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Eva= luación de la calidad microbiológica de dos plantas embotelladoras mediante la técn= ica de filtro de Membrana y Placa 3M™ Petrifilm™ Aqua <= b>en la Región de Azuero

 

Alexis De La Cruz<= sup>1, Shamir Melillo2, Magali Pérez2

1 Docente e investigador Centro Regional Universitario de Azuero, Esc= uela de Biología.

2 Licenciados en Biología, Universidad de Panamá.

 

 

*Autor para Correspondencia. E-mail: alexis= .delaclombardo@gmail.com

 

    Recibido: 12 de mayo de 2020 

Aceptado: 22 de jun= io de 2020

______= ________________________________________________________________________Resumen

En los últimos años se ha dado un aumento = en la demanda de agua envasada, por lo cual han surgido una gran cantidad de plantas embotelladoras de agua. Este estudio se enfocó en determinar la cal= idad microbiológica de las etapas de tratamiento de dos plantas embotelladoras (= G y Q). Se seleccionaron puntos de tratamientos análogos en ambas plantas. Estas muestras fueron procesadas mediante la técnica de filtro de membrana con me= dios re hidratados de 3M™Petrifilm™Aqua para recuento heterotróficos, para Coliformes y para recuento de hongo y levaduras. Los análisis determinaron que no existe diferencias significativas entre = las semanas de muestreo, para Heterótrofos, ni para la variable hongo y levadur= as (KW H=3D1.4883 p =3D0.6850 y KW H=3D0.1935 p =3D0.9786 respectivamente). Para los Coliformes, si se encontraron diferencias (KW H=3D16. 0547 p =3D0.0011). <= /o:p>

P= alabras clave: Heterótrofos, Coliformes, Hongos y Levaduras, Etapas de tratamiento= .

 

A= bstract

Analog treatment points were selected in both plants. These samples = were processed using the membrane filter technique with rehydrated media from 3M= ™ Petrifilm ™ Aqua for heterotrophic counting, for Coliform and for fungus and yeast counts. The analyzes determined that there are no significant differe= nces between the sampling weeks, for Heterotrophy, nor for the variable fungus a= nd yeast (KW H=3D1.4883 p =3D0.6850 and KW H=3D0.1935 p =3D0.9786 respectivel= y). For Coliform, if differences were found (KW H=3D16. 0547 p =3D0.0011).

Keywords: Heterotrophy, Coliform, Fungi and Yeast, Stages of treatment.

1.   Introducción

 

El agua es uno de los recursos más abundantes de la naturaleza, pero= es cada vez más escasa. En el caso del agua que abastece a las ciudades por lo general proviene de fuentes superficiales como ríos o subterráneas como los pozos profundos; sin embargo, el ser humano ha contaminado tanto estas fuen= tes que sus aguas deben ser sometidas a estrictos tratamientos de purificación<= span style=3D'color:#333333'>.

En = la actualidad el acceso a fuentes de agua segura, es una preocupación mundial = por el crecimiento poblacional y los altos índices de contaminación. En el mundo existen alrededor de 783 millones de personas, es decir, un 11% de la población, que aún vive sin acceso a agua potable y saneamiento (OMS 2012). Muchos países están afrontando una distribución desigual en espacio y tiempo ocasionada por la fuerte contaminación y el agotamiento de fuentes superficiales y subterráne= as (Gossling et al., 2012). Se prevé que para el año 2,100 más de 3.2 millones de personas enfrentarán problemas de acceso al agua bajo un escenario de aumen= to de 4°C debido al cambio climático. = (Parry et al., 2009)

Estudios recientes indican que el mercado nacional= de aguas envasadas, presenta un notable crecimiento debido a la falta de confi= anza de las personas en la calidad del agua de abastecimiento público. (López, 2006)

La calidad del agua potable envasada ha aumentado durante los últimos años, no obstante, se desconoce la calidad que puede ofrecer al consumidor. En la ciudad de Maracaibo, Venezuela, científicos realizaron un estudio en el que se evaluaron 10 marcas de agua envasada, es= tas fueron comparadas con los estándares de calidad que las normas establecen, = como resultado solamente 2 de las 10 marcas cumplieron con el requisito microbiológico, siendo aptas para el consumo humano. (Benítez et al., 2013)

Un estudio similar se realizó en el municipio de Montería, departamento de Córdoba, Colombia; en este estudio se analizaron las características microbiológicas en 16 plantas de procesamiento y el cumplimiento de las nor= mas vigentes en ese país, como consecuencia varias de las empresas tuvieron que hacer correctivos en su proceso de purificación. (Simanca et al.,  2010)

 

El estudio consistió en evaluar la calidad microbiológica de las diversas etapas del sistema de procesamiento dentro dos plantas embotellado= ras de agua en la región de Azuero. La investigación fue realizada en el mes de agosto y la primera semana de septiembre de 2016. En este trabajo se utiliz= a la técnica de filtro de membrana y la técnica de placas 3M™Petrifilm™Aqua, para levantar un perfil microbiológico de las diversas etapas y así compararlas, durante las diferentes semanas de muestr= eo, así cumplir con el objetivo primordial de determinar la calidad microbiológica = de las etapas de tratamiento de dos plantas embotelladoras de agua en la regió= n de Azuero.

