MIME-Version: 1.0 Content-Type: multipart/related; boundary="----=_NextPart_01D5C640.2C3C17C0" Este documento es una página web de un solo archivo, también conocido como archivo de almacenamiento web. Si está viendo este mensaje, su explorador o editor no admite archivos de almacenamiento web. Descargue un explorador que admita este tipo de archivos, como Windows® Internet Explorer®. ------=_NextPart_01D5C640.2C3C17C0 Content-Location: file:///C:/8472D2FA/04ALEXISDELACRUZ.htm Content-Transfer-Encoding: quoted-printable Content-Type: text/html; charset="windows-1252" Microbiologia ambiental de suelo

Evaluación de Microorganismos de

Algunos Suelos Procedentes de la

Región de Azuero

 

Alexis De La Cruz = L.1, 2*

1Docente e investigador de la Escuela de Biología, Facultad de Ciencias Naturales, Exactas                      y Tecnología, Centro Regional Universitario de Azuero, Universidad de Panamá.<= /p>

2Profesor-Investigador, Centro de Estudios e Investigaciones en Ciencias Agrarias                            y Ambientales, Centro Regio= nal de la USMA en Azuero, Chitré, Panamá.

*Autor para correspondencia. Emai= l:  alexisdelac@gmail.c= om =

 

Recibido: 10 de enero de 2018

Aceptado: 03 de abril de 2018

­________________________________= ______________________________________________

Resumen

La cuenta viable de microorganismos del suelo puede realizarse por la técnica de cuenta en plac= a o la técnica del número más probable (NMP). Los principios fundamentales de e= stas técnicas son dispersión de una muestra en un diluyente apropiado, distribuc= ión en un medio apropiado de crecimiento, incubación bajo condiciones óptimas, = y conteo de las colonias desarrolladas. La producción microbiológica de CO2 en el su= elo puede ser determinada incubando el suelo en jarras, el objetivo de este proyecto consistió en Caracterizar  los microorganismos existentes de tres tipos de suelos: Agrícola, Ganadero y Forestal, a través de múltiples técnicas de microbiología. Se seleccionará = un área preferiblemente rectangular de aproximadamente 10x5 metros, sobre la c= ual se empleara un muestreo en forma zigzag en donde se tomaran 5 submuestras de aproximadamente 10g de cada una (que se depositan en bolsas plásticas de 1 = lb), a 20 cm de profundidad, para luego homogenizarla en una sola muestra. Una v= ez realizada el procedimiento las muestras son llevadas a la Unidad de investigación del Centro Regional Universitario de Azuero. Al finalizar este proyecto de investigación hemos llegado a la conclusión de que la Hipótesis= de investigación fue aceptada ya que se presenta una mayor ocurrencia y divers= idad de microorganismos en uno de los tres suelos evaluados.

Palabras Clave: Suelo, Microorganismos, Zigzag, homogenización y diversidad.

 

 

Abstract

The viable count of microorganisms in the soil may be performed by plate count technique or most probable number technique (MPN). The fundamental principl= es of these techniques are dispersing a sample in an appropriate diluent, distribution in an appropriate growth medium, incubation under optimal conditions, and counting the colonies developed. Microbial production of CO= 2 in the soil can be determined by incubating the floor akimbo, the aim of this project was to characterize the microorganisms of three types of soil: Agricultural, Livestock and Forestry, through multiple techniques of microbiology. one preferably rectangular area of ​​about 10x5 meters, on which sampling is employed as zigzag where five subsamples = of about 10g of each (which are deposited in plastic bags 1 lb) were taken are selected, a 20 cm deep and then homogenize in a single sample. Once the procedure samples are taken to the Research Unit of the University Regional Center Azuero. Upon completion of this research project we have concluded t= hat the research hypothesis was accepted as an increased occurrence and diversi= ty of microorganisms in one of the three soils tested is presented<= /span>

Keywords: Soil, Microorganism, Zigzag, Homogenize and Diversit.

