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ENUMERATION OF HYDROCARBON-DEGRADING BACTERIA BY MOST
               PROBABLE NUMBER USING RESAZURIN AS INDICATOR
            Jubany I.1, Calderer M. 1, González C. 1, Corcho D. 2, Muelle A. 2 ,Martí V.1,3
            1CTM,  Technological Center Foundation, Environmental Technology Area (UPC), Av. Bases de Manresa, 1, E-08242 Manresa (Spain)
            2 INTRAVAL S.L. Llull, No. 109, 2nd floor, E-08005 Barcelona (Spain)
            3Department of Chemical Engineering, Technical University of Catalonia (UPC), ETSEIB, Av. Diagonal, 647, E-08028, Barcelona (Spain)




   INTRODUCTION
Enumeration of bacteria is very useful in the biological soil treatment in order to detect and quantify the
microorganisms involved in the bioremediation. One of the most widely used methods is the most
probable number (MPN) technique. A new MPN method for enumeration of hydrocarbon-degrading
bacteria (HDB) was developed in this work using 96-wells microtiter plates for incubation, commercial
                                                                                                                                                               Figure 1. Chemical change of resazurin and
diesel as the carbon source and the use of resazurin as activity indicator. The method was a modification                                                                resulting colour change.
of the work by Wren and Venosa (1996).
Resazurin is an oxazine which upon reduction changes colour from blue to pink due to the loss of an oxygen atom loosely bound (see Figure 1).

   MATERIALS AND METHODS
  Developed method: MPN with resazurin and diesel                                                            Bacteria enumeration using plate count:
  For each sample, tenfold serial dilutions were performed in a saline                                       Plate count was performed as an indicator of the total
  buffer solution (8.5 g/L NaCl). 96-wells microtiter plates were                                            heterotrophic bacteria as described in APHA (1998). Two
  inoculated by adding 20 μL of each dilution (8 wells per dilution) to                                      different growth substrates were used. A nutrient broth was
  180 μL of mineral medium (2.0 g/L NH4Cl, 0.89 g/L KH2PO4, 1.25 g/L                                         used for pure cultures enumeration and R2A Agar was used
  Na2HPO4, 0.6 mg/L FeCl3). 10 μL of diesel were added to each well as                                       for environmental samples. Plates were incubated for 7 days
  a sole substrate. Each sample was tested in duplicate. Plates were                                         at 28 ºC. After this period, only plates having 30 to 300
  incubated at 25 ºC for 21 days and then, 50 μL of resazurin (4.5 mg/L)                                     colonies were considered for couting. All samples were
  were added to each well. Positive wells (pink coloured) were scored                                        tested in duplicate
  after 48 h. The MPN was calculated.
                                                     Pure cultures                                                                   Environmental samples
        Tested
        samples:                 Pseudomonas putida                      Escherichia coli                Compost from municipal wastewater                        Soil from hydrocarbon-
                                     (CECT 845)                            (CECT 101)                    treatment sludge                                         contaminated site
                                        HDB                                       No HDB                 Low HDB content                                          High HDB content


   RESULTS
   Table 1. Results obtained with pure cultures (p=0.5) in cells/g (dry matter)                       • Same count of bacteria with plate count and MPN with the nutrient
                                               P. putida                          E.coli              broth were obtained
     Method          Medium            Count     Min       Max       Count        Min         Max     • The same count of bacteria for P. putida was obtained with the
   Plate count Nutrient broth 1.75·108 1.67·108 1.82·108 2.74·108 2.23·108 3.25·108                   developed method and the plate count.
                  Nutrient broth 2.60·108 1.01·108 6.69·108 6.21·108 2.42·108 1.60·109                • No E. coli was detected with the developed method (no false
      MPN
                      Diesel       1.22·108 4.74·107 3.13·108              Not detected               positive responses were detected)

   Table 2. Results obtained with environmental samples (p=0.5) in cells/g (dry matter)               • Low amount of HDB in the compost
                                  Compost sample             Hydrocarbon-contaminated soil            sample was detected as expected.
    Method      Medium         Count      Min        Max       Count         Min            Max       • Similar count of bacteria in the
  Plate count R2A Agar 1.10·1010 9.10·109 1.09·1010 6.60·107 2.590·107                     7.30·107   hydrocarbon-contaminated soil was                       Figure 2. MPN in 96-well microtiter plates.
      MPN         Diesel    1.57·103 6.11·102 7.03·103 2.59·107 1.01·107                   6.65·107                                                           A. P. putida in nutrient broth. B. P. putida in
                                                                                                      obtained with both methods,                              diesel medium and resazurin. C. E. coli in
                                                                                                      indicating that all bacteria are HDB.                           diesel medium and resazurin



  CONCLUSIONS
   The developed MPN method was based on three aspects: (1) the use of 96-wells microtiter plates for incubation, (2) the use of commercial diesel as
   the carbon source, and (3) the use of resazurin as activity indicator.

   The method resulted to be appropriate when testing with pure cultures since bacteria counts where comparable with counts obtained with the
   plate count method. It was confirmed that resazurin did not react with diesel which could have caused false positives.

    Very different HDB was found in compost and contaminated soil samples indicating that the bacteria in the contaminated soil were already adapted
   to hydrocarbons.

    These results demonstrated that the developed method could be used for the enumeration of hydrocarbon-degrading bacteria in the field of
   biological treatment of hydrocarbon-contaminated soil where, usually, amendments based on compost are used.

