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Evaluación de Pseudomona spp. y Coliformes asociad= os a parámetros abióticos en fuentes de agua subterráneas de la región de Azuero= =

Alexis De La Cruz1*

1 Docente e investigado= r de la Universidad de Panamá, Investigador del Ministerio de Salud, Departament= o de Calidad de Agua

 

* Autor para correspondencia. E-mail: alexisdelac= @gmail.com=

Recibido: 8 de juli= o de 2019

Aceptado: 12 de ago= sto de 2019

­­­­­­­____= ___________________________________________________________________________= ______

Resumen<= span style=3D'font-size:12.0pt;font-family:"Garamond",serif;mso-ansi-language:ES= -PA'>

En las aguas subterráneas se transportan muchos parásitos, bacterias coliformes y otras especies como la Pseudomona aeruginosa, Klebsiela, Enterococos, entre otros.  Siendo u= na peligrosa fuente de toxiinfecciones y Enfermedades gastrointestinales. El objetivo de este trabajo fue determinar la ocurrencia de Pseudomona aeruginosa y coliformes, en estación seca y lluviosa, en pozos de aguas subterráneas de la Provincia de Herrera y Los Santos y su relación con parámetros fisicoquímicos. Este estudio fue no experimental, que consistió en tomar al azar 15 pozos de agua subterránea en la Provincia de Los Santos y La Provincia de Herrera tanto en temporada seca y lluviosa, = se procedió a determinar la ocurrencia de Pseudomonas spp., y coliformes media= nte filtración por membrana, con la medición de parámetros físico químicos de campo. Los resultados, arrojaron que los niveles de crecimi= ento de P. aeruginosa en los pozos subterráneos de la Provincia de Los Santos, indican que es mayor en cantidades significativas en ambas épocas en comparación con la provincia de Herrera, la época lluviosa presentó una may= or ocurrencia de P. aeruginosa en comparación con la época seca, Los parámetros fisicoquímicos se mantuvieron constantes en las dos épocas de estudio, Concluimos que los niveles  de cloro residual en ambas  Provincias,  en lo que concierne a las épocas en est= udio fueron, encontrados valo= res casi aceptables para la Provincia de Herrera pero cierto incumplimiento par= a la Provincia de Los Santos.

Palabras clave: Pseudomona spp., Coliformes, Agua Subterránea.=

Abstract

In the groundwater = are conveyed many parasites, coliform bacteria and other species such as the Pseudomona aeruginosa, Klebsiela, Enterococci, aerobic mesophilic, among others.  Being a dangerous source of poisoning and gastrointestinal diseases.= The main objective of this study was to determine the occurrence or absence of = P. aeruginosa in dry and rainy sea= son in Wells of groundwater in the province of Herrera and Los Santos, and its relationship with physicochemical parameters. This study was non-experiment= al, which consisted in taking random 15 wells of groundwater in the province of Herrera and Los Santos province both in dry season and rainy, was to determ= ine the occurrence of Pseudomonas spp. with measuring chemical physical field parameters. Results, showed that the levels of growth of P. aeruginosa in groundwater from wells of the Los Santos province, indicate that it is high= er in significant quantities in both periods compared to the province of Herre= ra, the rainy season presented a greater occurrence of P. aeruginosa in compari= son with the dry season, physicochemical parameters were kept constant in the t= wo periods of study, concluded that the levels of residual chlorine in both provinces the maximum values required by the standard of Quality of water drinking DGNT-COPANIT 23-395-99, in regards to the times study were, found almost acceptable values for the province of Herrera but certain failure for the province of Los Santos.

Key words: Pseudomona = spp, Coliforms, underground water.

 

1   Introducción<= o:p>

El = agua subterránea es uno de los recurs= os más valiosos y asequibles, aunque nuestras percepciones con respecto al ambiente sub-superficial del que procede son a menudo poco claras e incorrectas (Var= gas, 2004).