 

 

1   Antecedentes y Justificación

 

El análisis de suelo, es una importante herramienta que bien usada sirve para el diagnóstico de suelo, p= ara determinar las propiedades edáficas así como su estado de fertilidad, lo que permitirá recomendar sobre la fertilización y verificar avances en la degra= dación de los suelo. (Villareal y Name, 1996). Los ambientes terrestres son heterogéneos y discontinuos, ya que contienen una gran cantidad de microorganismos. Las comunidades microbianas varían en cuanto a la profundi= dad y tipo de suelo, en el horizonte superficial se tiene muchos microorganismos que en otros horizontes, también las comunidades pueden variar de un sitio a otro, debido a que coexisten grandes comunidades microbianas de suelo, de a= llí que sea necesario tomar más de una muestra para obtener un análisis microbi= ano. La respiración del suelo se define como la producción total de CO2, por uni= dad de área y de tiempo, y se debe a la respiración de organismos edáficos, raí= ces, hifas micorrícicas, y en menor extensión, a la oxidación bioquímica de los compuestos de carbono (Lloyd y Taylor, 1994). La respiración del suelo constituye un evento central de los cambios ecológicos globales debido a su papel controversial en los procesos de calentamiento global ya que puede determinar si un ecosistema dado se comporta como fuente o sumidero de CO2 (Jassal et al., 2007).La catalasa forma parte de los sistemas de des-toxificación de las células animales y vegetales, y de bacterias aerobi= as y anaerobias facultativas. La reacción específica que cataliza es la ruptura = del H2O2 para formar agua y oxígeno. El H2O2 se forma en el transporte de electrones de la cadena respiratoria y en ciertas reacciones de hidroxilaci= ón y oxigenación (Alef y Nannipieri, 1998). La catalasa se relaciona con la actividad microbiana del suelo por ser una enzima intracelular presente en microorganismos aerobios y en la mayoría de los anaerobios facultativos. Durante los procesos biológicos (metabolismo) se generan especies químicas conocidas como radicales libres, los cuales se caracterizan por presentar un electrón desapareado y por ser muy reactivas. Entre estos radicales, las especies reactivas derivadas del oxígeno (EROS) resultan de gran interés de= bido a su estructura birradical y al gran número de procesos que las generan y en los que pueden verse involucradas. Se han empleado muchos métodos para determinar la actividad de la catalasa, los cuales miden la cantidad de oxí= geno liberado (O2) o el H2O2 remanente. El oxígeno puede cuantificarse por volumetría de gases o cromatografía de gases. El H2O2 se determina por volumetría o colorimetría (García et al., 2003).          Castro y Flores (2014), realizaron estudios con el obje= tivo de determinar la actividad, densidad microbiana y físico-química de tres suelos, con distintos sistemas de manejo agrícola, durante los meses de abr= il y mayo en el Ejido, corregimiento de Santa Ana, provincia de los Santos, el c= ual aislaron  Echerichia coli, mediante= la técnica de cultivo de enriquecimiento y selección por medios específicos. L= os resultados encontrados en esta investigación, no arrojan diferencias significativas (p˃0,05), respecto a la densidad microbiana en los distintos manejos ag= rícolas (alternativa orgánica, convencio= nal y casa de vegetación). En cuanto a la actividad microbiana, la enzima deshidrogenasa presento significancia solamente para = la alternativa orgánica con una X=3D1,54, y respecto a la respiración no se presentaron diferencias entre los tratamientos agrícolas. Brito (2014), rea= lizo un estudio con el objetivo de aportar al conocimiento del control de las enfermedades del suelo realizando la identificación molecular de bacterias = en suelo agrícola tratado con el agente químico: 1-3 Dicloropropeno al 45% y Cloropicrina al 55%, y comparo su efecto versus un suelo sin la aplicación = del mismo. Las muestras de suelo fueron recolectadas en la finca productora de flores “Latitud Cero”. Para este estudio se evaluaron las poblaciones de bacterias del suelo en cultivo de Hypericum (familia de Hypericaceae), como resultado, se observó que el agente químico biosida destruyó gran parte de = la biodiversidad de bacterias en el suelo estudiado y a su vez disminuyó la población total. Las bacterias identificadas por medio de técnicas molecula= res en el tratamiento antes del biosida no fueron previamente descritas en las bases de datos siendo nuevos descubrimientos que un futuro deberán determin= arse y clasificarse, mientras que el tratamiento después del biosida fueron: Bacillus megatherium, Bacillus cereus, Bacillus flexus, Bacillus bombysepti= cus y  Pseudomonas flourescens.  Esta investigación o estudio servirá co= mo una caracterización de microorganismos presente en los suelos, ya que esto permitirá conocer qué tipo de suelos es más acto para la siembra de cultivo= s,  el pastoreo de animales y el nacimiento= de reservas forestales, además comparar con otros tipos de suelos las alteraci= ones que pueda llegar a tener y corregirlas mediante los datos obtenidos en este estudio brindará información valiosa a los agricultores, ganaderos y a los guarda bosques. Promoverá el desarrollo de una adecuada escogencia de los suelos. Comprobara  si las condicio= nes de estos suelos es acta para el cultivo y el pastoreo. El objetivo de esta investigación fue, caracterizar  los microorganismos existentes de tres tipos de suelos: Agrícola, Ganadero y Forestal, a través de múltiples técnicas de microbiología.

