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Análisis fisicoquímico y bacteriológico de las piscinas de aguas termales, más concurridas, de la parroquia Baños. Cuenca – Ecuador

 Physicochemical and bacteriological analysis of = the most popular thermal pools in Baños. Cue= nca – Ecuador

 


= 1

Alexandra Estefania Anguisaca = Vega

 

https://orcid.org/0009-0006-3814-0684

 

 

Facultad de Bioquí= mica y Farmacia -Universidad Católica de Cuenca, Ecuador

= 2

Jonnathan Gerardo Ortiz Tejedo= r

 

https://orcid.org/0000-0001-6770-2144

 

 

Facultad de Bioquí= mica y Farmacia -Universidad Católica de Cuenca, Ecuador

 

 

 

 

 

 

 

Artículo de Investigación Científica y Tecnológi= ca

Enviad= o: 17/06/2023

Revisa= do: 14/07/2023

Acepta= do: 08/08/2023

Public= ado:04/09/2023   

DOI:      https://doi.org/10.33262/anatomiadigita= l.v6i3.2.2678                       <= /span>               =

 

 

&= nbsp;

Cítese:

 

&= nbsp;

Anguis= aca Vega, A. E., & Ortiz Tejedor, J. G. (2023). Análisis fisicoquímico y bacteriológico de las piscinas de aguas termales, más concurridas, de la parroquia Baños. Cuenca – Ecuador. Anatomía Digital, 6(3.2), 86-102. https://doi= .org/10.33262/anatomiadigital.v6i3.2.2678

 

 

 

ANATOMÍA DIGITAL, es una Revista Electrónica, Trimestral, que se publicará en soporte electrónico tiene como misión contribuir a la   formación de profesionales competentes con vi= sión humanística y crítica que sean capaces de exponer sus resultados investigativos y científicos en la misma medida que se promueva mediante = su intervención cambios positivos en la sociedad. https://anatomiadigital.org  

La revista es editada por la Editorial Ciencia Digital (Editorial de prestigio registrada en la Cámara Ecuatoriana de Libro con No de Afiliación 663) www.celibro.org.= ec

 

 

 

Esta revista está protegida ba= jo una licencia Creative Commons Atribución-NoComercial-CompartirIgual 4.0 International. Copia de la licencia: https://creative= commons.org/licenses/by-nc-sa/4.0/deed.es

 

Palabras claves:

Aguas Termales, Calidad del agua, Bacteriología del agua.

Bromatología.

&= nbsp;

Resumen

Intr= oducción.   En la mayoría de las aguas termales se desconoce la calidad sanitaria y microbiológica, esto ayuda al crecimient= o de ciertos microorganismos propios de estos ambientes, que han evolucionado adaptándose a condiciones extremas de estos ecosistemas. La calidad de es= tas aguas va a depender de sus propiedades fisicoquímicas como la temperatura= , pH y conductividad eléctrica. Objetivo. Analizar el estado fisicoquím= ico y bacteriológico de las piscinas de aguas termales, más concurridas, de la parroquia Baños. Cuenca – Ecuador. Metodología. El estudio fue de = tipo descriptivo, experimental de corte transversal. El universo fueron los 3 Balnearios “El Riñón”, “Hostería Durán” y “Balneario Durán”, y 1 muestra = de la vertiente, de donde se obtuvieron 16 muestras. Para el análisis fisicoquímico y bacteriológico de estos balnearios. Resultados. En= el análisis bacteriológico se identificó con un porcentaje de 77% la presenc= ia de Staphylococcus aureus, en el análisis fisicoquímico se observó = un valor promedio de pH de 7,92 en el “Balneario el Riñón” y la Vertiente, e= n la “Hostería Durán” y “Balneario Durán” un promedio de 8,43 y la temperatura= se encontraba en 35°C exceptuando la vertiente. Conclusión. Estas agu= as termales dependen de las condiciones fisicoquímicas, son aguas mesotermal= es y alcalinas, su calidad microbiológica es notablemente buenas ya que la presencia de Staphylococcus aureus no representa un riesgo para la población que acude a estos centros recreativos. Área de estudio gener= al: Bioquímica. Área de estudio específica: Bromatología. Tipo de estudio:  Artículos originales.