En = las aguas subterráneas se transportan muchos parásitos, bacterias coliformes y otras especies como la Pseudomona aeruginosa, Klebsiella, Enterococcus spp., Mesofilos aerobios, entre ot= ros. Siendo una peligrosa fuente de toxiinfecciones y Enfermedades  gastrointestinales en la población consumidora de esta  agua (Campos et al.2002).Por tal motivo es impo= rtante el estudio de la calidad microbiológica y fisicoquímicas en los municipios = de La Paz y San Diego, para identificar los posibles agentes y causas que gene= ran enfermedades de origen hídrico y peligros sanitarios, determinando los agen= tes patógenos que alteran la calidad  d= e las aguas subterráneas, tomando dichos estudios  como base para el control y tratamientos de estas aguas.<= /span>

Por= su tolerancia a una amplia variedad de condiciones físicas se comporta como un patógeno oportunista eficaz. Su papel como patógeno responsable de infecciones comunitarias y nosocomiales está plenamente reconocido y resulta problemáti= ca la elección del antimicrobiano más adecuado. Esto se debe a que posee una elevada resistencia intrínseca a múltiples antibióticos y a una extraordina= ria capacidad para adquirir nuevos mecanismos de resistencia, principalmente por mutaciones. (Jorgensen, 2000)

El grupo Pseudomonas está constitu= ido por bacilos aerobios gramnegativos y móviles, algunos de los cuales producen pigmentos solubles en agua. Las especies del género Pseudomonas  se identif= ican sobre la base de varias características fisiológicas. Una de las propiedades más notables de Pseudomonas es la gran variedad de compuestos orgánicos que utilizan como fuente de carbono y energía (ONTIVEROS, 1983). Peudomonas aeruginosa, no es un pa= rásito obligatorio, puede ser fácilmente encontrada en el suelo y se comporta como desnitrificante, teniendo un papel importante en el ciclo del nitrógeno en = la naturaleza (SOARES, 1996).

El objetivo de este trabajo de investigación, fue valuar la ocurrencia de Pseudomona spp., y coliformes y su relación a parámetros físico químicos de= algunos pozos en la Región de Azuero.

 =

 =

2   Materi= ales y Método

2.2.1 Ubicación de sitios de estudio

Esta investigación se llevó a cabo,= en algunos Pozos de Agua Profunda en diferentes Comunidades y Distritos las Provincias de Herrera y Los Santos respectivamente.

Los análisis se realizaron seguidam= ente en las plantas potabilizadoras de Herrera (Ingeniero Roberto Reyna) y Los Santos (Rufina Alfaro).

 

Cuadro 1: Sitio de muestreo de la provincia de Herrera, evaluados los meses de noviembre 2016 y marzo 2017.

NUMERO

LOCALIDAD<= /span>

UBICACIÓN (NOMENCLATU= RA)

01<= /p>

CHUPAMAPA<= /span>

B 8=

02<= /p>

LOS POZOS<= /span>

B 11

03<= /p>

LOS POZOS<= /span>

B 12

04<= /p>

LOS POZOS<= /span>

 B 13

05<= /p>

OCU=

B 9=

06<= /p>

OCU=

B 11

07<= /p>

OCU=

B 13

08<= /p>

OCU=

B 15

09<= /p>

PESE

B 3=

10<= /p>

PESE

B 7=

11<= /p>

PESE

B 9=

12<= /p>

PESE

B 10

13<= /p>

SANTA MARIA

B 2=

14<= /p>

SANTA MARIA

B 3=

15<= /p>

SANTA MARIA

B 4=

Cuadro 2: Sitio de muestreo de la provincia de Los Santos, evaluados los meses de noviembre 2016 y marzo 2017= .

NUMERO

LOCALIDAD<= /span>

UBICACIÓN (NOMENCLATU= RA)

01<= /p>

EL CARATE<= /span>

B 7=

02<= /p>

EL COCAL

B 9=

03<= /p>

EL COCAL

B 13

04<= /p>

EL SESTEADERO

B 8=

05<= /p>

EL SESTEADERO

B 9=

06<= /p>

LAS CRUCES=

 B 4

07<= /p>

LAS CRUCES=

B 7=

08<= /p>

LAS PALMAS=

B 6=

09<= /p>

LAS PALMAS=

B 13

10<= /p>

LAS TABLAS=

B 53

11<= /p>

LAS TABLAS=

B 54

12<= /p>

SABANAGRANDE

B 6=

13<= /p>

SABANAGRANDE

B 7=

14<= /p>

TRES QUEBRADAS

B 7=

15<= /p>

TRES QUEBRADAS

B 8=

 

2.2.2 Diseño experimental

Este estudio fue no experimental, q= ue consistió en tomar al azar 15 pozos de agua subterránea en la Provincia de Los Santos= y La Provincia de Herrera tanto en época seca y lluviosa. Se tomaron 100 ml de muestras para los estudio microbiológico y 300 ml para los parámetros fisicoquímicos de agua en cada pozo de agua subterránea, 60 muestras por provincia (Los Santos y Herrera) durante 4 semanas de muestreo, con un tota= l de 120 muestras, tanto en época seca y lluviosa.