 

 

2   Materiales y métodos

Diseño del estudio

Para este trabajo se tomaron en cuenta tres suelos bajo las acciones ganadera, agrícola y bosque forestal, = cada uno de ellos fue monitoreado en  zigzag en donde se tomaran 5 submuestra= s y luego homogenizarla en una sola muestra. Para su debida caracterización y cuantificación de microorganismos de los tres suelos.

Ubicación del estudio

Las muestras de suelo fueron tom= adas en tres puntos de la región de Azuero, para esta investigación. Los suelos fueron monitoreados en el IDIAP en La Villa de Los Santos para el suelo agrícola, en la finca de Santa Ana de Los Santos para el suelo ganadero y L= os Cerritos de Los Pozos para el suelo de bosque forestal.

Variables

Dependiente: 3 tipos de suelos (agrícola, ganadero y bosque forestal) Independiente:   Microorganismos.

 

 

Hipótesis

Hay mayor ocurrencia y diversida= d de microorganismos en uno de los suelos evaluados.

 =

Recole= cción de las muestras

Se seleccionará un área preferiblemente rectangular de aproximadamente 10x5 metros, sobre la cual se empleara un muestreo en forma zigzag en donde se tomaran 5 submuestras de aproximadamente 10g= de cada una (que se depositan en bolsas plásticas de 1 lb), a 20 cm de profundidad, para luego homogenizarla en una sola muestra.

Una vez realizada el procedimiento las muestras son llevadas a la Unidad de investigación del Centro Regional Universitario de Azuero.

Proceso de laboratorio: (Estos procedimientos son aplica= dos a los tres tipos de suelo)

 

Técnic= a de dilución Seriada y Esparcido<= /o:p>

Se pesan 10 g de cada una de las muestras de suelo, que se depositan en una botella de vidrio contenida de agua destilada estéril, la cual se homogeniza con la muestra de suelo.

Homogenizada la solución se procede a aplicar la dilución seriada en 4 tubos de ensayo q= ue contiene agua destilada, el cual se tomara 1 ml de la solución, el proceso = de dilución se da de esta forma, se parte de la dilución  0.1 de la 0.01, de la 0.01 a la 0.001, = de la 0.01 a la 0.0001.

Luego del proceso de dilución con una micropipeta se toma 0.1 microlitro, esto se sembraran en Agar Saburaud (AS), Agar ENDOLES (AE), Agar Cetrimide (AC) y A= gar Plate Count (PC), por medio de la técnica de esparcido

Culminado el proceso de  siembra se incuban a temperatura de 30°C los platos con AS, a 26°C los platos con PC y a 37°C los platos con AE y AC. En un periodo de 5 días en el caso de hongos y levadura= s, y 24 horas en el caso de bacterias. Para la observación de resultados.

 Técnica de microscopia y Tinción de Gram=

Pasa el periodo previo de incubación, se realiza una cuantificación y caracterización de hongos y colonias de bacterias crecidas en cada medio, l= a tinción de Gram y verificación a través de la técnica de microscopia de la siguiente manera:

Tinción de Gram o diferencial en el AE, AC y PC, se real= iza el frotis, con una pequeña gota de agua destilada, inoculando la cepa al portaobjeto con movimiento circular por unos minutos, secándola en el meche= ro.

Colocar una gota de violeta cristal por un minuto, y  lavar con agua destilada.

Agregar una gota de lugol por 1 minuto, lavar con agua destilada

Decolorar como sigue se hace con alcohol decolorante por= 0 s, y lavar con agua destilada.

Por último se le agrega la sustancia de contraste que es safranina, para teñir las bacterias que pierden el cristal violeta, por 15 = s o 1 minuto, se lava y se deja secar.

Observar al microscopio.

Tinción para hongos AS, se agrega una pequeña gota en el portaobjeto si las esporas son de color, de no ser así se agrega lacto feno= l.

