad= de Cuenca, (iii) tramo bajo: corresponde a puntos ubicados dentro del casco ur= bano de la ciudad o después de él. Los resultados de este análisis se presentan = para cada río en la Figura 4.

El río = Tarqui puede catalogarse como “poco contaminado” en todos sus tramos y en ocasiones en caudales bajos el tramo alto presenta condiciones aceptables de calidad. Sin embargo, no se evidencia una incidencia significativa del caudal sobre la calidad de este río. Se observa también que el ICA en la Tr= amo Alto y Medio varía dentro de un rango entre 55 y 75 durante todo el periodo= de estudio, no así en la parte baja se evidencian valores muy dispersos en un rango desde 42 hasta 70. En el río Yanuncay<= /span>, en el tramo alto, se observa que en caudales por debajo de los 10 m^{3 <=
/sup>s^-1
se mantiene una calidad aceptable, obteniendo valores de ICA cercanos a 80.=
Sin
embargo, en un monitoreo con un caudal 5 veces mayor al medio, su calidad
disminuye apenas en 5 puntos aproximadamente, debido a la erosión y la
contaminación difusa. Los tramos medios y bajos se mantienen siempre en un
estado Poco Contaminado. Es evi=
dente
en el tramo medio y bajo, que a medida que incrementa el caudal, el efecto =
de
dilución se hace significativo y su calidad tiende a mejorar. Para el río <=
span
class=3DSpellE>Machángara} se optó por dividirlo únicamente en tramo = medio y bajo ya que desde la primera estación existen varias poblaciones establec= idas. No fue posible acceder a los tramos altos por movilización y la restricción= de ingreso a estas zonas ya que es una cuenca protegida. Sin embargo, es evide= nte que el caudal no incide en el tramo medio puesto que, con respecto a la mej= or condición, para la que se obtuvo un ICA de aproximadamente 80 a un caudal d= e 3 m³/s, si se quintuplica este caudal el ICA apenas disminuye en 6 unidades manteniéndose como Aceptab= le. Con respecto al tramo bajo, la calidad se mantiene estable con excepción de= un monitoreo en donde se registró toxicidad en el río, que puede ser debido a descarga de tipo industrial o a un mal funcionamiento puntual de los interceptores marginales. Por otra parte, en el río To= mebamba se distinguen claramente tres grupos de ICA. En el tramo alto la calidad es= Aceptable para rangos menores de c= audal de 5 m³/s. En el tramo medio la calid= ad se mantiene como poco contaminado = en un rango de caudales hasta los 60 m³/s. El tramo bajo el río Tomebamba recibe los tres afluentes, Tarqui, Yanuncay y Machángara. De manera adicional, el último punto de monitoreo se encuentra en una zona que todavía no dispone de interceptores marginales y sus aguas residuales son descargadas sin tratamiento. Se puede evidenciar en este último tramo que la calidad es baja en caudales bajos o altos, y mejora ligeramente en caudales medios. En conclusión, en todos los ríos la calidad disminuye a medida que aumenta el caudal; pero el descenso es mayor en caudales bajos, por lo que = la calidad es crítica en estiaje.

3.4.=         Usos del agua en los ríos de estudio

Los valores de ICA obtenidos permiten definir los usos del agua en cada río y en cada estación (Tabla 3), siendo importante identificar aquellos que pueden asignarse en períodos de estiaje, ya que constituye la condición más crítica para la calidad.

Los ríos de mayor atención en cuanto a la contaminación y por tanto a los usos, son el Tarqui y el Tomebamba en sus zonas bajas; así, para el abastecimiento público ya es dudoso= , en ambos ríos; el uso recreativo toma condiciones de aceptable no recomen= dable en todo el río Tarqui, y en el Tomebamba ya alcanza la condición de dudoso p= ara contacto directo; para mantenimiento de pesca y vida acuática es decir = para conservar las características del ecosistema, en el río Tarqui ninguna estación es aceptable para = todos los organismos; y el Tomebamba en cambio ya alcanza condiciones de sólo organis= mos muy resistentes; finalmente para el uso industrial y agrícola, el río <= span class=3DSpellE>Tarqui está catalogado sin tratamiento para la industria normal en todas las estaciones, y el Tomebamba ya adquiere la condición de tratamiento en la mayor parte de la industria.