 

 

 

 

2.   Mater= iales y método

Este trabajo de investigación se realizó en dos Plantas de procesamiento y embotellado de agua, una de las empresas, se localiza en la provincia de Los Santos y la otra, está en la provincia de Herrera. La localización exacta y= el nombre de ambas empresas están reservadas bajo un contrato de confidenciali= dad.

La investigación fue de carácter descriptivo, ex post facto, al azar, por un periodo de 4 semanas. Al final se recabaron 144 muestras por planta, 288 en= tre las 2 y consistió en seleccionar dos plantas procesadoras de agua. Se escogieron 4 puntos de muestreo análogos en ambas plantas: fuente primaria (FP), filtración por carbón activado (CA), etapa de desinfección (ED), etapa final (EF), En cada planta se tomó 1 muestra y 2 réplicas de 500 ml por pun= to de muestreo (3muestras x 4 puntos=3D12muestras en cada planta). Se debe tom= ar en cuenta que los sistemas de tratamiento y purificación de agua en las dos plantas son similares, mas no iguales en cuanto a sus etapas y procesos.

Las muestras fueron procesadas mediante la técnica de filtro de membrana (FM). Luego de pasar por el proceso de filtro de membrana, dichas membranas fueron colocadas sobre un medio rehidratado de 3M™Petrifil= m™Aqua de la siguiente manera: de cada muestra por puntos se colocará 1 membrana e= n un medio rehidratado de 3M™Petrifilm™Aqua para recuento de heterotróficos(AQCH), 1 en un medio rehidratado de 3M™Petrifil= m™Aqua para recuento de Coliformes (AQCC) y 1 en un medio rehidratado de <= span style=3D'font-size:12.0pt;font-family:"Garamond",serif;mso-fareast-font-fam= ily: "Times New Roman";mso-bidi-font-family:"Times New Roman";mso-ansi-language: ES-PA'>3M™Petrifilm™Aqua para recuento de hongos y levaduras(AQYM).

Para el análisis estadístico de los datos obtenidos, se transformó l= as unidades formadoras de colonias (UFC), a log (x+1), prueba de Kruskall-Wall= is, U de Mann- Whitney

 

3.   Resultados y discusión

De acuerdo a los análisis estadísticos aplicados a los datos entre los distint= os procesos de producción de agua para ambas plantas (Prueba “d” de Somers) que determina la Asociación entre datos Intervalo vs datos Ordinales, no se encontró asociación significativa en la presencia de Heterótrofos entre Puntos en las Plantas G y Q.

El diagrama de caja y bigote, (Figura Nº 1) muestr= a que para la planta G, no hay una asociación con relación a cada uno de los proc= esos de tratamiento.

En = el comportamiento de la planta Q, el número de heterótrofos, se mantuvo simila= r en todas las etapas (Figura Nº 2) salvo que= hubo un descenso en la última etapa, si comparamos con la planta G, pudiendo ser esta última menos efectiva en los procesos de remoción de heterótrofos. Par= a el caso de la planta Q, se encontró asociación significativa inversa de la presencia de Heterótrofos entre los 4 puntos de la planta Q.

 

3D"Cuadro3D"Cuadro=

 

 

 

 

 

Algunos microorgani= smos forman biopelículas sobre superficies que están en contacto con agua. La proliferación que se produce después del tratamiento del agua de consumo se conoce con frecuencia como “re-proliferación”. Es posiblemente que debido a ello se da la persistencia de microorganismos a través de las diversas etap= as y es que normalmente, se refleja en un aumento del recuento de heterótrofos en placa (RHP) en muestras de agua. Los valores de RHP aumentan sobre todo en partes de los sistemas de distribución por tuberías y en etapas donde se produce estancamiento de agua o se da la utilización de filtro de carbono. (OMS, 2006).

En relación a los Coliformes, existe asociación entre puntos en la concentración de Coliforme= s, siendo la asociación inversa, es decir que los valores más altos se encontr= aron al inicio del proceso, para la planta G, lo que indica que, a nivel del agua subterránea y almacenamiento, se pudo determinar que los valores son más al= tos, lo que revela que las últimas etapas son más efectivas en la remoción de los Coliformes (Figura Nº 3).

Podemos ver que el análisis determinó = un proceso de remoción, con tendencia al descenso de Coliformes durante las et= apas de procesamiento y tratamiento de la planta G (Figura Nº 3), no así en el c= aso de los Heterótrofos, ya que estos últimos tienden a ser más persistentes, en procesos de filtración.                   =                                                                           =                                                                            =  

Respecto a la plant= a Q, se encontró asociación altamente significativa inversa de la presencia de Coliformes entre puntos de procesamiento, (Figura Nº 4) muy similar a la pl= anta G. se pudo confirmar que ambas plantas son efectivas en la remoción para la variable Coliformes, hay una tendencia a la disminución en cada una de las etapas de tratamiento.