Se toma las esporas del hongo a identificar y se distribuyen en la gota de agua.=

Se coloca el cubre objeto sobre el inóculo

Se observan al microscopio.

 

Medición del CO2

Incuba= ción de la muestra de suelo en Erlenmeyer.

En un Erlenmeyer se depositan 10 ml de agua destilada como nuestro control, al cual colocamos un tubo de hidróxid= o de sodio suspendido dentro del mismo Erlenmeyer.

En dos Erlenmeyer agregamos 10 gramos de suelo a el cual se rotulara como (Erlenmeyer(A) y Erlenmeyer (B))

En el Erlenmeyer (A) se coloca un tubo con hidróxido de sodio y en el Erlenmey= er (B) colocamos un tubo con sacarosa= . Luego los Erlenmeyer con suelo y el Erlenmeyer control lo colocamos por 7 días en= el horno a temperatura ambiente.

Siembra por esparcido:

  para dilui= rlo en 90 ml de agua destilada estéril de la cual se hicieron 3 diluciones (desde = la 10-2 hasta la 10-4)  en medio de cultivos:

Titulación:

7 días después de haber montado el sistema de respiración de suelo Animal, se procede a cuantificar la producc= ión de CO2 y la medición de la actividad respiratoria.

Teniendo en cuenta la siguiente ecuación:

Na2CO3 + H2O + OH= - + BaCl2à NaCl + BaC= O2 + HCl + BaCl2+ HCO3 + NaCO3<= /o:p>

Asi pues:

CO2 + 2NaOHà Na2CO3 + H2O=

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Se evaluó el control con 100 ml de = HCl; el suelo sin Sacarosa; y el suelo con sacarosa.

A las muestras se le añadió Fenoftaleína como indicador de cambio de color al ser titulado con HCl.

 

 

Para después establecer la siguiente ecuación:                                            

 <= /span>C-  

 

 

Activación de la catalasa en el suelo

 

Preparación de la muestra de suelo

Muestra:

Se pesa 0,5 g del suelo húmedo en un Erlenmeyer y se añade 40 ml de agua destilada, se tapa y se comienza agitar  por 30 minutos en agitador rotatorio.

Luego = de los 30 minutos se  añadió 5 ml de H= 2O2  y se comenzó agitar nuevamen= te durante 10 minutos exactos en agitador. Para la reacción enzimática y la estabilización del peróxido de hidrogeno remanente se adiciona 5 ml de H2SO4 1,5 M y filtramos 25 ml.

 

Control:  <= /o:p>

Se prepara de igual manera que la muestra pero sustituye= ndo los 5 ml de H2O2  por igual volumen de agua destilada.

De igual manera se le adiciono 5 ml de H2SO4 1,5 M aunqu= e no se le haya adicionado el peróxido de hidrogeno. Se filtran 25 ml.

Blanco sin suelo:

Se agregan 40 ml de agua destilada en un Erlenmeyer.

Se vierten 5 ml de H2O2= Y 5 ml de H2SO4 1,5 M obteniendo una solución de H2<= /sub>O2 8,8 ml (este volumen de líquido contiene un total de 0,44 m moles de H= 2O2). Se filtran 25 ml.

 

Evaluación de la C= atalasa

    Titulación:

Cada una de las muestras se titulan con Permanganato de Potasio KMnO4  0,01 M, agitando continuamente la disolu= ción mientras se está titulando.  <= /o:p>

 

El punto final de cada valoración es señalado por: (cada muestra se le toma el tiempo de titulación).

 

Muestra: Se termina su titulación por la incorporación al añadir la gota.

Control: se señala con la aparición de un color rodado permanente. 

Blanco: su titulación inicia con la aparición de un color rosado y termina al cambi= ar a transparente.

 

Luego de titular todas las muestras se realiz= an los cálculos pertinentes para la evaluación de catalasa.<= /p>

 

 

3   Resultados y Discusión

Parte I: Caracterización de los suelos

 


Figura N°1: Eje de las Y=3D Suelo agrícola (naranja), suelo de Bosque forestal (amarillo), suelo ganadero (verde). Eje de las X=3D Medios de cultivos (Agar ENDOLES, Agar Cetrimide, Agar plate count, Agar Tripticasa de soja, Agar Extracto de malta).