   REFERENCES
• Wrenn , B.A. and Venosa A.D. (1996). Selective enumeration of aromatic and aliphatic hydrocarbon degrading bacteria by most-probable-number procedure. Canadian Journal of Microbiology, 42(3), 252-258
• APHA (1998). Standard methods for the examination of water and wastewater. Washington: American Public Health Association.

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Poster consoil 2010 dh

  • 1. ENUMERATION OF HYDROCARBON-DEGRADING BACTERIA BY MOST PROBABLE NUMBER USING RESAZURIN AS INDICATOR Jubany I.1, Calderer M. 1, González C. 1, Corcho D. 2, Muelle A. 2 ,Martí V.1,3 1CTM, Technological Center Foundation, Environmental Technology Area (UPC), Av. Bases de Manresa, 1, E-08242 Manresa (Spain) 2 INTRAVAL S.L. Llull, No. 109, 2nd floor, E-08005 Barcelona (Spain) 3Department of Chemical Engineering, Technical University of Catalonia (UPC), ETSEIB, Av. Diagonal, 647, E-08028, Barcelona (Spain) INTRODUCTION Enumeration of bacteria is very useful in the biological soil treatment in order to detect and quantify the microorganisms involved in the bioremediation. One of the most widely used methods is the most probable number (MPN) technique. A new MPN method for enumeration of hydrocarbon-degrading bacteria (HDB) was developed in this work using 96-wells microtiter plates for incubation, commercial Figure 1. Chemical change of resazurin and diesel as the carbon source and the use of resazurin as activity indicator. The method was a modification resulting colour change. of the work by Wren and Venosa (1996). Resazurin is an oxazine which upon reduction changes colour from blue to pink due to the loss of an oxygen atom loosely bound (see Figure 1). MATERIALS AND METHODS Developed method: MPN with resazurin and diesel Bacteria enumeration using plate count: For each sample, tenfold serial dilutions were performed in a saline Plate count was performed as an indicator of the total buffer solution (8.5 g/L NaCl). 96-wells microtiter plates were heterotrophic bacteria as described in APHA (1998). Two inoculated by adding 20 μL of each dilution (8 wells per dilution) to different growth substrates were used. A nutrient broth was 180 μL of mineral medium (2.0 g/L NH4Cl, 0.89 g/L KH2PO4, 1.25 g/L used for pure cultures enumeration and R2A Agar was used Na2HPO4, 0.6 mg/L FeCl3). 10 μL of diesel were added to each well as for environmental samples. Plates were incubated for 7 days a sole substrate. Each sample was tested in duplicate. Plates were at 28 ºC. After this period, only plates having 30 to 300 incubated at 25 ºC for 21 days and then, 50 μL of resazurin (4.5 mg/L) colonies were considered for couting. All samples were were added to each well. Positive wells (pink coloured) were scored tested in duplicate after 48 h. The MPN was calculated. Pure cultures Environmental samples Tested samples: Pseudomonas putida Escherichia coli Compost from municipal wastewater Soil from hydrocarbon- (CECT 845) (CECT 101) treatment sludge contaminated site HDB No HDB Low HDB content High HDB content RESULTS Table 1. Results obtained with pure cultures (p=0.5) in cells/g (dry matter) • Same count of bacteria with plate count and MPN with the nutrient P. putida E.coli broth were obtained Method Medium Count Min Max Count Min Max • The same count of bacteria for P. putida was obtained with the Plate count Nutrient broth 1.75·108 1.67·108 1.82·108 2.74·108 2.23·108 3.25·108 developed method and the plate count. Nutrient broth 2.60·108 1.01·108 6.69·108 6.21·108 2.42·108 1.60·109 • No E. coli was detected with the developed method (no false MPN Diesel 1.22·108 4.74·107 3.13·108 Not detected positive responses were detected) Table 2. Results obtained with environmental samples (p=0.5) in cells/g (dry matter) • Low amount of HDB in the compost Compost sample Hydrocarbon-contaminated soil sample was detected as expected. Method Medium Count Min Max Count Min Max • Similar count of bacteria in the Plate count R2A Agar 1.10·1010 9.10·109 1.09·1010 6.60·107 2.590·107 7.30·107 hydrocarbon-contaminated soil was Figure 2. MPN in 96-well microtiter plates. MPN Diesel 1.57·103 6.11·102 7.03·103 2.59·107 1.01·107 6.65·107 A. P. putida in nutrient broth. B. P. putida in obtained with both methods, diesel medium and resazurin. C. E. coli in indicating that all bacteria are HDB. diesel medium and resazurin CONCLUSIONS The developed MPN method was based on three aspects: (1) the use of 96-wells microtiter plates for incubation, (2) the use of commercial diesel as the carbon source, and (3) the use of resazurin as activity indicator. The method resulted to be appropriate when testing with pure cultures since bacteria counts where comparable with counts obtained with the plate count method. It was confirmed that resazurin did not react with diesel which could have caused false positives.  Very different HDB was found in compost and contaminated soil samples indicating that the bacteria in the contaminated soil were already adapted to hydrocarbons.  These results demonstrated that the developed method could be used for the enumeration of hydrocarbon-degrading bacteria in the field of biological treatment of hydrocarbon-contaminated soil where, usually, amendments based on compost are used. REFERENCES • Wrenn , B.A. and Venosa A.D. (1996). Selective enumeration of aromatic and aliphatic hydrocarbon degrading bacteria by most-probable-number procedure. Canadian Journal of Microbiology, 42(3), 252-258 • APHA (1998). Standard methods for the examination of water and wastewater. Washington: American Public Health Association.