 

 

2.3 Metodología de campo

2.3.1 Toma de Muestras

Se procedió a colectar la muestra según lo descrit= o en el (Methods for the Examination of Water and Wastewater) (APHA,1999) Se tomaron  2 muestras por = pozos de agua subterránea con envases previamente esterilizado, los grifos de los pozos fueron esterilizados con alcohol al 70% seguidamente se flameo el grifo  y se dejó correr el agua por= aproximadamente 3 minutos;  se midieron el pH  y Cloro Residual en campo  seguidamente se tomaron  300 ml de agua, para la evaluación físi= co química  (alcalinidad y conductivid= ad) la segunda muestra se tomaron  100 ml = para evaluación microbiológica  los cual= es fueron transportadas en hielera a temperatura de 4 a 5º C. Se procedió a to= mar 15 muestras de pozos de agua subterráneas al azar de la provincia de Herrer= a de igual manera para la provincia de Los Santos.

2.4 Metodología de laboratorio

2.4.1 Técnicas Microbiológicas para el Análisis del Agua

Después de ser tomadas fueron llevadas a las plant= as potabilizadoras Roberto Reyna y Rufina Alfaro respectivamente en una caja térmica que mantenga una temperatura aproximada de 4 – 5 C°. se utilizara el método de membrana filtrante de acuerdo al Standard Method  (1995);  que consiste en verter 100 ml de la muestra  en un embudo previamente esterilizado en el cual se colocará una membrana filtrante con una porosida= d de 0.45 µm  con el propósito de retene= r los microorganismos deseados,  seguidam= ente será retirada la membrana y será colocada en un plato Petri  que contenga agar Cetrimides que es un = medio para la detección de  Pseudomonas  spp  basado en la produc= ción de fluorescina (marcador fluorescente en diversos ensayos químicos y biológ= icos debido a que exhibe fluorescencia).

La misma será incubada a 37 ºC durante 24 horas, lo mismo será con el propósito de determinar la bacteria Pseudomona aeruginosa en cada muestreo por provincia tanto en é= poca seca y lluviosa.

2.4.2 Técnica de Filtro de Membrana

La técnica de filtración de los líquidos es una técnica que se ha utilizado desde principios de la humanidad. La asociación entre membranas de filtración ha permitido desarrollar técnicas de filtraci= ón de líquidos, tales como las que conocemos hoy.

Esta técnica es rápida y sencilla de estimar. Cons= iste en filtrar un volumen de 100 ml o volúmenes menores, según la densidad bacteriana con la ayuda del vacío, la muestra de agua líquida o solución de agua, a través de un filtro de una membrana estéril de celulosa de 0.45 micrómetros de diámetro; luego el filtro de coloca sobre una almohadilla absorbente en una caja Petri, la caja de contiene el disco y la almohadilla= son colocadas en posición invertida con el medio de cultivo específico y se inc= uba a la temperatura adecuada.

 

 

 

2.8 Análisis Estadístico

Para los análisis de los resultados microbiológico= s de Pseudomonas, coliformes y los parámetros físicos -químicos. = Se utilizó cuadros de ANOVA, mediante un diseño completamente al azar, pruebas= de LSD y correlación entre las bacterias y los análisis físico-químicos   para medir = la relación entre ambos factores. Estos análisis se llevaron a cabo mediante el programa estadístico sistema SAS.

 

3   Resultados y discusión

Este estudio fue realizado para evaluar la especie= Pseudomona spp., asociado a parámet= ros físico químico en la estación seca y lluviosa en aguas subterráneas de la región de Azuero.

