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Last Update 02/04/2009

 

 

    
     
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Tetracycline Resistance in Aerobic and Anaerobic Bacteria

Recovered from Landfill Leachate

 

Neil Kirkpatrick, Jenny Will, and James McGaughey

Biological Sciences Department, Eastern Illinois University, Charleston, IL

 

Introduction and Purpose

 

Solid waste landfills are inhabited by various microorganisms including bacteria. Leachate accumulating within these landfills has the potential to contaminate surrounding groundwater and surface waters with potentially pathogenic bacteria, some of which may exhibit resistance to currently prescribed antibiotics. Tetracycline, an antibiotic which has found widespread use in a variety of applications, may be useful as a model substance for investigating development of bacterial resistance.

 

The purposes of this experiment were to estimate the density of aerobic and anaerobic bacteria in landfill leachate and surrounding groundwater and to evaluate their resistance to tetracycline.

 

landfill.jpg (48225 bytes) Landfill
   

 

Methods

 

Leachate from a closed landfill and adjacent groundwater samples were obtained from a regional landfill site. All samples were extracted via a well/pump collection system integrated with the landfill and the surrounding ground. Samples were diluted 10-1 to 10-3 using phosphate buffered saline. Ten milliliter portions were vortexed and filtered through 0.22mm membrane filters. Replicate filters were transferred onto pads with 2mL of Plate Count broth. One half of the plates contained 20mg mL-1 tetracycline. The other half contained Plate Count broth without tetracycline. Of these plates, one half were incubated aerobically and the other half in a BBL GasPak Anaerobic System for 48 hours at 35oC . Statistical analyses were performed. A Mann-Whitney test was used to determine the probability of significant differences between tetracycline resistant and tetracycline sensitive populations.

 

samples.jpg (45058 bytes) Groundwater sample (left); Leachate sample (right)
chamber.jpg (29938 bytes) BBL Gaspak Anaerobic System
aparatus.jpg (55607 bytes) Manifold filtration system

  

Results

 

fig01.jpg (24853 bytes) Figure 1: Mean heterotrophic count of bacteria from groundwater.
fig02.jpg (25439 bytes) Figure 2: Mean heterotrophic count of bacteria from leachate.
fig03.jpg (21254 bytes) Figure 3: Heterotrophic bacteria resistant to tetracycline.

 

Table 1. Mann-Whitney test results. Heterotrophic counts with and without tetracycline (p<0.05).

Groundwater

Leachate

Aerobic

Anaerobic

Aerobic

Anaerobic

Mann-Whitney results

54.5

38.5

0.0

7.0

Significant Difference (p<0.05)

0.127

0.004

0.000

0.001

 

Populations of aerobic heterotrophs from groundwater ranged from 2,000-4,000mL-1; anaerobic populations ranged from 1,000-1,200mL-1.  Populations of aerobic heterotrophs from leachate ranged from 400 – 38,000mL-1; anaerobic populations ranged from 1,000 – 9,100mL-1.  33% of aerobic and 12% of anaerobic populations from groundwater were resistant to tetracycline.  1% of aerobic and 10% of anaerobic populations from leachate were resistant to tetracycline.  Mann-Whitney tests indicated a significant difference for tetracycline resistance among aerobic and anaerobic bacteria recovered from groundwater and aerobic bacteria recovered from leachate.  Mann-Whitney tests indicated no significant difference for tetracycline resistance among aerobic heterotrophic bacteria recovered from groundwater.

 

Summary

 

Populations of aerobic and anaerobic bacteria recovered from landfill leachate and groundwater displayed a wide range of values.  Resistance to tetracycline was highest among bacteria isolated from groundwater and lowest among bacteria isolated from leachate samples.  Anaerobic bacteria seemed to be more resistant to tetracycline than aerobic bacteria.  Tetracycline appeared to maintain its effectiveness in reducing populations of heterotrophic bacteria with the exception of the aerobic groundwater populations.

 

References

 

American Public Health Association (1985). Standard Methods For the Examination of Water and Wastewater. (16th ed.). Washington D.C.: Authors.

Barlaz, M.A. 1989. Bacterial Population development and Chemical Characteristics of Refuse Decomposition in a Simulate Sanitary Landfill. Applied Environmental Microbiology. 55: 55-65

Bulc, T. 1996. Persistence and Antibiotic Immunity of Bacteria from a Wetland used as a Medical Waste Landfill. Wetland Systems for a Water Pollution Control. 35: 301-306.

Boenign, D. 1996. Persistence and Antibiotic Immunity of Bacteria from a Wetland used as a Medical Waste Landfill. Journal of Environmental Health. 59: 6-13.

Devare, M. 1994. Biological monitoring of Landfill Leachate using Plants and Bioluminescent Bacteria. Chemosphere 28: 261-271.

Dickman, M. 1998. Municipal Landfill Impacts on a Natural Stream located in an Urban Wetland in Regional Niagra, Ontario. Canadian Field-Naturalist 112: 619-630.

Maritenssen, M. 1997. Biological Treatment of Leachate from Solid Waste Landfill Sites-alterations to the Bacterial Community during the Denitrification process. Water Research 31: 1164-1170.

NCCLS. 2001. Performance Standards for Anti-Microbial susceptibility testing; Eleventh informational supplement. NCCLS document M100-S11. Pennsylvania.

Senior, Eric (Ed.).(1995) Microbiology of Landfill Sites. Boca Raton: Lewis Publishers

Obbard, J.P. 1999. Landfill leachate: Characteristics and Biological Treatment in Hong Kong. Resource and Environmental Biotechnology 2: 235-248.

 

Acknowledgements

 

Funding and support from the College of Sciences; Department of Biological Sciences and the Undergraduate Research Council, Eastern Illinois University.  Dr. Scott Meiners for his help with data analysis and statistical calculations.  Matt Gresk for his help and support with the poster design.

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