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Determinación de la eficie= ncia en el uso de fosas sépticas y filtros anaerobios (Biodigestor) para el tratamiento de aguas residuales domésticas

 

Determination of the efficiency in the use of septic tanks and anaerobic filters (Biodigester) for the treatment of domestic wastewater

 


1

María Valeria González León

https://orcid.org/0000-0002-0034-6699

 

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Universidad Católica de Cuenca, Maestría en Construcciones con menc= ión en Administración de la Construcción Sustentable, Cuenca, Ecuador

maria.gonzalez.78@e= st.ucacue.edu.e c <= /p>

 

2

Diego Coronel Sacoto

&nbs= p;

https://orcid.org/0000-0001-8105-4102

 

&nbs= p;

Universidad Católica de Cuenca, Maestría en Construcciones con menc= ión en Administración de la Construcción Sustentable, Cuenca, Ecuador,

dcoronels@u= cacue.edu.e c  

 

3

Carlos Matovelle Bustos

&nbs= p;

https://orcid.org/0000-0003-2267-0323

 

&nbs= p;

Universidad Católica de Cuenca, Maestría en Construcciones con menc= ión en Administración de la Construcción Sustentable, Cuenca, Ecuador

cmmatovelle= b@ucacue.edu.ec 

 

=  

 

Artículo de Investigación Científica y Tecnológica

Enviado: 05/12/2021

Revisado: 20/12/2021

Aceptado: 17/01/2022

Publicado:05/04/2022

DOI: https://doi.org/10.33262/= ap.v4i2.1.191          <= u>

 

=  

 

 

Cítese:

 

 

González León, M. V., Coronel Sacoto, D., & Matovelle Bustos, C. (2022). Determinación de la eficiencia en el uso de fosas sépticas y filtros anaerobios (Biodigestor) para el tratamiento de aguas residuales domésticas. AlfaPublicaciones, 4(2.1), 6–24. https://doi.org/10.33262/= ap.v4i2.1.191

 

 

 

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Palabras claves:= fosa séptica, biodigestor, agua resid= ual, eficiencia.

 

Resumen

Introdu= cción La construcción de fosas sépticas o implantación= de biodigestores en residencias habitacionales generan una serie de dudas so= bre la calidad del tratamiento que se da a las aguas residuales domesticas; manifestadas en problemas como: malos olores, color del agua y la insegur= idad de la sociedad sobre los parámetros que cumple el líquido tratado próximo= a regresar a un lecho filtrante. Objetivo. En la presente investigac= ión, se plantea demostrar y comparar la efectividad de fosas sépticas y biodigestores en el tratamiento de aguas residuales domésticas. Metodo= logía. Esto se realiza mediante el análisis estadístico de los datos proporciona= dos del monitoreo de fosas sépticas que realiza el departamento de operacione= s de agua potable y saneamiento de ETAPA EP y del control de agua de salida qu= e se toma en Biodigestores. Para establecer los rangos de calidad del agua tra= tada y emitir recomendaciones para el diseño y uso de estos aparatos de tratamiento de aguas residuales fue necesario tabular datos estadísticos = de monitoreo de aguas. Con los datos obtenidos y en distintos escenarios en condiciones óptimas y condiciones específicas con diferentes características como:  tipo de suelo, área para su implantac= ión, vías de acceso y su disposición final, una vez obtenidos los resultados se realizó un diagnóstico comparativo para identificar la eficiencia en el u= so de fosas sépticas y biodigestores. Resultados. Los resultados obtenidos no demuestran que la falta de conocimiento sobre las condiciones previas a la implantación de este tipo de tratamiento influye directament= e en el mal uso de estos. Conclusión. Concluimos que tanto fosas séptic= as como biodigestores son efectivos en el tratamiento de aguas residuales domesticas siempre y cuando estén bien construidas e instaladas, tomando = en cuenta las normativas existentes para su construcción, es importante mencionar que es imprescindible tomar medidas para la utilización de estos aparatos en las edificaciones actuales y futuras y así obtener resultados positivos.