= 4.      =       DISCUS= IÓN

1.1.=         Características estéticas

En términos generales, durante el período de monitoreo, en el río Tarqui predomina el color,= con altos valores de turbiedad; en el río Yanuncay predomina el color acompańado de baja turbiedad; en el río Machángara la turbiedad y el color son relativamente bajos, mientras que en el Tomebamba predomina la turbiedad. Estas variaciones a= fectan los usos posteriores del agua; así, la potabilización se dificulta en perío= do invernal, mientras que en estiaje se puede incrementar la concentración de sustancias tóxicas no identificadas porque la corriente pierde capacidad de autodepuración.

En el río Machángara la regulación del caudal tiene un efecto positivo en la calidad pues presenta menos variaciones que las observadas en los otros ríos; no hay color ni tur= bidez significativa en invierno, y en verano tampoco hay concentración de solució= n. Los sólidos suspendidos, que tienen una relación directa con la turbiedad, pres= entan los niveles más altos en los ríos Tarqui, Yanuncay y Tomebamba y en condiciones de lluvia; pero es necesario considerar el aporte de sólidos por escorrentía pluvial urbana y por erosión en las subcue= ncas altas, por lo que es necesaria la protección de los suelos para evitar su deterioro, y en estudios posteriores establecer la diferenciación entre las= dos fuentes de generación de sólidos.

Durante los días anteriores a un evento de lluvia se produce un proceso de acumulación de ca= rga contaminante en superficie; esta acumulación se debe a diferentes fuentes de contaminación, entre las cuales cabe destacar: residuos vegetales y restos = de animales domésticos; compuestos y sustancias en suspensión que han precipitado, resi= duos tóxicos procedentes de emisiones de vehículos, etc. Durante un evento de ll= uvia extremo, el agua arrastra todos estos elementos transportando la carga contaminante hacia la red y evacuándola hacia el medio receptor (Temprano-González, Gabriel-Cervign= i, Suárez-López, & Tejero-Monzón, 1996).

1.2.= Nutrientes

Nitrógeno amoniacal

En el río Tarqui la concentración aumentó en estiaje (1.67 mg= L^-1), mientras que en periodo de lluvias se produjo arrastre. En el Yanuncay la mayor concentración también sucedió en estiaje (1.06 mg L^-1) pero no se nota arrastre en invierno; el = Machángara= presentó niveles bajos en la parte alta, y en estiaje no aumentó la concentración, debido a que su caudal está regulado; el valor máximo se obs= ervó en la última estación (0.99 mg L^-1). En el río Tomebamba, en la zona alta se presentar= on los valores más bajos de entre todos los ríos (0.01 mg L^-1), pero en= la parte baja (Challuabamba) se observaron los más altos, aumentaron en lluvia y en estiaje (3.1 mg L^-1).

La concentración de nitrógeno amoniacal es importante por su relación con el pH; un incremento de 7.4 a 8.0 reduce a la mitad el nivel de la concentración tóxica de este compuesto (NH₃= ); el amoníaco ionizado (NH4⁺) que predomina a bajos niveles de pH = es menos tóxico que las formas no ionizadas (NH₃); algunas estacion= es alcanzan un pH igual o mayor a 8 (Tebbutt, 1998b).