Se realizó comparación de la ocurrencia de P. aerugin= osa en época seca y época lluviosa de la región de Azuero. De igual manera se c= ompara parámetros físico químicos tales como alcalinidad, Cloro Residual, Conducti= vidad y pH y ver de manera gráfica que relación toma el crecimiento de la bacteri= a P. aeruginosa en base a los parámetros físico químicos y a la época en la cual fueron tomadas las muestras.

También se evaluó de manera exhaust= iva que los parámetros más relevantes para nuestro estudio fueron el Cloro Resi= dual y la conductividad, razón por la cual se comparó mediante gráficas, el crec= imiento de P. aeruginosa frente a Cloro Residual y Conductividad tomando en cuenta = las épocas para confirmar que tanto influían el crecimiento de la bacteria en estudio, para ambas provincias.        

Figura Nº 1. Crec= imiento de Pseudomona aeruginosa en época seca y época lluviosa de la Provincia de Herrera.

Figura Nº 2. Cre= cimiento de Pseudomona aeruginosa en época seca y época lluviosa de la Provincia de = Los Santos.

 

Con respecto a los resultados obtenidos se llega a observar que los valores de P. aeru= ginosa en cuanto a la época lluviosa fue alto su crecimiento para ambas provincias, mientras que en la estación seca el crecimiento fue menor en la provincia de Herrera, sin embargo, en la provincia de Los Santos permanece con valores significativos de igual manera altos a los de la época lluviosa.

Figura Nº 3. Comp= aración de niveles de Alcalinidad en época seca y época lluviosa de la Provincia de Herrera.

Figura Nº 4. Compa= ración de niveles de Alcalinidad en época seca y época lluviosa de la Provincia de= Los Santos.

 

En estas graficas muestran estadísticamente que los niveles de Alcalinidad para ambas provincias sobrepasan los valores máximos requeridos por la Norma de Calidad de Agua Potable DGNT-COPANIT 23-395-99 tanto en época lluviosa como seca.

Figura Nº 5. Comp= aración de niveles de Cloro Residual en época seca y época lluviosa de la Provincia= de Herrera.

Figura Nº 6. Comp= aración de niveles de Cloro Residual en época seca y época lluviosa de la Provincia= de Los Santos.

 

Estas graficas muestran estadísticamente que los nive= les de Cloro Residual para la provincia de Los Santos no cumplen con los valores máximos requeridos por la Norma de Calidad de Agua Potable DGNT-COPANIT 23-= 395-99, en lo que concierne a las épocas en estudio. Sin embargo, podemos señalar q= ue la Provincia de Herrera con respecto a este parámetro físico si cumplen con= los valores máximos requeridos por la Norma antes mencionada.=

Figura Nº 7. Comparación = de niveles de Conductividad en época seca y época lluviosa de la Provincia de Herrera.

Figura Nº 8. Com= paración de niveles de Conductividad en época seca y época lluviosa de la Provincia = de Los Santos.

 

 

Con respecto a los resultados obtenidos se llega a observar que los valores de conductividad para ambas provincias cumplen con= los valores máximos requeridos por la Norma de Calidad de Agua Potable DGNT-COP= ANIT 23-395-99 tanto en época lluviosa como seca.

Figura Nº 9. Comp= aración de niveles de pH en época seca y época lluviosa de la Provincia de Herrera.=

Figura Nº 10. Comp= aración de niveles de pH en época seca y época lluviosa de la Provincia de Los Santos.=

 

 

 

Figura Nº 11. Com= paración de Cloro Residual y Crecimiento de = P. aeruginosa en época seca y época lluviosa de la Provincia de Herrera.

 

Figura Nº 12. Comp= aración de Cloro Residual y Crecimiento de = P. aeruginosa en época seca y época lluviosa de la Provincia de Los Santos.

 =

Realizando comparación grafica de las provincias en estudio con lo que concierne a crecimiento vs cloro residual / época, ambas mantuvieron crecimiento en tanto en épocas lluviosa como en época seca. En = lo que respecta al cloro residual ninguna de las Provincias cumplía con los valores máximos requeridos por la Norma de Calidad de Agua Potable (0.8-1.5 mg/L) DGNT-COPANIT 23-395-99

Siendo la provincia de Los Santos d= onde se incide un alto crecimiento de P. aeruginosa ya que los niveles de cloro residual para esta provincia son= muy bajos a los niveles que la norma requiere. Sin embargo, en la Provincia de Herrera el crecimiento fue de mayor concentración en la época lluviosa mien= tras que en la época seca su crecimiento no fue elevado.