 

 

Keywords:=

 

Abstr= act

Introduction= The construction of septic tanks or the implantation of biodigesters in residences generate a series of doubts about the quality of the treatment given to domestic wastewater; manifested in problems such as: bad odors, color of the water and the insecurity of society about the parameters that the treated liquid meets, about to return to a filter bed. Target. In the present investigation, it is proposed to demonstrate and compare the effectiveness of septic tanks and biodigesters in the treatment of domest= ic wastewater. Methodology. This is done through the statistical analysis of= the data provided from the monitoring of septic tanks conducted by the depart= ment of drinking water and sanitation operations of ETAPA EP and from the cont= rol of outlet water that is taken in Biodigesters. To establish the quality ranges of the treated water and issue recommendations for the design and = use of these wastewater treatment devices, it was necessary to tabulate statistical data from water monitoring. With the data obtained and in different scenarios in optimal conditions and specific conditions with distinctive characteristics such as: type of soil, area for its implementation, access roads and its final disposal, once the results were obtained, a comparative diagnosis was made to identify the efficiency in = the use of septic tanks and biodigesters. Results. The results obtained do not show that the lack of knowledge about the conditions prior to the implementation of this type of treatment directly influences their misuse. Conclusion. We conclude that both septic tanks and biodigesters are effec= tive in the treatment of domestic wastewater if they are well built and instal= led, considering the existing regulations for their construction, it is import= ant to mention that it is essential to take measures for the use of these dev= ices in current and future buildings and thus obtain positive results.

 

 

 

Introducción

El presente artículo tiene como objetivo demostrar= la efectividad de dos tipos de tratamiento para aguas residuales que son, la f= osa séptica y el uso de biodigestores, para lo cual se realiza un análisis estadístico de datos obtenidos, tanto de fosas sépticas, proporcionados por= la empresa municipal ETAPA EP, como de biodigestores, datos obtenidos  del laboratorio ANAVALAB, donde los resu= ltados nos demuestran una efectividad de las dos metodologías, dado que  se evidencia una tendencia baja consider= able en cuanto a los valores de ingreso del agua con los de salida, para el tratamiento de agua basadas en fosas sépticas se consigue  una efectividad de DBO del 80,86%, para= DQO 75,1% y para SST de un 90,23%, mientras que para los biodigestores la efect= ividad es de 84.16% para DBO, 75,32% para DBQ y 85,44% para SST.  En los resultados que se pudieron anali= zar de los distintos tratamientos existe una diferencia no mayor al 5% lo que sign= ifica que funcionan de manera adecuada y que son sistemas óptimos para cumplir co= n el tratamiento primario de aguas residuales.

Aguas Residuales

El agua es una fuente vital para el ser vivo, sobre todo para el ser humano ya que no solo la utiliza para consumo sino también para diferentes actividades que le proporcionan una buena salud, alimentación, desarrollo, confort, entre otros, estas aguas usadas se convierten en desechos que han adquirido el nombre de aguas residuales (Muñoz Cruz, 2008= ). Provienen de cuatro fuentes principales, aguas domésticas, industriales, de uso agrícola, y pluviales <= /span>(Muñoz y Orellana, 2019).

Es en las zonas residenciales y centros comerciales en donde se generan la mayor cantidad de agua residuales. En la primera se producen caudales que dependen de la densidad de la población y = de la contribución de aguas residuales por habitante, en la segunda la obtenci= ón de caudales se basa en la comparación de datos existentes en la zona con la futura o nueva implantación (Cajigas, 1995).

Por otro lado, Valdez y Vázquez (2003) mencionan que lo= s componentes más significativos de este tipo de agua son:  1) Los sólidos suspendidos, de naturalez= a orgánica, en su gran mayoría se encuentran en los desechos humanos, desperdicios de a= limentos, papel, trapos, entre otros, 2) Los compuestos orgánicos biodegradables, est= os se consideran organizamos solubles y está compuesto de proteínas, carbohidr= atos y lípidos, estos contiene carbono por lo que poseen una demanda de oxígeno y oxigeno nitrogenado y 3) Los microorganismos patógenos, en estos están presentes bacterias, virus, protozoarios y helmintos, estos pueden ser causantes de varias enfermedades como la tularemia, cólera,, Hepatitis, amebiasis, equinococosis, entre otros.

Las aguas residuales posen ciertas caracterí= sticas físicas , químicas y bilógicas que son de suma importancia para su análisis= , aquí mencionaremos unas de las principales, dentro de las físicas están los sóli= dos totales( desde ahora ST) que a su vez se dividen en 1) Solidos suspendidos totales (SST), a estos pertenecen los sólidos suspendidos volátiles(SSV) y = los sólidos suspendidos fijos (SSF), 2) Solidos Disueltos Totales (SDT) y 3) Solidos Sedimentables (SS), en cuanto a los parámetros químicos tenemos: 1)Materia orgánica (MO) en donde encontramos proteínas, lípidos y carbohidratos los cuales se pueden analizar bajo  dos= parámetros a) Demanda Bioquímica de Oxigeno (DBO) que es un método indirecto que mide = el oxígeno disuelto, se usa para estudios de materia orgánica, que sea biodegradable, = y b) Demanda Química de Oxigeno (DQO) que de igual manera mide el oxígeno pero c= on el fin de crear procesos de estabilización química, además este valor siemp= re será mayor al de DBO (Muñoz y Orellana, 2019).

