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Recibido: 30-06-2021 / Revisado: 09-07-2021 / Aceptado: 28-07-2021 / Publicado: 05-08-2021

 

Evaluación de la capacidad de reacción de coliformes de aguas residuales a la fotocatálisis = con técnicas de recubrimiento por inmersión DOI: https://doi.org/10.33262/ap= .v3i3.1.102

 

Evaluat= ion of the reaction capacity of wastewater coliforms to photocatalysis with dip coating techniques

 

Sofía Carolina Godoy Ponce, [1] Juan Carlos González García. [2], José Gerardo León Chimbolema. [3] & Erika Daniela Castillo Hidalgo. = [4]

 

Abstract                     =            

=
Intro=
duction: The =
presence of fecal and total coliforms in wastewater are indicators of water=
 quality and the degree of exposure and impact of human activities on it. O=
bjective: Apply photocatalysis processes with sunlight and the Dip - Coatin=
g method for the reduction of coliforms in wastewater. Objec=
tive: App=
ly photocatalysis processes with sunlight and the Dip - Coating method for =
the reduction of coliforms in wastewater. Methodology: The process i=
ncluded perpendicular immersion and subsequent extraction of the substrate =
at a controlled speed in a solution prepared for the formation of the Titan=
ium Dioxide film, drainage in the same equipment, evaporation and drying kn=
own as the DIP_coating method together with the solar disinfecti=
on of the water (SODIS) that used solar energy to destroy pathogenic microo=
rganisms that cause water-borne diseases, relating UV-A radiation, which ha=
d a germicidal effect, and infrared radiation, responsible for raising the =
temperature of the water. The combined use of UV-A radiation and heat produ=
ced a synergistic effect that increased the efficiency of the process. Four=
 experimental units were used: two were applied by the SODIS method and the=
 other two applied SODIS with TIO2 in the Dip-coating method. The residual =
water samples were placed in PET plastic bottles prepared in three solution=
s (10-1, 10-2 and 10-3), performing the mi=
crobiological analysis_quantification of coliforms in Compact Dry E=
C plates incubated for 24 hours at 35 ° C. Results: A significant re=
duction was evidenced, especially in the 10-3 dilution, accounti=
ng for the case of fecal coliforms in the SODIS method: 3900 MPN / 100ml an=
d DIP-COATING: 100 MPN / 100ml; and for total coliforms in SODIS: 12500 NMP=
 / 100ml and DIP-COATING: 1100 NMP / 100ml, at optimal treatment conditions=
 of 180 min at 42 ° C. Conclusions: the exposed conditions and suitable cli=
matic conditions give the maximum reduction effect by combining the two SOD=
IS / DIP-Coating methodologies where the photocatalysis process with sunlig=
ht microbiologically improved the water quality where titanium dioxide was =
a low-cost semiconductor , easy accessibility, low toxicity, resistance to =
photo corrosion and catalytic efficiency
Keywords: Sodis, Dip-coating, fecal and tota=
l coliforms, waste water

Resumen.

Introducción: La presencia de coliformes fecales y totales en aguas residuales constituyen indicadores de la calidad= del agua y del grado de exposición e impacto de las actividades humanas en ella= . Objetivo: Aplicar procesos de fotocatálisis con luz solar y el método Dip - Coating para la reducción de coliformes de ag= uas residuales. Metodología: El proceso incluyó la inmersi= ón perpendicular y posterior extracción del sustrato a velocidad controlada en= una solución preparada para la formación de la película de Dióxido de Titanio, drenaje en el mismo equipo, evaporación y secado conocido como método DIP_coating conjuntamente con la desinfección solar d= el agua (SODIS) que usó la energía solar para destruir los microorganismos patógenos que causan enfermedades transmitidas por el agua, relacionando  la radiación UV-A, que tuvo efecto germ= icida y la radiación infrarroja, encargada de elevar la temperatura del agua. El = uso combinado de la radiación UV-A y del calor produjo un efecto de sinergia que incrementó la eficacia del proceso. Se trabajaron cuatro unidades experimentales: dos fueron aplicadas por el método SODIS y las otras dos aplicaron SODIS con TIO2 en el método Dip-c= oating. Las muestras de agua residual fueron dispuestas en botellas de plástico PET preparadas en tres disoluciones (10-1, 10-2 y 10= -3) realizándose el análisis microbiológico_cuantificación= de coliformes en placas Compact Dry EC incubada= s 24 horas a 35°C. Resultados: Se evidenció una reducción significativa, sobre todo en la dilución 10-3, llegando a contabilizar para el = caso de coliformes fecales en el método SODIS: 3900 NMP/100ml y DIP-COATING: 100 NMP/100ml; y para coliformes totales en SODIS: 12500 NMP/100ml y DIP-COATIN= G: 1100 NMP/100ml, a condiciones óptimas de tratamiento de 180 min a 42°C. = Conclusiones: las condiciones expuestas y condiciones climáticas adecuadas se da el efect= o de reducción máxima combinando las dos metodologías SODIS/DIP-Coating donde el proceso de fotocatálisis con luz solar mejoró microbiológicamente = la calidad del agua donde el dióxido de titanio fue un semiconductor de bajo costo, fácil accesibilidad, baja toxicidad, resistencia a la foto corrosión y  eficiencia catalítica.  