&= nbsp;

 

Keywords:

Thermal waters, water quality, water bacteriology.

 

Abstract

Introduction. In most thermal waters, the sanitary and microbiological quality is unknown, enabling the growth of certain microorganisms inherent to these environments, which ha= ve evolved to adapt to the extreme conditions of these ecosystems. The water quality depends on its physicochemical properties, such as temperature, p= H, and electrical conductivity. Objective. To analyze the physicochem= ical and bacteriological status of the most visited thermal pools in Baños par= ish, Cuenca - Ecuador. Methodology. The study was descriptive, experimental, and cross-sectional. The universe was the three spas, "= ;El Riñón" Spa, "Durán Inn," and “Durán" Spa, along with = one spring sample, from where 16 samples were obtained for the physicochemical and bacteriological analysis of these spas. Results. In the bacteriological analysis, Staphylococcus aureus was identified with a percentage of 77%. In the physicochemical analysis, an average pH value of 7.92 was observed at "Riñón” Spa and in the spring, an average of 8.= 43 at "Durán Inn" and "Durán" Spa. The temperature was around 35 °C, except for the spring. Conclusion. These thermal wat= ers depend on the physicochemical conditions; they are mesothermal and alkali= ne waters, and their microbiological quality is excellent since the presence= of Staphylococcus aureus does not represent a risk for individuals who visit these recreational facilities.

 

 

 

Introducción<= /b>

Las aguas termales son un recurso sumamente valioso para abordar cuestiones de salud pública, ya que estas aguas tienen efectos curativos. Su acción terapéutica, ha dado lugar = a la demanda de servicios relacionada con el turismo, como los Balnearios. Según= la hidrología médica, el termalismo activo ofrece beneficios para el tratamien= to de enfermedades del sistema respiratorio, digestivo y locomotor, estos efec= tos beneficiosos se logran a través de vías térmicas, mecánicas y transmineralizantes (1).

En la medicina tradicion= al, existe un conocimiento popular sobre las diversas propiedades curativas de = los baños termales, ya que estas aguas suelen contener diversos componentes minerales, las personas suelen visitar estos lugares con el fin de tratar a= fecciones de la piel como alergias, quemaduras, entre otros. También son frecuentes l= os tratamientos terapéuticos relacionados con problemas reumáticos, artritis, lesiones musculares e inflamaciones (2).

A pesar de sus efectos curativos es imprescindible destacar el riesgo sanitario que pueden pasar l= as personas que hacen uso de estas aguas. La calidad de las aguas termales exh= ibe una amplia variedad de microorganismos, los cuales están influenciados por = las propiedades fisicoquímicas del agua, como la temperatura, pH y la conductiv= idad eléctrica. A pesar de que el agua termal de los balnearios se considera un hábitat extremo debido a sus altas temperaturas, se ha observado la presenc= ia de una población microbiana que logra adaptarse a estas condiciones adversas (3).

La calidad de las aguas termales presenta gran diversidad de microorganismos que dependen de sus propiedades fisicoquímicas como la temperatura, pH, conductividad eléctrica. Pese a que el agua termal de los balnearios es un hábitat extremo por sus a= ltas temperaturas existe una población microbiana que se adaptan a estas condici= ones adversas, siendo de mayor interés sanitario Escherichia coli (4).