Cajigas (1995) menciona que para el estudio = de aguas residuales existen métodos cuantitativos que ayudan apara determina la composición química, estos pueden ser gravimétricos, volumétricos o fisicoquímicos y métodos cualitativos que permiten un estudio de las características físicas y bilógicas.

Fosas Sépticas

Las llamas fosas sépticas aparecen gracias a Haute Saone quien por  una eventualidad, = decidió ejecutar un estanque, donde recolectaría, aguas usadas y agua proveniente d= e la lluvia, con fin de evadir limpiezas constantes adiciono al estaque un tubo que  daba salida a un pozo absorben= te, durante años el estanque no necesito limpieza, es por eso que  junto con Moyrno, un periodista, realiz= aron varios ensayos añadiendo materias fecales, orina, entre otros, con fin de estudiar el fenómeno, sus pruebas constataron una desintegración de la mate= ria completa , a los 20 días, obviando algunos componentes que no eran digeribl= es en el estómago humano, semillas, coles, cebollas entre otros,  como resultado de las descomposición se generaba un líquido,  de color café= tenue con olor a sulfhidrato de amoniaco, comprobaron además que el uso de abunda= nte de agua  era de gran ayuda para una= mejor descomposición de la materia (López, 2014).

Ahora bien, las fosas sépticas, se han ido implementando a lo largo de los años, como uno de los mecanismos más importantes para el tratamiento de aguas residuales, según Gijón et al. (2= 007) las fosas sépticas están diseñadas y construidas para recibir estas aguas, separar sólidos de líquidos, proveer = una digestión de la materia orgánica, almacenar sólidos, y permitir extraer el líquido para posteriormente darle tratamiento. Este tratamiento consta de 3 etapas: 1) El tanque como tal, que funciona como sedimentador, 2) La etapa = del drenaje, aquí se presentan dos acontecimientos, a) la continuación del tratamiento mediante biodegradación y b) la absorción que se genera por la preparación del suelo, para esta etapa es recomendable utiliza piedras, ent= re 7 y 10cm, con objeto de permitir una evapotranspiración y 3) y la remoción, q= ue se refiere al tratamiento de lodos (Rosales Escalante, 2005).

Respecto al tanque séptico este posee tres zonas determinadas: 1) Zona inferior, donde se asientan los llamados lodos, 2) Zo= na Central, la que permite la separación de las partículas, y 3) Zona Superior, donde se alojas las grasas, aceites, entre otros, formando una capa de espu= ma en la superficie del tanque, llamadas natas (Gijón et al., 2007). Dentro de este se origina un proceso bioló= gico considerado natural y bacteriológico, que provoca la presencia de un tipo de bacterias pertenecientes al grupo de las anaeróbicas, esto se debe a que el tanque al ser hermético no permite el ingreso de aire, además de las bacter= ias se producen gases, encargados de una mayor descomposición en la zona superi= or, estos gases ayudan a la putrefacción, por otro lado es importante destacar = que el tiempo de funcionamiento del taque está determinado por la capacidad anaerobia que poseen, ya que no solo ayudará a la descomposición de solidos sino además de materia orgánica disuelta y coloidal (González et al., 2020).

Asimismo, Rosales Escalante (2005), menciona que e= ste sistema aprovecha la capacidad de absorción del suelo, por lo que, su efica= cia depende de que el tanque cumpla de manera apropiada la retención de sólidos= y grasas, sin dejar de lado que el suelo donde se emplace deberá permitir una= absorción adecuada, asevera además que el tamaño ideal para una buena sedimentación debería tener una relación de 1:3 entre el ancho y la longitud, y una profundidad mínima de 1metro.

Es indispensable mencionar que el mantenimiento del taque es primordial para que este tratamiento funcione de manera correcta, = por lo que es preciso realizar como mínimo una inspección al año, donde se considera, la revisión del taque, el ingreso de sustancias toxicas y desinfectantes al tanque, los empaques en las conducciones que conectan el tanque con el sistema en campo, y la cantidad de lodo y espuma acumulado (Gijón et al., 2007).