                Figura Nº 13. Comparación de Conductividad y Crecimiento de P. aeuroginosa en época seca y época lluvios= a de la Provincia de Herrera.

Figura Nº 14. Comp= aración de Conductividad y Crecimiento de P= . aeruginosa en época seca y época lluviosa de la Provincia de Los Santos.

 

En estas grafi= cas se muestra estadísticamente que las provincias en estudio con lo que concierne= a crecimiento vs conductividad / época, ambas mantuvieron crecimiento en époc= as lluviosa como en época seca, pero permaneciendo con niveles más elevados de crecimiento la provincia de Los Santos.

4   Conclusiones

Los niveles de crecimiento de P. aeruginosa en los pozos subterráneos de la Provincia de Los Santos, indican que es mayor en cantidades significativas en ambas épocas en comparación con la provincia de Herrera.

 

Se manifestó que en la época lluviosa presentó una mayor ocurrencia de P. aeruginosa <= /i>en comparación con la época seca, debido al incremento o actividad bacteriológ= ica en los acuíferos filtrado por las aguas externas que van hacia el pozo.  

 

Los parámetros fisicoquímicos se mantienen en este estudio constantes en las dos épocas de estudio, estas fueron: pH y conductividad en donde ambas se mantuvieron dentro de los valores máximos requeridos por la Norma de Calidad de Agua Potable DGNT-COPANIT 23-395-99.<= o:p>

 

Los parámetros fisicoquímicos con mayor importancia para nuestro estudio están el Cloro Residual y la conductividad. Siendo el cloro residual un parámetro clave para el control del crecimiento de P. aeruginosa. 

 

Concluimos que los niveles de cl= oro residual en ambas Provincias los valores máximos requeridos por la Norma de Calidad de Agua Potable DGNT-COPANIT 23-395-99, en lo que concierne a las épocas en estudio fueron<= /span>, encontrados valores aceptables.

 

 

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Galvín, R. 2006.Fisicoquímica y microbiología de l= os medios acuáticos: tratamiento y control de la calidad de las aguas. España. Ediciones Díaz de Santos. Consultada el: 26 de Junio de 2011. Disponible en= : http://books.google.com.pa/books?id=3Dk8bIixwJzY= UC&pg=3DPR13&lpg=3DPR13&dq=3DFisicoquimica+y+microbiologia+de+l= os+medios+acuaticos++tratamiento+y+control+de+la+calidad+de+las+aguas&s= ource=3Dbl&ots=3Dl1IrOBq7I1&sig=3DtISv7tfm43B5GU5X6XaUBll9qj0&h= l=3Des-419&sa=3DX&ei=3DEbXzT7rzIZOs8ASel-XxBg&ved=3D0CFEQ6AEwAQ= #v=3Donepage&q=3DFisicoquimica%20y%20microbiologia%20de%20los%20medios%= 20acuaticos%20%20tratamiento%20y%20control%20de%20la%20calidad%20de%20las%2= 0aguas&f=3Dfalse

 

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Gobernado, M. 2003.Identificacion bacteriana. Consultada el: 11 de J= ulio de 2012. Disponible en : http://www.elsevier.e= s/sites/default/files/elsevier/pdf/28/28v21nSupl.2a13059086pdf001.pdf

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Herrera, J., Sánchez. 2005.Analisis de la calidad microbiológica del agua potable provenientes de las redes de distribución del área metropolita= na y la chorrera. Trabajo de graduación. Universidad de Panamá. Panamá. Págs. 15= -17 Consultada el: 19 de mayo de 2012.

 

 

 

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Invest. pens. crit. (ISSN 1812-3864)

Vol. 7, No. 2, mayo- agosto 2019    

pp. 05-20

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20

 

34

 

Invest. Pens. Crit. (ISNN 1812-3864; e= ISNN 2644-4119)

Vol. 7, No. 2, Mayo- Agosto 2019    

pp. 19-34

______________________________________= ________________________________________

19

 

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