P= alabras claves: Sodis, Dip-coating, coliformes fecales y totales, agua residual

 

Intro= ducción

En la actualidad, el cuidado y la protección de los cuerpos de agua dul= ce se ha convertido en una tarea de primera línea en la agenda de países y organismos multilaterales como las Naciones Unidas (ONU), por ser una problemática que está directamente relacionada con el desarrollo y la salud humana (Restrepo et al., 2008). A partir del = siglo XX la interacción de la materia con la luz se realiza desde el punto de vis= ta microscópico, considerándola como un proceso de absorción de un fotón que conlleva la creación de un par electrón-hueco o la emisión o destrucción de= un fotón creando excitaciones. La materia puede interactuar con la luz en un amplio rango de longitudes de onda y con diversos cambios en la estructura = de las moléculas (Chen, 2004).

Ante esta grave crisis del agua a nivel global, hace tiempo que se plan= tea una gestión ecosistémica del agua, siguiendo los principios del desarrollo sostenible. Ello quiere decir que los recursos hídricos son limitados y que= no se pueden mantener sin la conservación de los ecosistemas acuáticos en buen estado, de manera que se haga una gestión eficaz basada en el ahorro, el reuso y la no contaminación del agua, todo ello en una planificación sostenible del territorio y una gestión integrada de las cuen= cas hidrográficas (Morató et al., 2006).

Hoy día existen tecnologías para el tratamiento de aguas residuales, las cuales dependen en gran medida del tipo de efluente, así como del grado de = tratamiento requerido para su reutilización (Nieto, 2011). En la mayoría de los casos se emplean tratamientos convencionales, los cuales incluyen diversas etapas de separación físicas, como cribado, desarenado, sedimentación, separación de grasas y aceites, seguidos de proceso con o sin aireación, para finalmente = ser sometidas a etapas de desinfección, como cloración, oz= onación o UV. En los últimos ańos se han desarrollado opciones que proyectan una al= ta viabilidad en su aplicación, como oxidación química (O3, O3= /H2O2, H2O2/Fe+2), fotocatálisis (TiO2= /UV, foto-Fenton), degradación fotoquímica (O3/UV, O3/H2O2), o bien la combinación de éstos (electro-Fenton; fotoel= ectro-Fenton, electrocoagulación/O3 (Rivera, 2016)

Se han desarrollado muchas técnicas para inmovilizar catalizadores de TiO2 sobre un sustrato sólido, por ejemplo, revestimiento por inmersión de suspensión, revestimien= to por pulverización, pulverización catódica, métodos relacionados con sol-gel= y deposición electroforética. Además, se han probado diferentes tipos de sustratos; por ejemplo, perlas de vidrio, tubos de vidrio, fibra de vidrio, cuarzo, acero inoxidable, aluminio, carbón activado y sílice (Hosseini, 200= 7).

El proceso de fotocatálisis c= on luz solar es una tecnología simple empleada para mejorar la calidad del agu= a y disminuir su carga microbiana (Awag, 2002). La inactivación de microorganismos se debe a la acción de la radiación ultravioleta emitida por la energía solar que sumado al proceso Dip-coating (con Dióxido de Titanio) reducen el tiemp= o de exposición solar para un tratamiento más efectivo, considerando que el Dióx= ido de titanio es el semiconductor más frecuente usado en fotocatálisis por su = bajo costo, fácil accesibilidad, baja toxicidad, resistencia a la fotocorrosión y a su eficiencia catalítica (Castillo, 2017). La destrucción de los contaminantes mediante el empleo de esta técni= ca tiene por objeto la formación de radicales hidroxilo que posteriormente tienen un efecto oxidante sobre los contaminantes químicos (Garc= és et al., 2004).

Las investigaciones en fotocatálisis incrementaron exponencialmente desde 1972 con el descubrimien= to de la hidrólisis electroquímica fotoasistida de= l agua con un monocristal de Dióxido de titanio como electrodo de trabajo y un contraelectrodo de platino, bajo la aplicación de un potencial químico o electroquímico (Nevá= rez et al., 2012). En este proceso la oxidación tiene lugar directamente en la superficie de la partícula que se utiliza como catalizador o semiconductor (Dióxido de titan= io, entre otros), siendo la radiación solar la única fuente de energía (Bandala= et al., 2007). La fotocatálisis heterogénea mediada por Dióxido de Titanio y la foto oxidación mediada por compuestos férricos son dos alternativas atracti= vas para el tratamiento de aguas (Chen, 2004)

La ubicación del Ecuador en el planeta lo categoriza como un país de privilegio científico respecto al emp= leo de radiación solar para este tipo de estudios pues la incidencia de radiaci= ón solar es perpendicular a nuestra superficie durante todo el ańo. En el Ecua= dor la recepción de radiación solar varía dentro del territorio nacional únicam= ente por condiciones climatológicas locales y que varían de acuerdo a la cercaní= a o lejanía del sol (Díaz, 2012). En este sentido, la gestión del recurso hídri= co se convierte en un mecanismo clave para garantizar que el recurso esté disponible en cantidad y calidad para todos los usuarios que dinamizan su existencia (Delgado, 2017)

Algunos estudios han establec= ido que una fina capa de dióxido de titanio presenta buena respuesta fotocatalítica, por lo que no es necesario aplicar va= rios ciclos de inmersión. Adicionalmente establecieron que las películas obtenid= as por la técnica Dip-Coating no se desactivan des= pués de la primera inmersión y el posterior lavado(Ri= vera, 2016). La capa final de dióxido de titanio suele medirse mediante el peso de dicha capa, obtenido a través de una diferencia de pesos entre el peso inic= ial y final del proceso de impregnación = (Acevedo, 2015)