En la mayoría de aguas termales se desconoce la calidad sanitaria y microbiológica, esto ayuda al = crecimiento de ciertos microorganismos propios de estos ambientes y que han evolucionado adaptándose a las condiciones extremas de estos ecosistemas, ya que no se h= an realizado estudios sobre la calidad fisicoquímica, como es el análisis de la temperatura en las que se puede encontrar las aguas termales: entre 35 y 45= ºC, consideradas mesotermales y a una temperatura de más de 45ºC considerada hipertermal (5); el pH de estas aguas se encuentra en el rango de 6.5 y 7, y las aguas con una conductividad eléctrica superior a 1,000 mS/cm son consideradas de mineralización excesiva y no aptas para consumo (6). Los estudios bacteriológicos se asocian con los parámetros fisicoquímicos como = la temperatura y pH característicos de estas aguas ya que determinan las condi= ciones en las que las bacterias como: Escherichia coli y Coliformes Totales, crecen y se reproducen satisfactoriamente, la mayoría de las bacterias pued= en crecer en un pH entre 5,5 y 7,0. En el caso de las aguas termales, puede va= riar dependiendo de la fuente y condiciones específicas, algunas aguas termales pueden tener un pH neutro, mientras que otras pueden ser más alcalinas o ác= idas (7). La diversidad microbiana presentes en aguas termales se adapta a estas condiciones, como el Staphylococcus aureus la cual es una bacteria q= ue se encuentra en el microbiota normal de la piel y mucosas, especialmente en= la nasal (8), es capaz de crecer en un rango de pH desde 4,5 hasta pH 9,0, sobreviviendo a condiciones ácidas, neutras e incluso alcalinas, esto va a depender de la cepa específica (9).

En Ecuador, se ha presta= do poca atención al estudio de las aguas termales y no existe una normativa que establezca los requisitos microbiológicos y fisicoquímicos para su uso, cada piscina de agua termal tiene un microbiota específico en relación con sus características físicas, por lo tanto puede representar un riesgo sanitario importante para las personas que hacen uso de estas aguas.

La calidad de las aguas termales presenta gran diversidad de microorganismos que dependen de sus propiedades fisicoquímicas como la temperatura, pH y conductividad eléctric= a. Pese a que el agua termal de los balnearios es un hábitat extremo por sus a= ltas temperaturas existe una población microbiana que se adaptan a estas condici= ones adversas, siendo de mayor interés sanitario Escherichia coli, encontrando también Staphylococcus aureus, coliformes, hongos, levaduras, entre otros (10).

El presente estudio es relevante ya que no existen estudios fisicoquímicos y bacteriológicos a niv= el local, los resultados de este estudio pueden ayudar futuras investigaciones para el control microbiológico de estás aguas, beneficiando a la comunidad = que acuden a estos balnearios y a los dueños de estos centros para brindar una mejor calidad del agua.

Metodología

La presente investigación fue de campo de tipo descriptiva de corte transversa= l, el universo fueron los balnearios de aguas termales “El Riñón”, “Hostería Durán” y “Balneario Durán” de la parroquia Baños, cantón Cuenca – Ecuador. = Para poder realizar el estudio se obtuvieron los permisos correspondientes.=

Toma de muestras

Se analizaron un total de 16 muestras del agua termal de los balnearios “El Riñón”, “Hostería Durán” “Balneario Durán” y “Vertiente”.  ubicado en el sector Baños, Provincia d= el Azuay - Ecuador. Las muestras de agua fueron recolectadas de manera aséptic= a, utilizando frascos de vidrio esterilizados de 500 ml, de acuerdo con lo indicado en las normas ecuatorianas NTE-INEN-2-176 y NTE-INEN-2-169 (11,12). Las mismas fueron trasladadas en un cooler para mantener condiciones de temperatura de 35°C, hasta llegar al laboratorio de la Universidad Católica= De Cuenca, donde se realizaron los análisis microbiológicos.=

Análisis Fisicoquímico

Los análisis fisicoquímicos se realizaron con un medidor de pH de marca Dr. Met= er – China (pH y temperatura), la cual se analizó en el mismo instante de toma de muestra y la conductividad eléctrica con un medidor multiparámetro de marca HACH – Estados Unidos, se tomó lectura de la conductividad, para cada punto= de muestreo. La interpretación de los resultados se realizó según los lineamie= ntos establecidos por los fabricantes.