Las fosas sépticas son una herramienta bastante vá= lida para el tratamiento de aguas residuales, han sido utilizadas con resultados positivos durante varios años, sin embargo, la mala construcción, el mal us= o, la falta de mantenimiento, puede causar conflictos importantes para la salud del ser humano, es por esto la importancia de tomar en cuenta recomendacion= es que permitan que el sistema funcione adecuadamente.

Como ya se dijo este sistema es muy utilizado por = su efectividad, tal es el ejemplo de la ciudad de Cuenca en donde en los últim= os años se han construido diferentes proyectos para el tratamiento de aguas residuales, siendo algunos de ellos los siguientes: Achayacu, Cementerio, Escaleras, Laureles, Octavio Cordero, Quillopungo, Quingeo, Tutupali, San Pedro, Bella Unión, Tarqui Macas, Guabo, El Chorro, entre otras (Empresa de Telecomunicaciones, Agua Potable, Alcantarillado y saneamiento de Cuenca [E= TAPA], 2021).

Biodigestores

El uso de nuevas tecnologí= as para el tratamiento de aguas residuales domesticas ha generado que la empre= sa privada a nivel mundial innove y pueda brindar nuevas alternativas para cum= plir con esta función, teniendo así el sistema Biodigestor Autolimpiadle que es = un sistema para el tratamiento primario de aguas residuales domésticas.

El biodigestor es un contenedor hermético, cerrado, el cual se diseña para recibir materia orgán= ica, principalmente desechos, dentro de este se coloca agua pretendiendo descomp= oner la materia orgánica, este proceso genera gas metano y además fertilizantes = orgánicos que contienen potasio, fosforo y nitrógeno (Jaimovich et al., 1901).

Según Alarcón y Carrasco (2021) es un proceso digestivo que resulta de la secuenc= ia de varias etapas que se desarrollan en un marco de tiempo, está conformado = por varios componentes como son : a) Cámara de carga, donde se ingresa los dese= chos orgánicos, b) Reactor o digestor, es un tanque subterráneo que cumplen la función de descomponer desechos, está conectado con cámaras de carga y descarga, c) Cámara de descarga, recoge los residuos del reactor, mimas que sirven de abono d) Cubierta de plástico, va colocada sobre el reactor, su objetivo es no permitir que ingrese el aire evitando fugas de gas, e) Tuber= ía, conduce el gas que se produce e impide que sobresalga de los niveles permit= idos además expulsa el agua condesada y f) llave de paso, sirve como regulador de salida del gas.

Es transcendental aludir q= ue es considerado amigable con el medio ambiente, por su factibilidad para construir y por su capacidad de producir bacterias anaerobias, mismas que genera biogás, las cuales pueden ser utilizadas en vez de gasolina o Diesel= , en procesos de combustión, además pueden generar energía que remplaza a la electricidad, por otro lado las biogás convierten las excretas en residuos = válidos para destruir microrganismos, huevos de parásitos, con lo que logran impedir que se multipliquen y de esta manera ayudan a la reducción de contaminación= del ambiente (Menéndez Peralta, 2021).

Metodología

Para obtener datos del monitoreo de Plantas de Tratamiento de Aguas Residuales acudimos a entidades de control y monitoreo= de la ciudad de Cuenca; mientras que para los datos relacionados con la calida= d de agua de Biodigestores se obtuvo información del monitoreo que realiza el laboratorio ANAVANLAB a biodigestores ubicados en la ciudad de cuenca. La relevancia de los factores externos de la ubicación de cada una de las PTAR como de los Biodigestores han sido omitidos ya que todos están ubicados en = la zona rural del cantón.

Con estos datos pudimos realizar diferentes comparaciones de calidad de agua de salida, tomando en cuenta factores soci= ales de costo-beneficio de cada uno de estos sistemas.

En la parte comparativa de los sistemas de tratami= ento se ha tomado como horizonte del estudio los límites máximos permisibles encontrados en Norma de Calidad Ambiental y de descarga de efluentes: recur= so agua.