= Desarrollo= metodológico:

Se trabajó con cuatro unidades experimentales: dos fueron aplicadas por el método SODIS y las otras dos aplicaron SODIS con Dióxido de Titanio en el método DIP-Coating. Todas las unidades de estudio fueron sometidas a condiciones iguales de temperatura para determinar la efectividad de cada proceso, cada unidad experimental contó con 4 litros de agua residual distribuidos en 1 litro por unidad experimental. Para la recolección de datos se consideraron dentro de análisis de laboratorio a los parámetros microbiológicos de aguas residuale= s: coliformes totales, coliformes fecales (Castillo,2017).

1.      Proceso de fotocatálisis (SODIS):

Se verificaron las condiciones climáticas adecuadas para realizar la prueba SODIS, para su aplicabilidad se emplearon dos botellas de plástico PET de 1 litro con el agua residual y se consideraron dos puntos de muestras provenientes del agua residual de la parroquia Ulba del cantón Bańos de Agua Santa-Ecuador.  Una vez selladas las botellas, estas fueron expuestas al sol por 180 minutos hasta los 42şC dura= nte 12 días consecutivos bajo el esquema expuesto a continuación:

Tabla= 1

Consi= deraciones para la prueba SODIS

IDENTIFICACIÓN

&nbs= p;

SODIS

TIPO DE COLIFORMES

TIEMPO (min)

TEMPERATURA (°C)<= /o:p>

LÍMITE MÁXIMO NMP/100ml

P1 NMP/100ml=

P2 NMP/100ml=

Fuente: Cas= tillo, (2017)

De la Tabla 1 se denota que P= 1 y P2 representan la carga microbiana presente en los dos puntos de muestreo d= el agua residual (NMP/100 ml). Se realizó el conteo de coliformes fecales y totales en Placas Compact Dry EC.

2.      Procedimiento combinado SODIS con Dip – = Coating

2.1    Inmovilizaci= ón del Dióxido de Titanio en varillas de vidrio:

Para la preparación de las varillas de vidrio se pesaron 22 varillas de vidrio de boro silicato de 6 mm para proceder a su raspado y lavado con la finalidad de incrementar la rugosidad de su superficie, dejándolas secar a 70°C durante 2 horas para finalmente ser pesadas.  

Para la preparación de la solución de dióxido de titanio se preparó 100 ml de una solución de Dióxido= de titanio con agua desmineralizada al 5% dispuesta en bańo ultrasónico por 30= minutos.

 La disposición del dióxido de titanio en= las varillas de vidrio fue en una capa uniforme de dióxido de titanio, con la a= yuda de una bureta de 25 ml sumergidas cada una de ellas en la solución preparada dejándolas secar a 35°C por 2 horas y repitiendo este proceso hasta por 12 veces para lograr el espesor de la capa del catalizador adecuado.

El recubrimiento obtenido en = las varillas fue calcinado en un horno a 300 °C durante 4 horas.  Al finalizar con la inmovilización del Dióxido de titanio en las varillas de vidrio mediante = Dip-Coating se procedió a tomar el peso final de cada una de estas.

2.2     Desinfección por radiación solar:

Las muestras de agua residual para este método fueron dispuestas en dos botellas de plástico PET selladas= y agitadas durante 1 minuto.

Cinco varillas de vidrio de b= oro silicato de 6 mm inmovilizadas previamente con Dióxido de titanio se introdujeron en cada uno de los envases exponiéndolas en reposo a radiación UV-A (luz solar) por un lapso promedio de 60 minutos. Posterior a este tiem= po los envases se agitaron durante 20 segundos para obtener una muestra de cada una de ellas para realizar en ellas sus correspondientes análisis físicos químicos y microbiológicos (Castillo,2017)..

2.3    Reducción de coliformes de aguas residuales:

Para la determinación, cuantificación y diferenciación de coliformes se empleó un procedimiento se= guro con placas Compact Dry EC compuestas por dos sustratos enzimáticos cromógenos que son: Magenta-GAL y X-Gluc.

 Para cada uno de los envases PET utiliza= dos tanto en el método SODIS y SODIS/Dip coating se prepararon 3 disoluciones (10-1= , 10-2 y 10-3) con agua de peptona en tubos de ensayo que fueron homogenizados y de los cuales se extrajeron 1ml de muestra para el análisis microbiológico en la cuantificación de coliformes totales y fecales incubad= as 24 horas a 35°C (Castillo,2017)..

Para el análisis estadístico = se realizó la prueba de Kruskal - Wallis para conocer el proceso fotocatalítico con mayor nivel de reducción de colifo= rmes de las aguas residuales.