Análisis microbiológico

Se realizó la siembra y cuantificación de las colonias de (hongos, levaduras, = E. coli, coliformes y Staphylococcus aureus), utilizando las placas= de Compact Dry X-SA para determinación de Staphylococcus aureus, Compact Dry YM para determinación de hongos y levaduras, y Compact Dry EC para determinar E. coli y Coliformes. Se colocó 1000 μL de cada una de las muestras de los balnearios en las placas Compact Dry. Las placas se incubar= on a una temperatura de 35-37°C para Compact Dry X-SA y EC, por un periodo de 24 horas y a 25°C de 5 a 7 días para las placas Compac Dry YM.

 

 

Resultados

Para el presente estudio se analizó el agua term= al de los balearios “El Riñón”, “Hostería Durán”, “Balneario Durán” y una vertiente la cual se distribuye a los 3 balnearios, se tomó una muestra cada domingo durante 4 semanas, puesto que la misma agua de las piscinas termale= s se encuentra desde el viernes, se tomó la muestra a partir del horario de 17:00 pm, ya que a partir de las 17:30 pm se procede a realiza el lavado de las piscinas.

Para cada muestra tomada cada domingo se analizó mediante cultivo la presencia de Escherichia coli, Staphylococcus aureus= , coliformes, hongos y levaduras.

Análisis bacteriológico

La calidad de las aguas termales presenta gran diversidad de microorganismos que dependen de sus propiedades fisicoquímicas como la temperatura, pH, conductividad eléctrica. Pese a que el agua termal= de los balnearios es un hábitat extremo por sus altas temperaturas existe una = gran población microbiana siendo de mayor interés sanitario Escherichia coli<= /i>, encontrando también Staphylococcus aureus, coliformes, hongos, levaduras, entre otros (10).

En la tabla 1 se observa el análisis cualitativo (presencia y ausencia) de las muestras tomadas de los 3 balnearios y la vertiente, durante 4 semanas, mediante la identificación del crecimiento de= las colonias bacterianas, utilizando las placas de Compact Dry X-SA para determinación de Staphylococcus aureus, Compact Dry YM para determinación de hongos y levaduras, y Compact Dry EC para determinar E. co= li y Coliformes.

Tabla 1. Análisis cualitativo de la presencia o ausencia de colinas bacterianas, de las muest= ras tomadas cada semana, mediante placas Compact Dry XSA, EC y YM, a partir de = los balnearios de aguas termales de la parroquia Baños Cuenca – Ecuador, 2023.<= span style=3D'mso-bidi-font-weight:bold'>

Fecha

Balneario

Staphylococcus aureus

E. coli

Coliformes

Hongos

Levaduras

&nb= sp;

&nb= sp;

Semana 1=

“El Riñón”

Presenci= a

Ausencia=

Presenci= a

Ausencia=

Ausencia=

“Hostería Durán”

Presenci= a

Ausencia=

Presenci= a

Presenci= a

Ausencia=

“Balneario Durán”

Presenci= a

Presenci= a

Presenci= a

Presenci= a

Ausencia=

Vertiente

Presenci= a

Ausencia=

Ausencia=

Ausencia=

Ausencia=

<= /span>

&nb= sp;

&nb= sp;

&nb= sp;

Semana 2=

“El Riñón”

Presenci= a

Presenci= a

Presenci= a

Presenci= a

Presenci= a

“Hostería Durán”

Presenci= a

Ausencia=

Presenci= a

Presenci= a

Presenci= a

“Balneario Durán”

Presenci= a

Ausencia=

Presenci= a

Presenci= a

Presenci= a

Vertiente

Ausencia=

Ausencia=

Ausencia=

Ausencia=

Ausencia=

Tabla 2. Análisis cualitativo de la presencia o ausencia de colinas bacterianas, de las muestras tomadas cada semana, mediante placas Compact Dry XSA, EC y YM, a partir de los balnearios de aguas termales de la parroquia Baños Cuenca – Ecuador, 2023. (continuación)

Fecha

Balneario

Staphylococcus aureus

E. coli

Coliformes

Hongos

Levaduras

&nb= sp;

&nb= sp;

Semana 3=

“El Riñón”

Presenci= a

Presenci= a

Presenci= a

Ausencia=

Presenci= a

“Hostería Durán”