 En la siguiente grafica se presenta el crecimiento de las diluciones  semb= radas en los cinco medios de cultivo utilizados para la elaboración de este proye= cto en donde el suelo que presento un mayor crecimiento en 3 de los 5 medios de= cultivo fue el suelo agrícola en los medios Agar Cetrimide, Agar Plate Count, Agar Extracto de Malta, seguido en agar ENDOLES y Agar Tripticasa de Soja esto se puede explicar ya que el suelo agrícola es un suelo en el cual dominan más = las bacterias que los hongos en donde nuestros resultados presentaron un crecimiento equitativo entre hongos y bacterias. Seguidamente el suelo de bosque forestal presenta el mayor crecimiento en la siembra de diluciones en los medios  de cultivo Agar ENDOLES= y Agar Tripticasa de Soja, y crecimiento bajo en los medios Agar Cetrimide, A= gar Plate Count, Agar Extracto de Malta lo que explica que en estos tipos de su= elos los hongos se encuentran en mayor biomasa que las bacterias, pero en nuestro caso hubo mayor crecimiento de coliformes que de hongos debido a que el sue= lo fue tomado de un área cerca del río lo que puede explicar el incremento de coliformes ya que diversos factores pueden influir como el depósito de mate= ria fecal a lo largo del río. Y por último el Suelo Ganadero presento un alto crecimiento en las diluciones sembradas en Agar Cetrimide, Agar Plate Count, Agar Extracto de Malta presentó un bajo crecimiento en los medios  de Cultivo Agar ENDOLES y Agar Triptica= sa de Soja,  y la literatura nos dice que= estos suelos el crecimiento de Bacterias coliformes es mayor que el de hongos, pe= ro nuestros resultados arrojan un mayor crecimiento de levaduras y bajo crecimiento de bacterias coliformes.

 

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Fig.Nº2: Crecimiento en Agar Cetrimide y respectivas diluciones en cada suelo; A- Suelo Agrícola (A.1: Dilución 10-1, A.2: Dilución 10-2, A.3: Dilución 10-3);  B- Suelo Ganadero (B.1: Dilución 10-1, B.2: Dilución 10-2, B.3: Dilu= ción 10-3); C- Suelo Forestal (C.1: Dilución 10-1, C.2: Dilución 10-2, C.3: Dilu= ción 10-3

 

 

 

 

 

 

 

Fig. Nº3: Crecimiento en Agar Tripticasa de S= oja y respectivas diluciones en cada suelo; A- Suelo Forestal (A.1: Dilución 10= -1, A.2: Dilución 10-2, A.3: Dilución 10-3);  B- Suelo Agrícola (B.1: Dilución 10-1, B.2: Dilución 10-2, B.3: Dilu= ción 10-3); C- Suelo Ganadero (C.1: Dilución 10-1, C.2: Dilución 10-2, C.3: Dilu= ción 10-3).

 

 

 

 

 

 

Fig. Nº 4: Crecimiento en Ag= ar Plate Count y respectivas diluciones en cada suelo; A- Suelo Agrícola  (A.1: Dilución 10-1, A.2: Dilución 10-2= , A.3: Dilución 10-3);  B- Suelo Ganadero = (B.1: Dilución 10-1, B.2: Dilución 10-2, B.3: Dilución 10-3); C- Suelo Forestal (= C.1: Dilución 10-1, C.2: Dilución 10-2, C.3: Dilución




Fig.Nº5: Crecimiento en Agar Extracto de Ma= lta y respectivas diluciones en cada suelo; A- Suelo Agrícola  (A.1: Dilución 10-1, A.2: Di= lución 10-2, A.3: Dilución 10-3);  B- Suelo Ganadero (B.1: Dilución 10-1, B.2: Dilución 10-2, B.3: Dilución 10-3); C- Suelo Forestal (C.1: Dilución 10-1, C.2: Dilución 10-2, C.3: Dilución 10-3).

 

 

 

 

 

 

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Fig.Nº6: Crecimiento en Agar ENDOLES y respectivas diluciones en cada suelo; A- Suelo Forestal (A.1: Dilución 10-1, A.2: Dilución 10-2, A.3: Dilución 10-3);  B- Suelo Agrícola (B.1: Dilución 10-1, B.2: Dilución 10-2, B.3: Dilución 10-3); C- Suelo Ganadero (C.1: Dilución 10-1, C.2: Dilución 10-2, C.3: Dilución 10-3).

Medición del CO2

Respiración del suelo por medida del CO2 atrapado en una disolución de NaOH.=

Cuadro N° 2: RESPIRACIÓN DE TRES TIPOS DE SUELO CONSUMIDOS EN HCL EN EL ÁREA DE AZUERO. AÑO: MAYO Y JUNIO DE 2016.