Análisis de los resultados:

1.      Proceso de fotocatálisis (SODIS):

En la presente tabla se encuentran representados los valores adquiridos de coliformes fecales y tot= ales de cada una de las muestras después de ser expuestos a la radiación solar en intervalos de tiempo:

Tabla2

Resultados de la prueba SODIS al 1 día de tratamiento=

IDENTIFICACIÓN

 

SODIS

TIPO DE COLIFORMES

TIEMPO (min)

TEMPERATURA (°C)<= /o:p>

LÍMITE MÁXIMO <= /b>NMP/100ml=

P1 NMP/100ml=

P2 NMP/100ml=

Fecales

0

 

2000

24000

24000

Totales

0

18,1

N/E

20850

19220

Fecales

 

 

2000

19200

19450

Totales

60

26

N/E

19800

18635

Fecales

120

30

2000

18150

18350

 

Tabla2

Resultados de la prueba SODIS al 1 día de tratamiento= (continuación)

IDENTIFICACIÓN<= /b>

SODIS

TIPO DE COLIFORMES

TIEMPO (min)

TEMPERATURA (°C)

LÍMITE MÁXIMO <= /b>NMP/100ml=

P1 NMP/100ml=

P2 NMP/100ml=

Totales

120

30

N/E

18750

15812

Fecales

&nbs= p;

180

&nbs= p;

42

2000

17100

17200

Totales

N/E

17700

13000

Fuente: (Cas= tillo, 2017).

Al someter las muestras a la radiación solar se obtuvo un resultado favorable a 180 minutos y 42 °C, el = cual nos indica que en el punto 1 hubo 17100 NMP/100 ml de coliformes fecales y 17700 de coliformes totales NMP/100 ml; en el punto 2 hubo 17200 NMP/100 ml= de coliformes fecales y 13000 de coliformes totales NMP/100 ml.

Figura 1

Número de coliformes reducidas mediante SODIS

 

<= /o:p>

Fuente: Castillo, (2017)

En la tabla 3 se encuentran representados los resultados obtenidos al realizar un análisis para identif= icar el número de coliformes fecales y totales presentes en las muestras del pun= to 1 y del punto 2 después de haber transcurrido 12 días de la aplicación del proceso fotocatalítico SODIS.=

Tabla3

Resultados para la prueba SODIS a los 12 días de tratamiento

IDENTIFICACIÓN

 

LÍMITE MÁXIMO NMP/100ml

SODIS

TIPO DE COLIFORMES

TIEMPO (días)

P1 NMP/100ml

P2 NMP/100ml

Fecales

12

2000

7000

2000

Totales

12

N/E

14000<= /p>

11700<= /p>

Fuente: (Castillo, 2017).

 Al haber transcurrido un período de 12 días se tuvo u= na menor cantidad de coliformes fecales y coliformes totales, lo que indica qu= e al transcurrir el tiempo el proceso SODIS es más efectivo.

Figura 2

Número de coliformes reducidas mediante SODIS a los 12 días de tratamiento

 

Fuente: Castillo, (2017)

A continuación, se muestra la identificación del número de coliformes en las placas Compact Dry EC para SODIS

Figura 3

 Identificación de coliformes SODIS

Fuente: Castillo, (2017)

En la ilustración 1 se pueden diferenciar a las coliformes fecales que poseen coloración azul y a colifor= mes totales color rojo; en la imagen 1 perteneciente al punto 1 de muestreo se pudieron observar coliformes fecales y totales aproximadamente en las mismas proporciones, en el punto 2 de muestreo (imagen 2) se pudo observar mayor cantidad coliformes fecales que de coliformes totales (Castillo,2017). 

Al transcurrir 12 días, en el punto 1 (imagen 3) y en el punto 2 (imagen 4), se encontraron una reducción significativa de coliformes fecales y en menor cantidad coliformes totales; esto producto de las condiciones climáticas y la ubicación en la que se encontraban las muestras (Castillo,2017).

2.      Proceso de fotocatálisis (SODIS) con DIP- coating:

En la tabla 4 se encuentran representados los valores adquiridos en cada repetición aplicada para inmovilizar Dióxido de titanio (gramos /varilla) en 22 varillas de Boro silicato mediante el método Dip-Coating con doce repeticiones después de dos horas de actuación

Tabla 4

Inmovilización del dióxido de titanio en las varillas= de vidrio

de Varilla

Pi (g)

R1 (g)

R2 (g)

R3 (g)

R4 (g)

R5 (g)

R6 (g)

R7 (g)

R8 (g)

R9 (g)

R10 (g)

R11 (g)

R12 (g)