 

 

 

 

Tabla 1

Información PTAR rurales: Promedios anuales y Lími= tes máximos permisibles

Sistema

DBO de entrada

DBO de salida

Límite
máximo
permisible

DQO de entrada

DQO de salida

Límite
máximo
permisible

SST Entrada

SST Salida

Límite
máximo
permisible

Achayacu

108.88

41.67

100

335.68

154.75

250

197.94

59.07

100

Cementerio

366.02

93.17

100

786.29

251.5

250

504.43

53.25

100

Escaleras

296.33

53.56

100

1023.11

322.11

250

797.56

28.33

100

Laureles

352.15

87.69

100

937.11

274.26

250

318.04

39.73

100

Octavio

71.63

7.86

100

212.22

42.17

250

100.33

7.33

100

Quillopungo

216.79

84.39

100

612.54

188.31

250

743.56

31.84

100

Quingeo

436.63

23.07

100

1016.34

84.28

250

1856

15.1

100

Tutupali

662.18

53.23

100

1484.88

156.29

250

1283.28

58.15

100

San Pedro

200.85

30.33

100

616.93

147.57

250

338.46

29.69

100

Bella Unión

304.77

31.5

100

850.92

205.92

250

491.83

24

100

Tarqui

417.72

107.11

100

1221.44

304.61

250

846.59

116.12

100

Macas

98.34

15.14

100

252.22

67.53

250

121.21

33.71

100

Guabo

472.57

44.23

100

1334.03

170.32

250

1485.23

31.97

100

Churuguzo

282.44

58.38

100

647.75

187.27

250

941.08

56.04

100

Fuente: Empresa de Telecomunicaciones, Agua Potable, Alcantarillado y saneamiento de Cuenca (2021)

 

Tabla 2

Información Biodigestores: Promedios anuales y Lím= ites máximos permisibles

Sistema

DBO de entrada

DBO de salida

Límite
máximo
permisible

DQO de entrada

DQO de salida

Límite
máximo
permisible

SST Entrada

SST Salida

Límite
máximo
permisible

 

 

BIODIGESTOR 1

275.22

34.22

100

350.33

80.33

250

303.3

30.12

100

 

BIODIGESTOR 2

313.33

57.92

100

378

90.3

250

289.33

33.41

100

 

BIODIGESTOR 3

340.33

65.73

100

380.23

102.22

250

279.12

35.42

100

 

BIODIGESTOR 4

225.22

52.93

100

279.11

89.22

250

180.22

44.12

100

 

BIODIGESTOR 5

262.93

14.33

100

313.33

55.55

250

215.23

30.44

100

 

Fuente: Analítica Avanzada Asesoría y Laboratorios Cía. Ltda. (ANAVANLAB, 2021)= ;  Ministerio del Medio Ambiente (2011)

 

El esquema de funcionamiento de las Plantas de Tratamiento de Agua Residuales domesticas monitoreadas por ETAPA-EP tenemos= la Fosa Séptica + Filtro Anaerobio y Fosa Séptica + Humedales Artificiales (fi= gura 1).

Figura 1

Vista interna de la fosa séptica y filtro anaerobi= o de la PTAR Macas; y Esquema de funcionamiento del sistema humedal

 

Fuente: Guamán y Molina (2015)

Mientras que el biodigestor, posee un sistema para tratar aguas primarias domésticas, esto mediante un proceso de retención y degradación, séptica anaerobia, y de manera orgánica, el agua tratada es infiltrada hacia el terreno aledaño mediante una zanja de infiltración, poz= o de adsorción y/o humedal artificial según el tipo de terreno en donde se coloq= ue el biodigestor (Figura 2).

Figura 2

Esquema de funcionamiento biodigestor

Nota: Vista del funcionamiento del biodigestor

Fuente: PROCON (2018)

Una medida cuantitativa de la contaminación del ag= ua por materia orgánica es la determinación de la rapidez con la que se consum= e el oxígeno por la descomposición bacteriana y se denomina Demanda Biológica/Bioquímica de oxígeno (DBO). Existen algunos factores que afectan= la DBO como la temperatura del medio, la clase de microorganismos, la cantidad= y tipo de elementos nutritivos presentes, si estos factores son constantes, se puede utilizar el tiempo de la permanencia del agua en un reactor para elim= inar la materia orgánica por consumos en medios aerobios o anaerobios.

Esta investigación según su naturaleza es de tipo cualitativa participativa ya que estudiamos un caso en específico, como variables tenemos los datos de calidad de agua de ingreso y salida, estudia= do en la zona rural del cantón Cuenca obteniendo datos mediante monitoreos de ETAPA-EP y pruebas en laboratorio ANAVANLAB.