Presenci= a

Ausencia=

Presenci= a

Presenci= a

Presenci= a

“Balneario Durán”

Presenci= a

Presenci= a

Presenci= a

Presenci= a

Presenci= a

Vertiente

Ausencia=

Ausencia=

Ausencia=

Ausencia=

Ausencia=

<= /span>

&nb= sp;

&nb= sp;

&nb= sp;

Semana 4=

“El Riñón”

Presenci= a

Presenci= a

Presenci= a

Ausencia=

Presenci= a

“Hostería Durán”

Presenci= a

Ausencia=

Presenci= a

Presenci= a

Presenci= a

“Balneario Durán”

Presenci= a

Presenci= a

Presenci= a

Presenci= a

Presenci= a

Vertiente

Ausencia=

Ausencia=

Ausencia=

Ausencia=

Ausencia=

En la tabla 2 se observa el análisis cuantitativ= o de las muestras tomadas durante 4 semanas de los 3 balnearios y la vertiente, mediante el conteo de cada placa, utilizando las placas de Compact Dry X-SA para determinación de Staphylococcus aureus, Compact Dry YM para determinación de hongos y levaduras, y Compact Dry EC para determinar E. co= li y Coliformes.

 SEQ Tabla \* ARABIC 3. Análisis cuantitativo de colinas bacterianas, de las muestras tomadas cada semana, analizadas mediante placas Compact Dry XSA, EC y YM, a partir de los balnea= rios de aguas termales de la parroquia Baños Cuenca – Ecuador, 2023

Semana 1

Balneario

Staphylo= coccus aureus

E. coli<= o:p>

Coliformes<= /o:p>

Hongos

Levaduras

 

“El Riñón”<= /o:p>

100 UFC

0 UFC=

15 UFC

0 UFC=

0 UFC=

“Hostería Durán”=

100 UFC

0 UFC=

15 UFC

1 UFC=

2 UFC=

“Balneario Durán= ”

72 UFC

1 UFC=

2 UFC=

3 UFC=

2 UFC=

Vertiente

3 UFC=

0 UFC=

0 UFC=

0 UFC=

0 UFC=

 

 

 

Semana 2

“El Riñón”<= /o:p>

58 UFC

3 UFC=

5 UFC=

3 UFC=

5 UFC=

“Hostería Durán”=

20 UFC

0 UFC=

12 UFC

4 UFC=

1 UFC=

“Balneario Durán= ”

21 UFC

0 UFC=

8 UFC=

1 UFC=

1 UFC=

Vertiente

0 UFC=

0 UFC=

0 UFC=

0 UFC=

0UFC<= /span>

 SEQ Tabla \* ARABIC 4. Análisis cuantitativo de colinas bacterianas, de las muestras tomadas cada semana, analizadas mediante placas Compact Dry XSA, EC y YM, a partir de los balnea= rios de aguas termales de la parroquia Baños Cuenca – Ecuador, 2023 (continuació= n)

Semana 1

Balneario

Staphylo= coccus aureus

E. coli<= /span>

Coliformes<= /o:p>

Hongos

Levaduras

 

 

Semana 3

“El Riñón”<= /o:p>

50 UFC

3 UFC=

5 UFC=

0 UFC=

13 UFC

“Hostería Durán”=

51 UFC

0 UFC=

25 UFC

4 UFC=

6 UFC=

“Balneario Durán= ”

35 UFC

7 UFC=

13 UFC

2 UFC=

1 UFC=

Vertiente

1 UFC=

0 UFC=

0 UFC=

0 UFC=

0 UFC=

 

 

 

Semana 4

“El Riñón”<= /o:p>

100 UFC

3 UFC=

5 UFC=

0 UFC=

13 UFC

“Hostería Durán”=

100 UFC<= o:p>

1 UFC=

24 UFC

3 UFC=

8 UFC=

“Balneario Durán= ”

100 UFC

5 UFC=

13 UFC

3 UFC=

3 UFC=

Vertiente

0 UFC=

0 UFC=

0 UFC=

0 UFC=

0 UFC=

Nota: Leyenda. Unidades Formadoras de Colonias (UFC).