 

3D"Cuadro3D"Cuadro=

 

 

 

 

 

 

Para el caso de Las variables hongos y levaduras, también la tendencia es similar con respecto a los Coliformes, existe asociación significativa de presencia de hongos y levaduras entre puntos, es inversa también, esto para la planta G, (Figura = Nº 5 y 6). La tendencia en esta investigación, determinó que los hongos y levadu= ra, son removidos, pero hay cierta asociación en su presencia al principio de l= os procesos de tratamientos.

3D"Cuadro3D"Cuadro=

 

 

 

 

 

 

Los sistemas de filtración pulidores impiden fundamentalmente la entrada de bacterias y protozoos cuyo tamaño es de 0.3 a 25 micras y son muy útiles en la gran may= oría de situaciones. Los sistemas de purificación generalmente combinan técnicas= de filtración, con uno o más técnicas de desinfección. (Escobedo, Salas, y Muñ= oz. 2006)

Dichos procesos son aplicados tradicionalmente de manera consecutiva y como arrojan claramente = los resultados son altamente efectivas para las bacterias del grupo de los Coliformes; para los hongos y levaduras en ambas plantas procesadoras de ag= ua, pero evidenciándose una elevada persistencia por parte de microorganismos heterótrofos en ambas compañías.

La prueba de Kruskall-Wallis (Fig. No. 7 y 8) muestra que no hay diferencia entre las 4 semanas de evaluación microbiológica, para la variable heterótrofos en amba= s plantas embotelladoras de agua. (KW H=3D1.4883 p =3D0.6850). Para el caso de los ho= ngos y levaduras no se encontraron diferencias significativas (KW H=3D0.1935 p =3D= 0.9786), entre las 4 semanas del estudio.

 

3D"Cuadro

3D"Cuadro
 

 

 

 

 


Los resultados estuvieron, para las 4 semanas del estudio, entre 0 a 1.0, lo que determinó, que los hongos y levadura, no representaron problemas para ambas plantas.  Un estudio similar se realizó en el mun= icipio de Montería, departamento de Córdoba, Colombia; en este estudio se analizar= on las características microbiológicas en 16 planta de procesamiento y el cumplimiento de las normas vigentes en ese país, como consecuencia varias de las empresas tuvieron que hacer correctivos en su proceso de purificación. (Simanca et al., 2017).

Se determinó la rel= ación microbiológica entre las plantas de procesamiento de agua estudiadas, se ob= tuvo como resultado que en ambas plantas los valores se mantienen en el ámbito de 0.0 a 1.0 con leves variaciones que arrojan valores máximos de 2 de acuerdo= con la prueba ejecutada U de Mann Whitney no se encontraron  diferencias significativas de la presen= cia de microorganismos heterótrofos entre las dos  plantas embotelladoras (U=3D993  p=3D0.2440), la carga microbiología de heterótrofos es muy similar en ambas plantas, como se puede observar (Figura N° 9).

Figura No.9 Diagrama de caja que representa los resultados de la prueba u de mann-whitn= ey para la determinación de la diferencia entre plantas para la presencia de A= QHC.

 

 

 

 

 

 

Es = de esperarse que se observe la presencia de organismos heterótrofos en ambas platas, ya que las aguas subterráneas que sirven como fuente de captación brindan un ecosistema adecuado para el crecimiento de la población de estos microrganismos. Los cuales, son transportados a través de todo el sistema de tratamiento. Estos microrganismos abundan en el agua, incluidas las aguas tratadas, los tanques de almacenamiento y los sistemas de abastecimiento, ya que poseen gran adaptación, pueden tolerar condiciones adversas de suminist= ro de oxígeno y persisten por más tiempo que otros microorganismos en el agua. (M. Robert, 2014)

En la investigación realiza= da por Domínguez y Ríos (2011) en= agua embotellada, se demuestra que en cuatro marcas de agua la carga microbiológ= ica no muestra diferencia significativa. Por lo que se corrobora que tanto en plantas como en agua sucede el mismo fenómeno.

&= nbsp;

5.   Conclusión

No se encontró asociación significativa en la presencia de Heterótrofos entre Puntos en las Plantas G= y Q. En relación a los Coliformes, existe asociación inversa entre puntos en la concentración de Coliformes, a través de las etapas de procesamiento y trat= amiento de ambas plantas Los hongos y levadura, son removidos, pero hay cierta asociación en su presencia al principio de los procesos de tratamientos de ambas plantas. No existen diferencias significativas entre las semanas de muestreo, ni para Heterótrofos, ni para la variable Hongo y levaduras; para= los Coliformes sí se encontraron diferencias.

 

6.   Agradecimie= nto: Al laboratorio de Calidad= de Agua del MINSA de Los Santos.

 

 

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    Invest. Pens. Crit. (ISSN 1812-3864; eISSN 2644-4119)

    Vol. 8, No. 3, Septiembre – Diciembre 2020  

    pp. 68 - 77

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