Nitrógeno de Nitratos

Cuando la materia orgánica se descompone en condiciones aerobias, la primera forma de nitrógeno en aparecer es el amoní= aco, procedente de las proteínas, urea y aminoácidos, el cual paulatinamente se = va oxidando hasta su forma final que son los nitratos; pero esta nitrificación requiere tiempo porque es una reacción cinética. Durante el periodo de lluvias, los ríos Tarqui, Machángar= a y Tomebamba presentaron una concentración máxima de 2.14, 2.52 y 0.52 mg L^-1, respectivamente; solo el Yanuncay presentó una concentración máxima de 2.69 mg L^-1 durante el peri= odo de estiaje. Los resultados de las formas de nitrógeno muestran que en el rí= o Tomebamba la concentración de amoníaco es mucho mayor= que en los otros ríos, y la de nitratos, en cambio, es la más baja; lo que indi= ca que la contaminación en este río es reciente, es decir hay un aporte perman= ente de materia orgánica por aguas residuales domésticas, a la cual le hace falta tiempo para descomponerse, representando condiciones críticas de contaminac= ión, que no se observaron en los otros ríos.

Fósforo total

En el río Tarqui la concentración máxima fue de 3.16 mg L^-1 en invierno, y mínima de 0.46 mg L-1 en estiaje; esto significa que en periodos de lluvia hay arrastre de fósfor= o debido a la poca vegetación de soporte en la subcuenca, además, hay más actividad ganadera y agrícola que en los otros ríos; el 90%= del fósforo es orgánico, lo que indica que procede de abonos, plaguicidas, dete= rgentes sintéticos, etc. En el Yanuncay, la concentración máxima ocurrió durante el periodo de estiaje (0.461 mg L^=
-1) y no se incrementó en invierno; además, un 25% del fósforo fue de origen orgánico. En el Machángara, la concentración máxima fue de 0.358 mg L^-1en invierno (periodo lluvioso), lo cual significa poco arrastre de nutrientes, además de actividades agrícolas y ganaderas a peque= ńa escala y controladas. En el Tomebamba, las concentraciones altas variaron entre <= /span>4 y 7 mg L^-1 en casi todos los monitoreos, independientemente del período climático, predomina el fósforo orgánico, lo= que significa un uso intensivo de los abonos fosforados en esta subcuenca, descargas de detergentes sintéticos y principalmente de excretas humanas. En síntesis, el río Tarqui aporta mayor cantidad de nutrientes = de nitrógeno y fósforo, por arrastre de sedimentos debido a la erosión superficial; datos coincidentes con los obtenidos en los Planes Maestros de Agua Potable y Alcantarillado de ETAPA EP = del ańo1987.

<= /span>

1.3.= Oxígeno disuelto y Demanda Bioquímica de Oxígeno DBO(5)

Los valores máximos y mínimos para los r= íos evaluados se muestran en la Tabla 4. Los valores máximos de oxígeno fueron registrados en las primeras estaciones y sobre todo en época de lluvias, de= bido a un incremento en la velocidad y por tanto a la capacidad de reaeración. En todos los ríos los niveles de oxígeno = fueron superiores a los de saturación, a la temperatura correspondiente, esto indi= ca que se favorecen los procesos aerobios de descomposición, esto es típico en ríos de alta montańa; en estiaje, en cambio, el OD desciende hasta 4.6 mg L^-1, presentándose un déficit que representa un riesgo para especies biológicas sensibles, sin comprometer la vida acuática superior. Esta afección se observa sobre todo en las últimas estaciones del río Tomebamba (río Cuenca); en términos generales, el río Machángara presenta = la menor variación de oxígeno mientras que el Tomebamba la más importante. La concentración de oxígeno disuelto tiene un especial efecto en la toxicidad de los metales pesados; si la concentración disminuy= e a la mitad del valor de saturación, los niveles de toxicidad de estos metales= disminuyen al 70%, confirmando la condición crítica de la contaminación en estiaje (Tebbutt, 1998b).

En cuanto a la DBO(₅₎, esta alcanza valores máximos, por encima de 10 mg L^-1, para todos los ríos evaluados y durant= e el período de estiaje; en cambio, en tiempo lluvioso, las concentraciones son menores, compatibles con el efecto de dilución y lavado de la biomasa.