1

= 12,52

= 12,50

= 12,48

= 12,50

= 12,52

= 12,50

= 12,52

= 12,52

= 12,52

= 12,52

= 12,56

= 12,52

= 12,54

2

= 12,54

= 12,54

= 12,56

= 12,58

= 12,60

= 12,62

= 12,66

= 12,64

= 12,64

= 12,64

= 12,64

= 12,62

= 12,62

3

= 12,62

= 12,60

= 12,60

= 12,60

= 12,60

= 12,60

= 12,62

= 12,60

= 12,60

= 12,62

= 12,64

= 12,58

= 12,64

4

= 12,64

= 12,62

= 12,62

= 12,64

= 12,62

= 12,60

= 12,64

= 12,62

= 12,62

= 12,64

= 12,64

= 12,62

= 12,66

5

= 12,64

= 12,64

= 12,66

= 12,68

= 12,64

= 12,64

= 12,66

= 12,64

= 12,64

= 12,66

= 12,66

= 12,62

= 12,66

6

= 12,70

= 12,70

= 12,70

= 12,70

= 12,70

= 12,70

= 12,72

= 12,70

= 12,68

= 12,72

= 12,72

= 12,66

= 12,72

7

= 12,70

= 12,70

= 12,70

= 12,70

= 12,72

= 12,70

= 12,72

= 12,70

= 12,72

= 12,74

= 12,70

= 12,70

= 12,72

8

= 12,72

= 12,72

= 12,70

= 12,72

= 12,72

= 12,72

= 12,74

= 12,72

= 12,74

= 12,74

= 12,72

= 12,72

= 12,74

9

= 12,72

= 12,74

= 12,74

= 12,76

= 12,74

= 12,74

= 12,74

= 12,74

= 12,74

= 12,76

= 12,74

= 12,72

= 12,74

10

= 12,78

= 12,80

= 12,78

= 12,78

= 12,78

= 12,78

= 12,78

= 12,78

= 12,76

= 12,80

= 12,78

= 12,76

= 12,80

11

= 12,80

= 12,80

= 12,80

= 12,78

= 12,80

= 12,80

= 12,80

= 12,80

= 12,78

= 12,82

= 12,82

= 12,78

= 12,82

12

= 12,80

= 12,80

= 12,80

= 12,80

= 12,80

= 12,80

= 12,82

= 12,80

= 12,80

= 12,82

= 12,84

= 12,78

= 12,82

13

= 12,82

= 12,84

= 12,84

= 12,84

= 12,84

= 12,82

= 12,84

= 12,84

= 12,82

= 12,86

= 12,84

= 12,80

= 12,84

14

= 12,84

= 12,84

= 12,84

= 12,84

= 12,84

= 12,82

= 12,86

= 12,84

= 12,82

= 12,86

= 12,84

= 12,82

= 12,86

15

= 12,84

= 12,84

= 12,84

= 12,84

= 12,84

= 12,84

= 12,86

= 12,84

= 12,86

= 12,86

= 12,86

= 12,84

= 12,86

16

= 12,84

= 12,84

= 12,84

= 12,84

= 12,84

= 12,86

= 12,86

= 12,84

= 12,86

= 12,86

= 12,86

= 12,86

= 12,88

17

= 12,88

= 12,88

= 12,90

= 12,92

= 12,94

= 12,96

= 12,98

= 12,98

= 12,98

= 13,00

= 12,98

= 13,00

= 12,90

18

= 12,90

= 12,90

= 12,92

= 12,90

= 12,90

= 12,90

= 12,92

= 12,90

= 12,90

= 12,92

= 12,90

= 12,86

= 12,92

19

= 13,00

= 13,00

= 13,02

= 13,02

= 13,02

= 13,00

= 13,02

= 13,02

= 13,00

= 12,98

= 13,04

= 13,02

= 13,02

20

= 13,02

= 13,02

= 13,04

= 13,04

= 13,04

= 13,00

= 13,04

= 13,02

= 13,00

= 13,04

= 13,04

= 13,02

= 13,04

21

= 13,08

= 13,06

= 13,08

= 13,08

= 13,08

= 13,06

= 13,08

= 13,08

= 13,08

= 13,10

= 13,08

= 13,04

= 13,10

22

= 13,08

= 13,10

= 13,10

= 13,08

= 13,10

= 13,10

= 13,10

= 13,10

= 13,12

= 13,10

= 13,10

= 13,10

= 13,12

Fuente: Castillo, (2017)

La variación de los pesos en = las varillas fue consecuencia de aspectos como su origen, varillas sometidas a = un proceso de secado en horno (35 °C) y del lavado con agua destilada, ocasion= ando que partículas de Dióxido de titanio se vayan adhiriendo en proporciones distintas en cada una de ellas. Sin embargo, estos resultados no variaron significativamente (Castillo,2017).

Tabla 5=

Peso final de las varillas de vidrio con dióxido de titanio inmovilizado en ellas

 

de Varilla=

Peso de la varilla con rugosidad (g)=

Longitud de la varilla (cm)

Diámetro de la varilla (mm)

Peso de TiO2 en g

Peso final de la varilla (g)

1

12,52

20

6

0,02

12,54

2

12,54

20

6

0,08

12,62

3

12,62

20

6

0,02

12,64

4

12,64

20

6

0,02

12,66

5

12,64

20

6

0,02

12,66

6

12,70

20

6

0,02

12,72

7

12,70

20

6

0,02

12,72

8

12,72

20

6

0,02

12,74

9

12,72

20

6

0,02

12,74

10

12,78

20

6

0,02

12,80

11

12,80

20

6

0,02

12,82

12

12,80

20

6

0,02

12,82

13

12,82

20

6

0,02

12,84

14

12,84

20

6

0,02

12,86

15

12,84

20

6

0,02

12,86

16

12,84

20

6

0,04

12,88

17

12,88

20

6

0,02

12,90

18

12,90

20

6

0,02

12,92

19

13,00

20

6

0,02

13,02

20

13,02

20

6

0,02

13,04

21

13,08

20

6

0,02

13,10

22

13,08

20

6

0,04

13,12

Fuente: Cas= tillo, (2017)

La relación del peso adherido= se basa en una adhesión de 0,04 gramos en la varilla número 22 y número 16 con= un resultado sobresaliente en la varilla número 2 en la que la adhesión fue de 0.08 gramos (Castillo,2017)

De las 22 varillas sometidas = al tratamiento se tomaron 10 varillas al azar cuyo peso de adhesión fue de 0,02 gramos. Las varillas inmovilizadas con dióxido de titanio generalmente mantuvieron el mismo peso, no existió pérdida del reactivo (Castillo,2017).=

 <= /p>

 <= /p>

 <= /p>

 <= /p>

Tabla 6=

Varillas de vidrio con dióxid= o de titanio seleccionadas al azar, de acuerdo al peso final adquirido para someterlas al proceso SODIS/Dip-Coating

de Varilla=

Peso final de la varilla (g).