Resultados

Tanto del monitoreo de calidad de agua de PTAR en = la zona rural proporcionados por ETAPA-EP, como el monitoreo realizado con el laboratorio ANAVANLAB con un promedio anual tomado desde enero 2020 a dicie= mbre del mismo año. obtenemos curvas de comportamiento de los siguientes valores: DBO de entrada, DBO de salida, DQO de entrada, DQO de salida, Solidos Suspendidos Totales de entrada, Solidos Suspendidos Totales de salida, Coliformes Fecales de entrada, Coliformes Fecales de salida, mismos que ser= án analizados con porcentajes de efectividad mediante fórmulas matemáticas y d= etallados en cada una de las figuras.

Figura 3

Comportamiento DBO de entrada y salida de PTAR

Figura 4

Comportamiento DBO de entrada y salida de Biodigestores

Del análisis del DBO de PTAR hemos obtenido el comportamiento para determinar su porcentaje de efectividad en el tratamien= to de aguas residuales domesticas de la siguiente manera (Tabla 3).=

Tabla 3

Porcentaje de efectividad DBO PTAR

Sistema

DBO de entrada

DBO de salida

Diferencia

%

Achayacu

108.88

41.67

67.21

61.73

Cementerio

366.02

93.17

272.85

74.55

Escaleras

296.33

53.56

242.77

81.93

Laureles

352.15

87.69

264.46

75.10

Octavio

71.63

7.86

63.77

89.03

Quillopungo

216.79

84.39

132.4

61.07

Quingeo

436.63

23.07

413.56

94.72

Tutupali

662.18

53.23

608.95

91.96

San Pedro

200.85

30.33

170.52

84.90

Bella Unión

304.77

31.5

273.27

89.66

Tarqui

417.72

107.11

310.61

74.36

Macas

98.34

15.14

83.2

84.60

Guabo

472.57

44.23

428.34

90.64

Churuguzo=

282.44

58.38

224.06

79.33

 

En promedio de los porcentajes de efectividad tene= mos:

De la misma manera con el análisis del DBO de Biodigestores obtenemos el comportamiento para determinar su porcentaje de efectividad en el tratamiento de aguas residuales domesticas de la siguiente manera (Tabla 4).

Tabla 4

Porcentaje de efectividad DBO Biodigestor

Sistema

DBO de entrada

DBO de salida

Diferencia

%

BIODIGESTOR 1

275.22

34.22

241

87.57

BIODIGESTOR 2

313.33

57.92

255.41

81.51

BIODIGESTOR 3

340.33

65.73

274.6

80.69

BIODIGESTOR 4

225.22

52.93

172.29

76.50

BIODIGESTOR 5

262.93

14.33

248.6

94.55

 

 

 

 

 

= Figura 5

= Comportamiento DQO de entrada y salida de PTAR.=

Figura 6

Comportamiento DQO de entrada y salida de Biodigestores

Del análisis del DQO de PTAR hemos obtenido el comportamiento para determinar su porcentaje de efectividad en el tratamien= to de aguas residuales domesticas de la siguiente manera (tabla 5).=

Tabla 5

Porcentaje de efectividad DQO PTAR

Sistema

DQO de entrada

DQO de salida

Diferencia=

%

Achayacu

335.68

154.75

180.93

53.90

Cementerio

786.29

251.5

534.79

68.01

Escaleras

1023.11

322.11

701

68.52

Laureles

937.11

274.26

662.85

70.73

Octavio

212.22

42.17

170.05

80.13

Quillopungo

612.54

188.31

424.23

69.26

Quingeo

1016.34

84.28

932.06

91.71

Tutupali

1484.88

156.29

1328.59

89.47

San Pedro

616.93

147.57

469.36

76.08

Bella Unión

850.92

205.92

645

75.80

Tarqui

1221.44

304.61

916.83

75.06

Macas

252.22

67.53

184.69

73.23

Guabo

1334.03

170.32

1163.71

87.23

Churuguzo

647.75

187.27

460.48

71.09

De la misma manera con el análisis del DQO de Biodigestores obtenemos el comportamiento para determinar su porcentaje de efectividad en el tratamiento de aguas residuales domesticas de la siguiente manera (Tabla 6).