1.4.= Conductividad, cloruros y Escherichia col= i

Los valores mínimos de conductividad y cloruros se registraron en las primeras estaciones, y los máximos al final = del recorrido; la menor variación de estos dos parámetros ocurrió en el Machángara, y la más significativa en el Tarqui, aunque en este río es importante la conductiv= idad de origen geológico. El parámetro que más incide en la calidad es el alto contenido de bacterias coliformes fecales en to= dos los ríos (Tabla 4)

La empresa ETAPA EP, en base a un estudio de la calidad de aguas en las zonas bajas de los cuatro ríos de la ciudad, en el ańo 2012, mediante el uso del = índice tradicional WQI d= e 9 parámetros (desarrollado por la Fundación Nacional de Saneamiento) concluyó= que los parámetros que más afectan al mantenimiento del ecosistema son la DBO₅y el contenido de Oxígeno Disuelto. El aporte del presente trabajo es el estudio= de la calidad con un modelo que incluye parámetros químicos que permiten identificar el origen de la contaminación (orgánico o inorgánico) a través = de medidas como la conductividad, cloruros, alcalinidad, y dureza total; el presente índice, basado en 18 paráme= tros, también aporta información sobre el momento en que se produce la contaminación, a través de la evolución= de las formas de nitrógeno; finalmente, la medición de los caudales es otro pa= rámetro útil para una evaluación más integral de la calidad de agua (ETAPA, 2008).

En el presente estudio el río Tomebamba, en la zona baja (río Cuenca), registró índ= ices de Coliformes semejantes a los reportados por E= TAPA EP en el ańo 2012. Se espera que los actuales niveles de contaminación sean= menores ya que, según información suministrada por ETAPA, en el ańo 2014 se constru= yó el interceptor en la margen derecha del río Cuenca, en una longitud de 4.2 = km; y entre el 2014 y el 2015, el interceptor en la margen izquierda del mismo = río, en una longitud de 8.9 km.

<= span style=3D'mso-bidi-font-size:9.0pt;mso-ansi-language:ES-EC'>El modelo de cal= idad utilizado en el presente estudio es válido para un diagnóstico preliminar de los cuerpos receptores, especialmente cuando se trata de estimar la calidad= en el estado preoperacional, o línea base, aspecto indispensable para evaluar el posible impacto ambiental que obras de difere= nte naturaleza puedan producir sobre la calidad del cuerpo receptor.=

<= span style=3D'mso-bidi-font-size:9.0pt;mso-ansi-language:ES-EC'>

1.5.= Metas de calidad propuestas

En los Estudios de Diagnóstico y Factibi= lidad de los “Planes Maestros de Agua Potable y Alcantarillado del Área Metropoli= tana de la ciudad de Cuenca” en 1987, se fijó una meta de calidad, a fin de que = el agua de los ríos sea apta para algunos usos como: estético, recreativo por contacto primario y secundario, y para riego= . La aptitud del agua para estos usos requiere, entre otros, un valor de bacterias coliformes fecales (Escherichia coli), hasta de 1000 NMP/100 ml, = valor recomendad= o por la Agencia de Protección Ambiental de los EEUU (EPA). En este aspecto, la Normativa Ecuatoriana TULSMA considera los usos del agua, con sus correspondientes criterios para coliformes totales y fecales (Tabla 5). Por lo visto, el criterio de meta tiene total relación con los exigidos por la Normativa Ecuatoriana, excepto para contac= to primario, (200 NMP/100 ml).