Longitud de la varilla (cm).

Diámetro de la varilla (mm).

Peso de TiO2 (g).

Peso varilla TiO2 después= de 12 días

Punto de muestreo 1 (P1).=

 

1

12,7481<= o:p>

20<= /o:p>

6

0,02

12,7482<= o:p>

2

12,7512<= o:p>

20<= /o:p>

6

0,02

12,7612<= o:p>

3

12,7623<= o:p>

20<= /o:p>

6

0,02

12,7801<= o:p>

4

12,7753<= o:p>

20<= /o:p>

6

0,02

12,8002<= o:p>

5

12,8212<= o:p>

20<= /o:p>

6

0,02

12,8213<= o:p>

Punto de muestreo 2 (P2).=

 

6

12,8404<= o:p>

20<= /o:p>

6

0,02

12,8404<= o:p>

7

12,8790<= o:p>

20<= /o:p>

6

0,02

12,8801<= o:p>

8

12,9396<= o:p>

20<= /o:p>

6

0,02

12,9400<= o:p>

9

13,1143<= o:p>

20<= /o:p>

6

0,02

13,1201<= o:p>

10<= /o:p>

13,1375<= o:p>

20<= /o:p>

6

0,02

13,1400<= o:p>

Fuente: Cas= tillo, (2017)

En la tabla 7 se encuentran representados los valores adquiridos de coliformes fecales y coliformes tot= ales presentes en cada una de las muestras después de ser expuestos a la radiaci= ón solar con intervalos de tiempo correspondiente al proceso fotocatalítico SODIS/Dip-Coating (Castillo,2017)

Tabla 7

Resultados del análisis microbiológico de SODIS/DIP- Coating=

            IDENTIFICACIÓN=

 

LÍMITE MÁXIMO<= /p>

(NMP/100 ml)

SODIS/Dip-Coati= ng

TIPO DE COLIFORMES=

TIEMPO (min)

TEMPERATURA (°C)

P1

(NMP/100 ml)

P2

 (NMP/100 ml)

Fecales

&nb= sp;

0

&nb= sp;

18,1

2000

24000

24000

Totales

N/E=

20850

19220

Fecales

&nb= sp;

60<= /o:p>

&nb= sp;

26<= /o:p>

2000

13950

13475

Totales

N/E=

17235

15470

Fecales

&nb= sp;

120=

&nb= sp;

30<= /o:p>

2000

6150

9225

Totales

N/E=

14620

13110

Fecales

&nb= sp;

180=

&nb= sp;

42<= /o:p>

2000

3900

100=

Totales

N/E=

12500

1100

Fuente: Castillo, (2017)

Al someter las muestras a la radiación solar se obtuvo un resultado favorable a 180 minutos y 42 °C, que indicó que en el punto 1 hubieron 3900 NMP/100 ml de coliformes fecales y 1= 2500 de coliformes totales NMP/100 ml; mientras que en el punto 2 hubieron 100 NMP/100 ml de coliformes fecales y 1100 de coliformes totales NMP/100 ml; d= onde esta última presentó un menor crecimiento microbiano en los rangos de temperatura y tiempo establecidos cómo se indica en la siguiente gráfica (C= astillo,2017)

Figura 4

Número de coliformes reducidas mediante SODIS/ Dip – Coat= ing

Fuente: Castillo, (2017)

Se evidenció una reducción si=
gnificativa para los dos puntos de muestreo, pero en el punto dos (P2) exis=
tió una reducción mayor de coliformes fecales y coliformes totales en compa=
ración con el punto uno (P1), esto porque las muestras fueron obtenidas de =
dos puntos distintos y por el grado de incidencia de la luz solar dentro de=
 la cual a mayor grado de incidencia de la luz solar mayor reducción de la =
carga microbiana. Esta reducción significativa se relaciona directamente co=
n la comprensión de la relación entre múltiples presiones, condiciones y se=
rvicios de los ecosistemas acuáticos que ayuda a diseńar medidas para logra=
r el objetivo del buen estado de los sistemas hídricos considerando los ben=
eficios de invertir en la conservación y restauración de la naturaleza (Grizzetti, 2016)

Figura 5

Número de coliformes mediante SODIS/ DIP - Coating después de 12 días

Fuente: Castillo, (2017)

Existió una reducción significativa en el punto uno (P1) después de 12 días de aplicado el proces= o, en cambio en el punto dos (P2) los valores se mantuvieron constantes.<= /o:p>

Figura 6

Identificación de coliformes SODIS/Dip-Coating.

1

2

3

4

Fuente: Castillo, (2017)=

En la ilustración 2 se puede diferenciar a los coliformes fecales con color azul y coliformes totales identificados por el color rojo; en la imagen 1 se puede observar una mayor cantidad de coliformes totales, en el punto 2 (imagen 2) se pudo observar la reducción de coliformes fecales con mayoritaria presencia de coliformes totales. Al transcurrir 12 días, en el punto 1 (imagen 3) se encontró una reducción significativa de coliformes fecales, en el punto 2 (imagen 4) exi= stió una reducción significativa tanto en coliformes fecales como en coliformes totales, pero destacando que la reducción principal fue en coliformes fecal= es (Castillo,2017).

