Biodegradation of nitrogen- and oxygen-containing aromatic compounds in groundwater from an oil-contaminated aquifer

The aerobic biodegradation of oxygen and nitrogen heterocycles and o-cresol by subsurface bacteria in groundwater from an oil contaminated site at Zealand, Denmark, was compared to the biodegradation of these compounds in laboratory adapted suspended and fixed-film cultures. The aquifer at the abstr...

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Published inJournal of contaminant hydrology Vol. 3; no. 1; pp. 65 - 75
Main Authors Jensen, Bjørn K., Arvin, Erik, Gundersen, Anders T.
Format Journal Article
LanguageEnglish
Published Amsterdam Elsevier B.V 01.09.1988
Elsevier Science
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Abstract The aerobic biodegradation of oxygen and nitrogen heterocycles and o-cresol by subsurface bacteria in groundwater from an oil contaminated site at Zealand, Denmark, was compared to the biodegradation of these compounds in laboratory adapted suspended and fixed-film cultures. The aquifer at the abstraction site had a relatively high redox potential, since it contained nitrate. The groundwater (i.e. without the soil phase) had a high biodegradation potential for dibenzofuran, indole, quinoline, flourenone and o-cresol. All the compounds were degraded in groundwater within 5–15 days from an initial concentration of about 0.5 mg L −1 in both mixed substrate and single substrate experiments with an initial ATP concentration of 0.2 ng mL −1. Pyrrole, however, was not degraded in groundwater within 55 days in the mixed substrate experiment and very slowly, after a lag period of 20 days, in the single substrate experiment. The biodegadability picture found for groundwater in the mixed substrate experiment was similar to the results found with laboratory adapted suspended and fixed-film cultures. None of the compounds had any inhibitory effect on the biodegradation of naphthalene.
AbstractList The aerobic biodegradation of oxygen and nitrogen heterocycles and o-cresol by subsurface bacteria in groundwater from an oil contaminated site at Zealand, Denmark, was compared to the biodegradation of these compounds in laboratory adapted suspended and fixed-film cultures. The aquifer at the abstraction site had a relatively high redox potential, since it contained nitrate. The groundwater (i.e. without the soil phase) had a high biodegradation potential for dibenzofuran, indole, quinoline, flourenone and o-cresol. All the compounds were degraded in groundwater within 5–15 days from an initial concentration of about 0.5 mg L −1 in both mixed substrate and single substrate experiments with an initial ATP concentration of 0.2 ng mL −1. Pyrrole, however, was not degraded in groundwater within 55 days in the mixed substrate experiment and very slowly, after a lag period of 20 days, in the single substrate experiment. The biodegadability picture found for groundwater in the mixed substrate experiment was similar to the results found with laboratory adapted suspended and fixed-film cultures. None of the compounds had any inhibitory effect on the biodegradation of naphthalene.
Author Jensen, Bjørn K.
Arvin, Erik
Gundersen, Anders T.
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Issue 1
Keywords Biodegradation
Oxygen
Pollution
Europe
Hydrocarbons
Denmark
Nitrogen
Aquifers
Language English
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Elsevier Science
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  ident: 10.1016/0169-7722(88)90017-4_BIB3
  article-title: Structure-toxicity relationships of selected nitrogenous heterocyclic compounds
  publication-title: Arch. Environ. Contam. Toxicol.
  doi: 10.1007/BF01056938
  contributor:
    fullname: Dumont
– volume: 3
  start-page: 473
  year: 1981
  ident: 10.1016/0169-7722(88)90017-4_BIB11
  article-title: ATP determination with firefly luciferase
  publication-title: J. Appl. Biochem.
  contributor:
    fullname: Leach
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Snippet The aerobic biodegradation of oxygen and nitrogen heterocycles and o-cresol by subsurface bacteria in groundwater from an oil contaminated site at Zealand,...
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SubjectTerms Earth sciences
Earth, ocean, space
Exact sciences and technology
Hydrology. Hydrogeology
Title Biodegradation of nitrogen- and oxygen-containing aromatic compounds in groundwater from an oil-contaminated aquifer
URI https://dx.doi.org/10.1016/0169-7722(88)90017-4
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