Promedio de las muestras tomadas durante 4 semanas de l= as bacterias presentes en el “Balneario el Riñón”, “Hostería Durán”, “Balneario Durán” y la Vertiente, de la parroquia Baños.  Cuenca – Ecuador 2023

En la figura 1 se observa el predominio de las muestras tomadas durante cuatro semanas del Staphylococcus aureus en= las piscinas de aguas termales “Balneario el Riñón” con un promedio de 77% sien= do este el valor encontrado más alto, “Hostería Durán” con un 68% y “Balneario Durán” con un porcentaje de 57%.

Análisis Fisicoquímico

La calidad de las aguas termales exhibe una ampl= ia variedad de microorganismos, los cuales están influenciados por las propied= ades fisicoquímicas del agua, como la temperatura, pH y la conductividad eléctri= ca. A pesar de que el agua termal de los balnearios se considera un hábitat ext= remo debido a sus altas temperaturas, se ha observado la presencia de una poblac= ión microbiana que logra adaptarse a estas condiciones adversas (3).=

 SEQ Tabla \* ARABIC 5. Análisis físico químico de los parámetros (pH, temperatura y conductividad), de las muestras tomadas cada semana, mediante un medidor de pH de marca Dr. Meter (pH y temperatura), la cual se analizó en el mismo instante de toma de muestra, e= n el horario de 17:00pm y la conductividad eléctrica con un medidor multiparámet= ro de marca HACH, a partir de los balnearios de aguas termales de la parroquia Baños Cuenca – Ecuador, 2023.

Semana

Balneario

pH

Temperatura=

Conductividad

Semana 1

“El Riñón”<= /o:p>

7.92<= /span>

35.5°C

38,7 µS/cm<= /o:p>

“Hostería Durán”=

8,29<= /span>

35.7°C

40,5 µS/cm<= /o:p>

“Balneario Durán= ”

8,51<= /span>

33°C<= /span>

41,7 µS/cm<= /o:p>

Vertiente

7,42<= /span>

65.3°C

38,5 µS/cm<= /o:p>

 

Semana 2

“El Riñón”<= /o:p>

7.92<= /span>

35.5°C

38,6 µS/cm<= /o:p>

“Hostería Durán”=

8,36<= /span>

35.8°C

40,5 µS/cm<= /o:p>

“Balneario Durán= ”

8,65<= /span>

33,1°C

39,7 µS/cm<= /o:p>

Vertiente

7,92<= /span>

66.5°C

39,5 µS/cm<= /o:p>

 

Semana 3

“El Riñón”<= /o:p>

7.93<= /span>

35°C<= /span>

38,9 µS/cm<= /o:p>

“Hostería Durán”=

8,46<= /span>

35°C<= /span>

38,5 µS/cm<= /o:p>

“Balneario Durán= ”

8,45<= /span>

33,4°C

39,9 µS/cm<= /o:p>

Vertiente

7,93<= /span>

68.3°C

39,2 µS/cm<= /o:p>

 

Semana 4

“El Riñón”<= /o:p>

7.92<= /span>

35.5°C

38,7 µS/cm<= /o:p>

“Hostería Durán”=

8,29<= /span>

35.7°C

41,5 µS/cm<= /o:p>

“Balneario Durán= ”

8,50<= /span>

33°C<= /span>

41,7 µS/cm<= /o:p>

Vertiente

7,42<= /span>

66.3°C

38,5 µS/cm<= /o:p>

En la tabla 4 indica el valor de pH en el “Balne= ario el Riñón” y la Vertiente con un valor promedio de 7.92, en la “Hostería Dur= án” y “Balneario Durán” con un valor promedio de 8,43.

La temperatura en medida en grados centígrados (= °C) se encuentra con un valor constante de 35°C en el “Balneario el Riñón” y “Hostería Durán”, al contrario de la Vertiente la cual tienen una temperatu= ra promedio de 66,6°C.