Para alcanzar este nivel, es necesario disminuir la contaminación bacteriana en 2, 3 y hasta 4 ciclos logarítmicos en los ríos de Cuenca, pero sobre todo en el río Tomebamba en su parte baja= (río Cuenca), el cual, desde la estación Puente del Vado requiere atención, en todas las condiciones climatológicas. Es= te nivel de reducción no es fácil de alcanzar si se considera el aporte de la contaminación difusa por fuentes no puntuales, que son difíciles o imposibles de controlar, como: descargas de escurrimiento directo superficial de las áreas urbanas, la carga de sedimentos por erosión = del suelo en las subcuencas, la contaminación por escorrentía pluvial no urbana, la descarga y rebose de los colectores marginales hac= ia los cuerpos superficiales y sobre todo los derrames sin control de agua de lluvia en los alcantarilla= dos combinados que se incluyen también en la categoría de contaminación no punt= ual.

Cuando se practica un control eficiente = de las fuentes puntuales, por ejemplo, a través de los interceptores marginales, l= as fuentes no puntuales pueden tener una contribución significativa en la contaminación; siendo importante que, al preparar las políticas de control = de la contaminación, se tenga en cuenta esta contribución ya que de otra maner= a se pueden sobreestimar las metas de la política para el control del medio ambi= ente (Tebbutt, 1998b).

Al tratar de resolver el problema de la contaminación de los ríos, no se pueden centrar todos los esfuerzos en la construcción de depuradoras y en el tratamiento de las aguas residuales pues aproximadamente un 50% de la contaminación vertid= a al medio receptor proviene de los vertidos en tiempo de lluvia. En muchas ocasiones, los logros conseguidos mediante la construcción de depuradoras y= el tratamiento de las aguas en tiempo seco quedan anulados por este tipo de descargas (Temprano-González et al., 1996).

1.6.= Plan de vigilancia de la calidad de los ríos

Un monitoreo trimestral, incluyendo tiempos de paso y mediciones de caudal, permitirá un diagnóstico oportuno de la calidad, sobre todo en las zonas bajas y en estiaje, que representan las condiciones más desfavorables. Un plan de vigilancia de este tipo permitirá evaluar la eficiencia de los interceptores marginales. Según información proporcionada por ETAPA EP, en el período 2014-2018 se han construido en total 34.8 km de interceptores, y entre el 2018 y el 2019 se construyeron los interceptores de la Quebrada Alpayacu= (0.4 km) y del río Machángara (5.6 km). Los nue= vos interceptores se van sumando a la red ya existente en los diferentes ríos y quebradas del sector. El plan de vigilancia permitirá detectar condiciones = de riesgo toxicológico sobre todo cuando el agua es destinada para consumo hum= ano, debido a descargas accidentales y/o clandestinas de materiales tóxicos y, aunque su identificación y cuantificación no son sencillas, sí es posible implementar “bioensayos de control” que adviertan la presencia de material peligroso.

&= nbsp;

= 5. = CONCLU= SIONES

En todos los ríos el índice de E. Coli es el parámetro que más incide en= la calidad. El análisis estadístico muestra que en condiciones de estia= je este parámetro aporta con menos de una unidad de calidad al valor del ICA total, sobre todo en las zonas medias y bajas. Es de esperar que la construcción de los interceptores marginales (onerosa obra de saneamiento) tenga un efecto positivo en la reducción de la contaminación microbiana, sin aspirar a los niveles deseados (NMP/100 ML, semejantes a 1,000) por los factores anteriormente expuestos. Menos significativos que la polución microbiana, son la contaminación por materia orgánica y el descenso de oxíg= eno. Otros parámetros que restan calidad al recurso son los nutrientes de nitróg= eno y fósforo, provenientes de fuentes puntuales como descargas de aguas residu= ales domésticas y fuentes no puntuales, difíciles e imposibles de controlar como= lo son las descargas de escurrimiento directo superficial procedentes de áreas urbanas y rurales.<= /span>

