About Us | Help Videos | Contact Us | Subscriptions

Journal of Environmental Quality Abstract - Bioremediation and Biodegradation

9,10-Phenanthrenequinone Photoautocatalyzes its Formation from Phenanthrene, and Inhibits Biodegradation of Naphthalene


This article in JEQ

  1. Vol. 34 No. 2, p. 462-468
    Received: June 23, 2004

    * Corresponding author(s): rsanford@uiuc.edu
Request Permissions

  1. Jonathan Holtad,
  2. Seth Hothemb,
  3. Heidi Howertonb,
  4. Richard Larsonb and
  5. Robert Sanford *ac
  1. a Department of Civil and Environmental Engineering, University of Illinois at Urbana-Champaign, Urbana, IL 61801
    d Department of Crop Sciences, University of Illinois at Urbana-Champaign, Urbana, IL 61801
    b Department of Natural Resources and Environmental Sciences, University of Illinois at Urbana-Champaign, Urbana, IL 61801
    c Department of Geology, University of Illinois at Urbana-Champaign, Urbana, IL 61801


Polycyclic aromatic hydrocarbons (PAHs) have earned considerable attention due to their widespread environmental distribution and toxicity. In the environment, PAHs decompose by a variety of biotic and abiotic pathways. In both polar and nonpolar environments, phenanthrene (Phe, a common, three-ring PAH) is converted by sunlight to more polar products such as 9,10-phenanthrenequinone (PheQ) and subsequent oxidation products such as the corresponding open-ring dicarboxylic acid product. Biodegradation of phenanthrene also usually leads to oxidative metabolites, and eventually ends in mineralization. Our experimental objective was to investigate the photodegradation of phenanthrene and determine the effect of reaction products such as PheQ on microbial biodegradation of two- and three-ring PAHs. Abiotic experiments were performed to examine the photolytic breakdown of Phe; Phe was converted to PheQ, which catalyzed its own formation. In biodegradation experiments PheQ (0.04–4 mg/L) caused marked inhibition of naphthalene (Nap) biodegradation by a Burkholderia species; Phe did not. Only 20% of the naphthalene was degraded in the presence of PheQ compared with 75% in the control culture with no PheQ added. No PAH-degrading cultures were able to use PheQ as sole carbon source; however, the Phe-degrading enrichment culture dominated by a Sphingomonas species was able to degrade PheQ cometabolically in the presence of Phe. These results may explain why photooxidized phenanthrene-containing mixtures can resist biodegradation.

  Please view the pdf by using the Full Text (PDF) link under 'View' to the left.

Copyright © 2005. American Society of Agronomy, Crop Science Society of America, Soil Science SocietyASA, CSSA, SSSA