Prueba de Kruskal-Wallis para SODIS/Dip-Coating. =

Tabla 8=

Rangos para Kruskal-Wallis SODIS/Dip-Coating

Rangos

 

= TIEMPO_EXPOSICIÓN

N

COL= IFORMES_SODIS_TiO2

0

4

60<= o:p>

4

Tabla 8=

Rangos para Kruskal-Wallis SODIS/Dip-Coating (continuación)

Rangos

 

= TIEMPO_EXPOSICIÓN

N

COLIFORMES_SODIS_TiO2

120=

4

180=

4

Tot= al

16

Fuente: Castillo, (2017)

En la primera columna se ubican la información de coliformes con SODIS/= Dip-Coating así como el ti= empo de exposición, en la segunda columna el número de casos válidos.

 

Tabla 9

Prueba de Kruskal-Wallis SODIS/D= ip-Coating

Estadísticos de contrastea,b

 

COLIFORMES_SODIS_TiO2

Chi= -cuadrado

12,813

gl

3

Sig= . asintót.

,005

a. Prueba de Kruskal-Wallis

b. Variable de agrupación: TIEMPO_EXPOSICIÓN

Como P=3D0,005 esto represent= ó que existen diferencias en la concentración de coliformes por efecto del tiempo= de exposición

Figura 7

Número de coliformes mediante SODIS/DIP-Coating en relación al tiempo de exposición.

Fuente: Cas= tillo, (2017)

El gráfico 5 muestra en el eje de las abscisas el tiempo de exposición expresado en minutos (min) y en el eje de las ordenadas el número de colifo= rmes reducidas expresadas en (NMP/100ml) en el cual se empleó el método SODIS/Dip-Coating para reducir coliformes de las aguas resi= duales. Las barras representan el porcentaje de reducción existente entre el número= de coliformes y el tiempo de exposición como resultado de la aplicación del mé= todo SODIS/Dip-Coating, obteniendo un resultado favo= rable a 180 minutos (Castillo,2017).

 

Conclusiones:

 

ˇ      =    De las cuatro unidades experimentales propuestas en el proceso metodológico y con base en= el número de coliformes presentes y reducidas en las aguas residuales durante = la aplicación de SODIS y SODIS/Dip-Coating las condiciones óptimas para el desarrollo del proceso fueron en el rango de 18= .1 °C a 42 °C, tiempo de exposición 180 minutos, incidencia de los rayos ultravioletas de la región A (UV-A) que es la radiación ultravioleta natural que llega a la superficie terrestre con una longitud de onda comprendida en= tre 400 y 320 nm. Dichas condiciones determinaron que el proceso fotocatalítico con luz solar más óptimo sea SODIS/Dip-Coating; donde las coliformes se redujeron más rápidamente y en mayor proporción.

ˇ      =    Se evidenció= una reducción significativa, sobre todo en la dilución 10-3, llegando a contabilizar para el caso de coliformes fecales en el P1: 3900 NMP/100ml y = P2: 100 NMP/100ml; y para coliformes totales: P1: 12500 NMP/100ml y P2: 1100 NMP/100ml, a condiciones óptimas de tratamiento de 180 min a 42°C. Dichos resultados demostraron que bajo las condiciones expuestas y condiciones climáticas adecuadas se da el efecto de reducción máxima de coliformes feca= les y totales. En cuanto al proceso de fotocatálisis con luz solar SODIS se pud= o observar una reducción menor en comparación al otro proceso aplicado, llegando a contabilizar en el P1: 17100 NMP/100ml y P2: 17200 NMP/100ml de coliformes fecales; P1: 17700 NMP/100ml y P2: 13000 NMP/100ml de coliformes totales, b= ajo las mismas condiciones expuestas. El proceso de fotocatálisis con luz solar= más adecuado para la reducción de coliformes fecales y totales de aguas residua= les es SODIS/Dip-Coating.

ˇ      =    La eficiencia del proceso SODIS/ Dip-Coating para reducir coliformes fecales y coliformes totales de las aguas residuales de estudio = fue comprobada, pero sobre todo se logró conseguir con ello el aprovechamiento = de tecnologías limpias para cumplir con el objetivo propuesto promoviendo el tratamiento terciario de las aguas residuales y así promover el aprovechami= ento de la energía solar y la aplicabilidad conjunta de tecnologías coadyuvantes para su desarrollo, en este caso de estudio se empleó el Dióxido de Titanio= que tuvo el rol de catalizador del proceso. La fotocatálisis como una tecnología simple, económica, eficaz e innovadora, para el tratamiento de aguas, el atractivo de esta tecnología radica en su rentabilidad, facilidad de implementación y uso, y la inversión requerida de capital es mínima, en comparación con otras tecnologías (Gil, 2002).

Bibliografía:

 

Gar= cés Giraldo, L. F., Mejía Franco , E. A., y Santamaría Arango, J. J. (2004). La fotocatálisis como alternativa para el tratamiento. Revista Lasallista de Investigación, 83-92.