La conductividad eléctrica medida en microSiemens/centímetro (µS/cm) se encuentra en un valor promedio en los 3 balnearios de 39,9 µS/cm, al contrario de la vertiente la cual se encuentra= en un valor promedio de 38,5 µS/cm.

Discusión

En Ecuado= r, se ha llevado a cabo un número limitado de estudios sobre las propiedades m= icrobiológicas de las aguas termales que se encuentran en el país (13). Los diferentes microrganismos presentes en las aguas termales exhiben una amplia variedad = de formas de vida, las cuales son influenciadas por sus características fisicoquímicas, como su temperatura, pH y conductividad eléctrica. A pesar = de que las aguas termales de los balnearios constituyen un entorno extremo deb= ido a sus elevadas temperaturas, se ha observado la existencia de una población microbiana que logra adaptarse a estas condiciones. Las temperaturas tomadas cada semana de los balnearios (tabla 4) se considerada mesotermal según (15= ) y según (14), la temperatura de las aguas termales está relacionada con la profundidad del origen en medida del suelo, de esta manera la temperatura c= omo la presión aumenta a medida que se adentra a mayores profundidades, lo que permite discutir sobre el gradiente geotérmico de temperatura, que se estim= a en 3°C por cada 100 metros (14). La disminución de la temperatura va a ser considerada consecuencia del cambio climático (15).

En el parámetro de pH (tabla 4), la mayoría de las bacterias tienen la capacidad = de crecer en un rango de pH que vaya desde 5,5 hasta 8,0, por lo tanto, las piscinas de agua termal de la parroquia Baños coincide con el pH óptimo par= a el crecimiento de ciertos microorganismos (16). Se encontró que entre las variables que tienen mayor influencia en la variación del pH se destacan los sulfatos, los cloruros, las fluctuaciones en los niveles de oxígeno disuelt= o y el mes en el que se recolectaron las muestras. Esto se debe a que, en algun= os meses, el agua presenta una mayor concentración de iones de hidrógeno debid= o a diversos factores climáticos (17).

En un est= udio donde se evaluó el pH fue realizado por (18), en las aguas termales del balneario Ilaló en Pichincha Ecuador, obteniendo un valor promedio de pH 7,= 39 en los muestreos realizados, lo que indica que las piscinas termales se encontró un pH relativamente neutro, similar al obtenido en el presente est= udio en las aguas termales del “Balneario El Riñón” y la Vertiente, al contrario= del “Balneario Durán” y “Hostería Durán” (tabla 4) estos valores pueden variar debido a los minerales que contiene estas aguas y el mes de recolección de muestras ya que el agua en algunos meses tiene mayor concentración de hidró= geno debido a los diferentes factores climáticos (18).

Los resultados de conductividad revelan que el agua presenta una mineralización excesiva con una conductividad eléctrica superior a 1000 µS/cm, según un estudio realizado por (6), en las aguas termales del municipio libertador d= el Estado Sucre, Venezuela el resultado promedio fluctuó entre 9, 360 y 14, 16 mS/cm (6), en comparación con el estudio realizado en Los balnearios de la parroquia Baños, Cuenca Ecuador, esta variación se debe a las condiciones d= el lugar, como la ubicación geográfica.

En el cas= o de los parámetros bacteriológicos el Staphylococcus aureus es una bacte= ria patógena común en los seres vivos y se encuentra en gran parte del cuerpo humano, especialmente la piel, mucosa y fosas nasales. Se estima que aproximadamente el 30% de la población humana está colonizada por esta bacteria, permaneciendo en estado latente hasta que se activan los factores= de virulencia para desencadenar una infección (19). Los resultados obtenidos de los análisis microbiológicos de los balnearios se resumen en la tabla 2, comparando con los resultados del estudio de Calidad fisicoquímica y microbiológica de las aguas termales del “Complejo Turístico Santa Catalina” 2021, ubicado en Papallacta, Provincia de Napo, obtuvieron en el muestreo 1= un valor promedio de 1,66 x 10 UFC/ml; en el muestreo 2 se obtuvo un promedio = de 1,20 x 102 UFC/ml (20). La presencia de esta bacteria cada semana puede ser explicada debido a que se encuentran naturalmente en el entorno y es posible que hayan llegado al balneario a través de diferentes medios como el aire, suelo y lluvia (21).