Tabla 6

Porcentaje de efectividad DQO Biodigestor

Sistema

DQO de entrada

DQO de salida

Diferencia

%

BIODIGESTOR 1

350.33

80.33

270

77.07

BIODIGESTOR 2

378

90.3

287.7

76.11

BIODIGESTOR 3

380.23

102.22

278.01

73.12

BIODIGESTOR 4

279.11

89.22

189.89

68.03

BIODIGESTOR 5

313.33

55.55

257.78

82.27

Figura 7

Porcentaje de efectividad SST PTAR.<= /b>

 

 

Figura 8

Comportamiento SST de entrada y salida de Biodigestores

Del análisis de SST de PTAR hemos obtenido el comportamiento para determinar su porcentaje de efectividad en el tratamien= to de aguas residuales domesticas de la siguiente manera (Tabla 7).=

Tabla 7

Porcentaje de efectividad SST PTAR

Sistema

SST Entra= da

SST Salid= a

Diferenci= a

%

Achayacu

197.94

59.07

138.87

70.16

Cementerio

504.43

53.25

451.18

89.44

Escaleras

797.56

28.33

769.23

96.45

Laureles

318.04

39.73

278.31

87.51

Octavio

100.33

7.33

93

92.69

Quillopungo

743.56

31.84

711.72

95.72

Quingeo

1856

15.1

1840.9

99.19

Tutupali

1283.28

58.15

1225.13

95.47

San Pedro

338.46

29.69

308.77

91.23

Bella Unión

491.83

24

467.83

95.12

Tarqui

846.59

116.12

730.47

86.28

Macas

121.21

33.71

87.5

72.19

Guabo

1485.23

31.97

1453.26

97.85

Churuguzo

941.08

56.04

885.04

94.05

De la misma manera con el análisis de SST de Biodi= gestores obtenemos el comportamiento para determinar su porcentaje de efectividad en= el tratamiento de aguas residuales domesticas de la siguiente manera (Tabla 8)= .

Tabla 8

Porcentaje de efectividad SST Biodigestor

Sistema

SST Entra= da

SST Salid= a

Diferenci= a

%

 

 

BIODIGEST= OR 1

303.3

30.12

273.18

90.07

 

BIODIGEST= OR 2

289.33

33.41

255.92

88.45

 

BIODIGEST= OR 3

279.12

35.42

243.7

87.31

 

BIODIGEST= OR 4

180.22

44.12

136.1

75.52

 

BIODIGESTOR 5

215.23

30.44

184.79

85.86

 

Discusión

Con el análisis de los parámetros de calidad de ag= ua tanto de entrada como de salida podemos observar gráfica y matemáticamente = que las tendencias en los tres parámetros analizados de DQO, DBO y Solidos Suspendidos Totales con respecto al agua que ingresa, versus a la que sale luego de su tratamiento, tiene una tendencia a la baja de sus valores tenie= ndo la siguiente efectividad para Plantas de Tratamiento de Aguas Residuales DBO 80.96% de efectividad, DQO 75.1% de efectividad y SST 90.23% de efectividad, mientras que en Biodigestores tenemos la siguiente efectividad DBO 84.16% de efectividad, DQO 75.32% de efectividad y SST 85.44% de efectividad.

Conclusiones

·&nb= sp;        Con el análisis de la efectividad de cada uno de l= os parámetros y en distintas condiciones tanto climáticas como territoriales y al tener resultados que no varían con más del 5% podemos decir que los dos sistemas cumplen su objetivo primordial que es dar un tratamiento primario a las agu= as residuales domesticas antes de ser depositadas en un receptor final para así evitar la contaminación y mejorar las condiciones de vida de sus habitantes= .

·&nb= sp;        En un ámbito socio-económico se considerar varios aspectos como el tipo de suelo, número de habitantes, vías de acceso y presupuestos, sin embargo, existen otros factores que son imprescindibles t= omar en cuenta, como el caso del 1) el área disponible para la implantación, 2) = el presupuesto referencial, que para un Biodigestor es menor al de una PTAR, 3= ) el mantenimiento, en el caso de PTAR  = debe ser realizado con equipos especiales, mientras que el Biodigestor posee un sistema de autolimpieza, y 4) el número de usuarios para cada sistema, en c= aso de los Biodigestores existe límite de usuarios para un adecuado funcionamie= nto.

·&nb= sp;        Es necesario implementar un catastro general de es= tas unidades de tratamiento de manera tal que se pueda clasificar su uso según = el tipo de suelo del sector.

·&nb= sp;        Además, es indispensable el mantenimiento de las P= TAR mínimo cada 6 meses, puesto a que al no realizarlo estas pueden fracasar y = no cumplir su objetivo, lo que puede provocar malestares a la población.<= /o:p>

·&nb= sp;        Por otro lado, es conveniente considera que el uso= de PTAR y Biodigestores, al ser un tratamiento primario; lo óptimo seria contar con tratamiento posterior como los humedales.