Acevedo Dávila, A. (= 2015).  EStudio de la fotocatálisis heter= ogénea solar para tratar un efluente contaminado con productos farmacéuticos: Ibuprofeno, Diclofenaco, Sulfametoxazol Obtenido de http://bibdigital.epn.edu.ec/bitstream/15000/10366/3/CD-6165.pdf

Awag, S. (2002). SODIS (Sauberes trinkwasser für alle). Obtenido de SODIS (Sauberes trinkwasser für alle): http://www.sodis.ch/methode/anwendung/ausbildungsmaterial/dokumente_materi= al/manual_s.pdf

Castillo, E. (2017).= Procesos de fotocatálisis con luz solar y el método DIP – coating para la reducción= de coliformes de aguas residuales del barrio la ciénega con desembocadura en = el embalse Agoyán

Chen, C. (2004). Photocatalysis by Titanium Dioxide and Polyoxometalate/TiO2 Cocatalysts.Intermediates and Mechanistic Study. Enviromental Science & Technology, 329-337.

Delgado García, S. M= ., Trujillo González, J. M., y Torres Mora, M. A. (2017). Gestión del agua en comunidades rurales; caso de estudio Cuenca del río Guayuriba, Meta-Colomb= ia. Luna Azul, 59-70.

Díaz - Cuenca, E., Alvarado-Granados, A, y Camacho- Calzada, K. E. (2012). El tratamiento de = agua residual doméstica para el desarrollo local sostenible: el caso de la técn= ica delsistema unitario de tratamiento de aguas, nutrientes y energía (SUTRANE= ) en San Miguel Almaya,México. Quivera, 78-97.

Gil, Edison (2002). Fotocatálisis: una alternativa viable para la eliminación de compuestos orgánicos. Revista Universidad de EAFIT. Medellín, 59-64.

Grizzetti , B., Lanzanova , D., Liquete C, C., Reynaud , A., y Cardoso, A. (2016). = Assessing water ecosystem servic= es for water resource management. Environ Sci Policy, 194-203.

Hosseini S.N. (2007). Inmobilization of TiO2 on Perlite Granuels for Photocatalitic ELSEVIER. Degradation of Phenol. Science Direct. Applied Ca= talysis B: Environmental 74, 53-62

Morató, J., Gris, A., Carneiro, A., y Pastor, R. (2006). Tecnologías sostenibles para la potabilización y el tratamiento de aguas residuales.  Revista Lasallista de Investigación, 19-29.

Nevárez, M., Espinoz= a, P., Quiroz, F., y Ohtani, B. (2012). Fotocatálisis: inicio, actualidad y perspectivas a través del TiO2. Avances en Química, 45-49.

Nieto, N. (2011). La gestión del agua: tensiones globales y latinoamericanas. . Política y cult= ura, 157-176.

Restrepo, G. M., Río= s, L. A., & Marín , J. M. (2008). EVALUACIÓN DEL TRATAMIENTO FOTOCATALÍTI= CO DE AGUAS RESIDUALES INDUSTRIALES EMPLEANDO ENERGÍA SOLAR . Dyna, 145-153.<= o:p>

Rivera Gallardo, P. (2016). Estudio preliminar del uso de la fotoxidación y fotocatálisis como alternativa para el tratamiento de las a= guas de lavado de aceite y aceituna, utilizando TiO2 como catalizador, H2O2 como oxidante y luz UV (Tesis de pregrado, Universidad de Concepción Chile). eu= la. http://www.eula.cl/giba/wp-content/uploads/2017/09/tesis-pilar-rivera-2= 016.pdf

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

PARA CITAR EL ARTÍCULO INDEXADO.

 

 

Godoy Ponce, S. C., González García, J. C., León Chimbolema, J.= G., & Castillo Hidalgo, E. D. (2021). Evaluación de la capacidad de reacció= n de coliformes de aguas residuales a la fotocatálisis con técnicas de recubrimi= ento por inmersión . AlfaPublica= ciones, 3(3.1), 343–360. https:/= /doi.org/10.33262/ap.v3i3.1.102

 

 


 

 

 

El artículo qu= e se publica es de exclusiva responsabilidad de los autores y no necesariamente reflejan el pensamiento de la Revi= sta Alfa Publicaciones.

El artículo qu= eda en propiedad de la revista y, por tanto, su publicación parcial y/o total en otro medio tiene que ser autorizado por el director de la Revista Alfa Publicaciones.

 

                                                 =                                                                            =                       

                  =                                                                            =                                             

 



[1] Docente Investigador, Carrer= a de Ingeniería Ambiental, Facultad de Ciencias, Escuela Superior Politécnica de Chimborazo – ESPOCH. Riobamba, sofia.godoy@espoch.edu.ec ORCID: https://orc= id.org/0000-0002-6479-4343

[2] Docente Investigador, Carrer= a de Ingeniería Ambiental, Facultad de Ciencias, Escuela Superior Politécnica de Chimborazo= – ESPOCH. Riobamba, juan.gonzalez@espoch.edu.ec ORCID: https://orcid.org/0000= -0001-9066-1600

[3] Docente Investigador, Carrer= a de Ingeniería Ambiental, Facultad de Ciencias, Escuela Superior   Politécnica de Chimborazo – ESPOCH. Rio= bamba, gerardo.leon@espoch.edu.ec ORCID: https://orcid.org/0000-0001-9202-8542

[4] Investigador independiente, = latieridani@hotmail.com ORCID: https://orcid.org/0000-0002-2756-3810

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Alpha publicaciones<= o:p>

ISSN: 2773-7330                                                 =                        Vol. 3, 3.1, p. 343-360

                                                      =                                                                    agosto, 2021

 

Educación Superior                                    =                                                                        =                              Página 327

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