Los resul= tados obtenidos muestran que existen cantidades bajas de E. coli y colifor= mes fecales en los 3 Balnearios en comparación con el estudio realizado en las piscinas “El Salado” en el cantón Baños de Agua Santa provincia de Tungurah= ua con un promedio de 5000 UFC/ml a 410 UFC/ml (22), en comparación con los resultados de este estudio el valor de coliformes es elevado, esto puede deberse a el día de muestreo en los balnearios ya que en días feriados exis= te mayor afluencia de personas en estos centros recreativos. La detección de coliformes fecales en el agua supone un riesgo si se consume, ya que estas bacterias pueden provocar enfermedades y los síntomas más frecuentes son problemas gastrointestinales.

De igual manera se identificaron hongos y levaduras, en el estudio llevado a cabo por Aguirre en 2018 sobre el análisis microbiológico de las aguas termales del Cantón Baños, se encontró la presencia de mohos y levaduras en el agua, con niveles similares a los obtenidos en el presente estudio (23).

El estudio realizado en el balneario El Raposo en España indica que, aunque la presenc= ia de estos microorganismos no es común en aguas termales, se han encontrado en diversos manantiales. Esto se debe a que la mayoría de estos microorganismos provienen del suelo, pero son capaces de adaptarse a las condiciones de los ambientes acuáticos presentes en las aguas termales (24).=

De acuerdo con (25), se señala que la presencia significativa de mohos y levaduras en = el agua es un indicador de contaminación ambiental y posibles problemas de higiene.

Conclu= siones<= o:p>

·      =    Las piscinas de agua termal “El Riñón”, “Hostería Durán” y “Balneario Durán” en base a los resultados obtenidos se clasifican en alcalinas, la presencia de ciertos minerales como el carbonat= o de calcio, puede hacer que el agua sea más alcalina, según sus temperaturas se caracterizan como aguas mesotermales, de conductividad fuerte, estos paráme= tros se deben a la mineralización excesiva que tienen estas aguas ya que la cant= idad y el tipo de minerales disueltos pueden influir en estas propiedades. =

·      =    La presencia de bacterias en las pisci= nas proviene principalmente de la liberación de sudor por parte de los nadadore= s, de acuerdo con el análisis microbiológico, predomina la especie Staphylo= coccus aureus, la cual se encuentra comúnmente en la piel y en las membranas mucosas de los seres humanos, también se obtuvo en menor frecuencia E. c= oli, coliformes, hongos y levaduras las cuales puede ser transportada por personas al ingresar a las aguas termales.

·      =    La calidad microbiológica de estas agu= as termales dependen de las condiciones fisicoquímicas, después de haberlas analizado considero que las piscinas de agua termal “El Riñón”, “Hostería Durán” y “Balneario Durán” son aguas mesotermales y alcalinas, podemos confirmar que su calidad microbiológica es notablemente buenas ya que la presencia de Staphylococcus aureus no representa un riesgo para la población que acude a estos centros recreativos dado que esta bacteria forma parte de la flora normal de cuerpo humano, lo mismo sucede con las bacterias presentes en menor frecuencia: E. coli, coliformes, hongos y levadur= as no representan un riesgo a la población.

Conflicto de intereses

Los autores declaran que no existe conflicto de interés para la publicación del= presente artículo.

Declaración de contribución de los autores=

Alexandra Estefania Anguisaca Vega diseño el estudio, analizó los datos y elaboró el borrador.

Referencias Bi= bliográficas

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ISSN: 2697-3391

Vol. 6 No. 3.2, pp. 86 – 102, a= gosto – septiembre 2023

www= .anatomiadigital.org

 

 

 

 

 

<= span style=3D'mso-spacerun:yes'>                                      Neurocientífico                       Página <= span style=3D'mso-no-proof:yes'>86 = | 102<= o:p>

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