 

Agradecimientos

El presente artículo es parte del trabajo de investigación y titulación del Programa de Maestría en Construcción con Mención en Administración de la Construcción Sustentable de la Universidad Católica de Cuenca, por ello agradecemos a todos y cada uno de los instructores pertenecientes a los gru= pos de investigación;  Ciudad, Ambiente= y Tecnología (CAT), y  Sistemas embeb= idos y visión artificial en ciencias, Arquitectónicas, Agropecuarias, Ambientales y Automática (SEVA4CA), por los conocimientos e información brindados para la elaboración del trabajo.

Referencias Bibliográficas

Alarcón, Y., y Carrasco, M. (2021). Tratamientos de aguas residuales mediante biodigestor para el recinto matecito, cantón Vinc= es, provincia de los Ríos.

Analítica Avanzada Asesoría y Laboratorios Cía. Lt= da. (2021).  Promedios Anuales de Biodigestores.

Cajigas, Á. (1995). Ingeniería de aguas residua= les (3.a ed.).

Empresa de Telecomunicaciones, Agua Potable, Alcantarillado y saneamiento de Cuenca.   =      (2021). Datos de Plantas = de Tratamiento de Aguas Residuales en la ciudad de Cuenca.

Gijón, Y., Quintal, F., Rodríguez, O., & Ménde= z, N. (2007). Determinación de la tasa de acumulación de lodos en fosas séptic= as de la ciudad de Mérida, Yucatán. Ingeniería, 11(3), 55-64.

González, J., González, A., & González, F. (20= 20). Evaluación de un sistema de filtración lenta en arena como alternativa p= ara la remoción de contaminación bacteriológica en aguas residuales de efluentes secundarios Anaerobio.

Guamán, V., & Molina, M. (2015). Evaluación= de las plantas de depuración de agua residual de las comunidades de Macas y San Pedro, cantón Cuenca, Azuay. https://dspace.ucuenca.edu.ec/bitstream/123456789/21662/1/TESIS.pdf

Jaimovich, O., Acevedo, F., Badell, N., Cerdá, A., Hardoy, E., & Vallarino, J. (1901). Tratamientos de residuos cloacales = con Biodigestores, (1).

López, J. L. y. (2014). Fosas Sépticas. Anales = del Instituto de Ingenieros de Chile, 295-310. https://revistas.uchile.cl/index.php/AICH/article/view/34514/36222

Ministerio del Medio Ambiente. (2011). Norma de Calidad Ambiental y de descarga de efluentes: Recurso Agua. TULAS Te= xto unificado de legislación secundaria del Ministerio del Ambiente.

Muñoz, A. (2008). Caracterización y tratamiento de aguas residuales. Instituto de Ciencias Básicas e Ingeniería, 305. http://cvonline.uaeh.edu.mx/Cursos/Especialidad/Modulo1_PDF/Gen12/ESTEM01T0= 1E08.pdf

Muñoz, I., & Orellana, C. (2019). Caracteri= zación de lodos de fosas sépticas de las plantas de tratamiento rurales del cantón Cuenca.

Peralta, W. M. (2021). Sistema de tratamiento de a= guas residuales domiciliarias con biodigestores para la comunidad El Ramito, Parroquia La Unión Del Cantón Jipijapa.

PROCON. (2018). Ficha técnica de biodigestor autol= impiadle. http://www.proconsrl.com/pdfs/3.pdf

Rosales-Escalante, E.  (2005). Tanques sépticos. Conceptos teóricos base y aplicaciones. Tanques sépticos. Conceptos teóricos base y aplicaciones, 18(2), 26-33.<= o:p>

Valdez, E., & Vázquez, A. (2003). Ingeniería de los sistemas de tratamiento y disposición de aguas residuales. Fundación= Ica, 341. http://siar.minam.gob.pe/puno/sites/default/files/archivos/public/docs/inge= nieria_de_los_sistemas_de_tratamiento_y_disposicion_de_aguas_residuales_civ= ilgeeks.pdf

 

 

 

El artículo que se publica es de exclusiva responsabilidad de los autores y no necesariamente reflejan el pensamiento de la Revista Alfa Publicaciones.

 


El artíc= ulo queda en propiedad de la revista y, por tanto, su publicación parcial y/o t= otal en otro medio tiene que ser autorizado por el director de la Revista Alfa Publicaciones.<= /o:p>

&nb= sp;

 

 

 


&nb= sp;

 

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= ISSN: 2773-7330

= Vol. 4 No. 2.1.  pp. 6 – 24. abril 2022

 

 

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