De los ríos estudiados, el Tomebamba puede ser catalogado como el cuerpo re= ceptor más crítico en lo que se refiere a contaminación. En su parte baja (= río Cuenca), su único uso posible corresponde a “transporte y asimilación de desechos”. En general, en las cabeceras de los ríos, la <= span style=3D'mso-bidi-font-weight:bold'>calidad bacteriológica es satisfactoria= , pero esta calidad comienza a deteriorarse paulatinamente a partir de la par= te media, experimentando una notable degradación en el área urbana de la ciuda= d, esto no solo ocurre con la calidad bacteriológica sino de todas las características evaluadas. Los recuentos de coliformes= son superiores con tres o cuatro ciclos logarítmicos, a los establecidos por los criterios de calidad para varios usos, por esto, la contaminación bacteriana constituye el mayor problema en la calidad de los cuerpos recept= ores, representando así un problema de salud pública. El río Machángara presentó la= calidad más alta durante el período de evaluación, con un ICA máximo de 79.6 y un mínimo de 53.4; no obstan= te, en un monitoreo se detectó toxici= dad en la última estación, esto es, pasando la zona del parque industrial, aunque esta situación fue esporádica, es importante un control sobre el vertido de las descargas industriales sobre = todo de las instantáneas, las cuales según su naturaleza inciden fuertemente en = el ecosistema.

Los cuatro ríos evaluados pertenecen a subcuencas frágiles, de alta pendiente, con perío= dos de retención cortos. La naturaleza química del agua demuestra po= ca capacidad de amortiguamiento, con alcalinidades que no superan los 65 mg/l = como CaCO₃, en condiciones naturales; en general son aguas blandas, c= on bajas concentraciones de calcio y magnesio; bajas concentraciones de elemen= tos como el sodio o potasio, lo que incrementa el efecto tóxico de metales pesa= dos como el plomo y el cinc para los peces, por la débil posibilidad del agua p= ara complejar los metales pesados en estas condiciones; se trata entonces de equilibrios químicos lábiles y de fácil modificación.

Previo a la asignación o concesión del recurso agua, organismos de control como la SENAGUA deben tomar en consideración estas características fundamentales que demuestran la fragilidad de los sistemas evaluados. Cualquier alteración de las zonas altas de estos ríos -por ejemp= lo, concesiones para actividades mineras- podría repercutir de forma directa y rápida en la calidad del agua, aspecto crítico cuando su uso es para consumo humano.

= 6. = RECOME= NDACIONES

Es necesaria una adecuada planificación urbana, que garantice la conexión total de las r= edes de alcantarillado a los interceptores marginales para impedir el vertido directo del agua residual doméstica a los cuerpos receptores. En cuanto al control de la calidad del agua, se debería iniciar un estudio relacionado c= on la formulación de un Índice de Calidad que incluya la presencia de sustanci= as tóxicas para ríos de alta montańa; para ello es necesario seleccionar el o = los indicadores de toxicidad que sean representativos de las aguas estudiadas; = por el alto contenido de nutrientes de fósforo en el río T= omebamba, quizás los plaguicidas órganos fosforados puedan considerarse los adecuados= ; en el río Yanuncay, el pronunciado color, acompańa= do de baja turbiedad, merece el estudio de su naturaleza; es decir, la identifica= ción de las sustancias húmicas presentes, las cuales, de no ser eliminadas eficientemente en los procesos de potabilización convencionales, durante la cloración pueden generar subproductos como los trihalo= metanos (THM), de reconocido efecto tóxico; estudios realizados sobre estas sustancias se han enfocado en la búsqueda de Cloroformo CHCl_{3;
Bromo diclorometano CHBrCl₂; Dibromoclorometano=

CHBr₂Cl Tribromometano
CHBr₃, o de sus principales precursores como los ácidos húmicos y
los ácidos fúlvicos. En el río Machángara,
después del Parque Industrial, los elementos tóxicos de interés pueden ser =
los
metales pesados, como plomo, mercurio, arsénico o aluminio. Todas las
sustancias mencionadas están citadas en la Normativa TULSMA, para los disti=
ntos
usos del agua. La razón de su búsqueda es importante por el efecto tóxico s=
obre
el hombre y los ecosistemas en general; la severidad de sus efectos depende=
de
la dosis recibida, el período de exposición y otros factores ambientales. La
principal preocupación en el abastecimiento del agua potable es el efecto a
largo plazo de la exposición crónica a niveles bajos de compuestos tóxicos,=
los
cuales no son eliminados por los tratamientos convencionales aplicados en
nuestro medio, por lo que la alternativa más segura es la protección del ag=
ua,
desde su fuente}(Pauta-Calle, 2014)= .