Tipo de suelo

ml de HCl consumidos

Ganadero

33,0

Agrícola

43,3

Bosque forestal

31,2

Blanco

51,7

N= ota: Estimación del CO2 desprendido durante la incubación del suelo en un sistema cerrado. El CO2 es atrapado en una disolución de NaOH que es posteriormente valorado con HC= l.

 

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Figura No.7= : RESPIRACIÓN DEL CO2 DEL SUELO TITULADO CON HCL CONSUMIDO. EN EL = ÁREA DE AZUERO. AÑO: MAYO Y JUNIO DE 2016.

 

Figura No.8 POR= CENTAJE DE C-CO2 DESPRENDIDO EN TRES TIPOS DE SUELO.EN EL ÁREA DE AZUERO. AÑO: MAYO Y JUNIO DE 2016.

 Los resultados obtenidos podemos observa= r  que el CO2 absorbido y despr= endido del suelo  el más sobresaliente fue= el suelo de bosque forestal con 34,1x10-3mg C-CO2 kg-1 suelo seco día-1 ya que tiene una estimació= n de la biomasa microbiana realmente activa. Mientras que el suelo agrícola tuvo= una menor liberación de CO2 con13, 4x10-3mg C-CO2 kg-1 suelo seco día-1, a pesar de que el suelo ganadero también presento un elevado desprendimiento = de CO2 aunque es considerado con menos actividad microbiana ya que = es pisado muchas veces por el ganado lo cual disminuye su porosidad.

 

Determinación de la actividad catalasa del suelo.

Evaluación de la catalasa

Cuadro N° 3: PRUEBA DE CATALASA EN TRES SUELOS TRATADOS EN LA REGIÓN DE AZUERO. AÑO: MAYO Y JUNIO DE 2016.

Tipo de suelo

Tratamiento

Consumo final (ml)

Tiempo consumido (segundos)<= /o:p>

 

Muestra

5,2

6

Ganadero

Control

2,2

5

 

Blanco

2,7

7

 

Muestra

8,2

10

Agrícola

Control

2,0

5

 

Blanco

5,1

6

 

Muestra

6,1

15

Bosque forestal=

Control

2,1

6

 

Blanco

2,4

8

<= o:p> 

=

F= igura No.9: COMPARACIÓN DE LOS TRATAMIENTOS DE TRES TIPOS DE SUELO CONSUMIDO POR KMnO4.AÑO: MAY= O Y JUNIO DE 2016.


Se obtuvo en el suelo ganadero 2,7 ml de KMnO4 gastado en= la valoración del blanco sin suelo y con H2O2, 5,2 ml de= KMnO4 gastado en la valoración de la muestra con suelo, H2O2 y H2SO4, y 2,2 ml de KMnO4 gastado en la valoración del control y sin  H2O2 correspondiente a cada muestra de suelo. En el suelo agrícola 5,1 ml = de KMnO4 gastado en la valoración del blanco sin suelo y con H= 2O2, 8,2 ml de KMnO4 gastado en la valoración de la muestra con suelo, H2O2 y H2SO4, y 2,0 ml de KMnO4 gastado en la valoración del control y sin  H2O2 correspondie= nte a cada muestra de suelo.

En el suelo de bosque forestal 2,4 ml de KMnO4 gastado en= la valoración del blanco sin suelo y con H2O2, 6,1 ml de KMnO4 gastado en la valoración de la muestra con suelo, H2<= /sub>O2 y H2SO4, y 2,1 ml de KMnO4 gastado en la valoración del control y sin  H2O2 correspondiente a cada muestra de suelo.

La muestra del suelo agrícola consumió mucho más KMnO4, ya que no se encuentra la enzima catalasa que provoca la descomposición del H<= sub>2O2 en H2O y O2 y el H2O2 que perma= nece inalterado después que tuvo lugar la reacción enzimática. Mientras que el blanco para los tres suelos estudiados debería haber consumido más ya que e= ste no presentaba el suelo.

 

4   Conclusión

Al finalizar esta investigación hemos llegado a la conclusión de que la Hipóte= sis de investigación fue aceptada ya que se presenta una mayor ocurrencia y diversidad de microorganismos en uno de los tres suelos evaluados.

La aplicación de las técnicas de Microscopia, tinción de Gram y esparcido predispuestas para este proyecto de investigación fueron efectivas a la hor= a de identificar los microrganismos existentes en los tres tipos de suelo (Agríc= ola, Ganadero y Forestal).

La cuantificación de los  microorganis= mo encontrados en los tres tipos de suelo (Agrícola, Ganadero y Forestal), en donde el suelo que obtuvo mayor crecimiento fue el agrícola presentando una alta incidencia en la siembra de diluciones en 3 de los 5 medios utilizados Agar ENDOLES, Agar Cetrimide, Agar Plate Count, Agar Extracto de Malta y Ag= ar Tripticasa de Soja.

La comparación de la activación de la catalasa fue mayor en el Suelo Agrícola.=


 

5   Bibliografía

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BRITO,= F. (2014). Identificación por fenotipo, cuantificación y técnicas moleculares de bacterias a dos profundidades en el cultivo ¨Hypericum¨ antes y después del tratamiento de 1-3 Dicloropropeno y Cloropicrina. Tesis de grado presentada como requisito para la obtención del título de Ingeniero en Agro-empresa. UNIVERSIDAD SAN FRANCISCO DE QUITO. Quito, mayo 2014.

CASTRO= , C. Y FLORES, A. (2014). Determinación = de la actividad, densidad microbiana y físico-química en tres suelos, bajo difere= ntes sistemas de manejo agrícola, durante los meses de abril y mayo en el Ejido, corregimiento de Santa Ana, Provincia de Los Santos. Tesis de investigación de la escuela de Biología, Centro Regional Universitario de Azuero.

CUEVAS, M., ESPINOSA, G., ILIZALITURRI, C. Y MENDO= ZA, A. (2012). Métodos ecotoxicológicos= para la evaluación de suelos contaminados con hidrocarburos. Instituto Nacio= nal de Ecología (INE). Universidad Veracruzana. p. 38.

GAR= CÍA, C., GIL, F., HERNÁNDEZ, T., TRASAR, C. (2003). Técnicas de Análisis de Parámetros Bioquímicos en suelos. Medid= a de Actividades Enzimáticas y Biomasa Microbiana. Editorial Mundi-Prensa. Españ= a

IBÁÑEZ, J. (2008). ¿Qué es la Fertilidad del Suelo?: Fertilidad Física, Química y Biológica. Un Universo invisible bajo nuestros pies: Los suelos y la vida. Obtenido el 4 = de junio del 2016 en: http://www.madrimasd.org/blogs/universo/2008/01/29/83481= .

JAS= SAL, T., BLACK, T., CAI, K., MORGENSTERN, Z., LI, D., GAUYMONT-GUAY Y NESIC. Z. (2007). Components of ecosystems respiration and an estimate of net primary productivity of an intermediate-= aged Douglas-Fir stand. Agric. For. Meteorol. 144: págs. 44-57.

LLO= YD, J. Y A. TAYLOR. (1994). On the temperature dependence of soil respiration. Functional Ecology 8: págs. 315-323. <= /p>

ORGANIZACIÓN DE LAS NACIONES UNIDAS PARA LA ALIMENTAC= IÓN Y LA AGRICULTURA (UNESCO). (2016). Degradación del Suelo. Ciudad del Saber, Panamá.

RAMOS, J. (2010). TÉCNICAS DE MUESTREO PARA MANEJADORES DE RECURSOS NATURALES. Unidad 6 Los Microorganismos de suelo. Obtenido el 10 de julio del 2016 de http://www2.inecc.gob.mx/publicaciones/libros/429/organismos.pdf.

VÁSQUEZ, J., MACÍAS, F. Y MENJIVAR, J. (2013). Respiración del suelo según su uso y su relación con algunas formas de carbono en el Departamento del Magdalena, Colombia. BIOAGRO versión impresa ISSN 1316-3361. Obtenido e= l 4 de junio del 2016 en: www.scielo.org.ve/scielo.php?script=3Dsci_arttext&= ;pid=3DS1316.

VIL= LAREAL, J. Y NAME, B. (1996) Monitoreo de c= ambios en la fertilidad de suelos por medio de análisis de laboratorios. Revis= ta Agronomía Mesoamericana. Págs. 301-309.=


 

 

 

 

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

Vol. 6, No. 1, enero-abril  2018     <= /p>

pp. 51-64

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

Vol. 6, No. 1, enero-abril  2018  =   

pp. 51-64 <= /p>

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