Todos los suministros de agua potable deben implementar un sistema de control de calidad del agua distribuida, no obstante, este control es variable en el tiempo y en espacio; para suministros pequeńos, y sobre todo a nivel rural, esta actividad consistirá en la detección de organismos indicadores de contaminación fecal, para eliminar el riesgo de la transmisión de enfermeda= des hídricas, las cuales si no son oportunamente atendidas pueden producir la m= uerte de los consumidores en menos de una semana. Para suministros grandes y con potencial técnico y económico, el control de la calidad está encaminado a la búsqueda de sustancias peligrosas que, ingeridas en pequeńas dosis y por la= rgos períodos, pueden producir una toxicidad crónica; por lo que se sugiere a los organismos de control, la selección, para cada una de las subcuencas, de indicadores de toxicidad del agua en los ríos, en función de los usos del suelo.

REFERENCIAS

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Carreter= o, M. I., & Pozo-Rodriguez, M. (2007). Mineral= ogía aplicada. Salud y medio ambiente. Recuperado de https://www.paraninfo.es/catalogo/9788497324878/mineralogia-aplicada--salud= -y-medio-ambiente

Catalán-= La Fuente, J., & Catalán-Alonso, J.-M. (1992). Ríos: Caracterización y calidad de sus aguas.

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Metcalf, & Eddy. (2003). Wastewater Engineering: Treatment and Reuse (4.<= sup>a ed.). Recuperado de https://www.iberlibro.com/servlet/BookDetailsPL?bi=3D30432970902&search= url=3Dan%3Dmetcalf%2Beddy%26sortby%3D20%26tn%3Dwastewater%2Bengineering%2Bt= reatment%2Breuse&cm_sp=3Dsnippet-_-srp1-_-title1

Minister= io del Ambiente. (2015). Reforma texto unificado legislación secundaria, medio ambiente (TULSMA), libro VI, Decreto Ejecutivo 3516, Registro Oficial Suplemento 2, 31/03/2003. Recuperado de http://www.ambiente.gob.ec/wp-content/uploads/downloads/2018/05/Acuerdo-097= .pdf

Pauta-Ca= lle, G. (2014). Estudio integral de la calidad del agua del río Burgay y evaluación del riesgo toxicológico por la probable presencia de plaguicid= as (Master thesis, Universidad de Cuenca). Recuper= ado de http://dspace.ucuenca.edu.ec/handle/123456789/19831

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MASKANA, Vol. 10, No. 2, 7= 6–88, 2019

https://publicaciones.ucue= nca.edu.ec/ojs/index.php/maskana/article/view/2670

<= span lang=3DEN-US style=3D'font-size:8.0pt;font-family:"Verdana","sans-serif"; mso-fareast-font-family:Calibri;background:white;mso-ansi-language:EN-US'= >doi: 10.18537/mskn.10.02.10

© Author(s) 2019. CC Attribution 4.0 License.

Publicado por DIUC - Dirección de Investigación de la Universidad de Cuenca = 1

G. Pauta-Calle et al. Evaluación de la calidad de agua de los ríos de la ciudad de Cuenca

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MASKANA, Vol. 10, No. 2, 76–88, 2019

doi: 10.18537/mskn.10.02.10 = = 2

R. Cazar et= al. Análisis cuantitat= ivo de una mezcla binaria

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