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Remediation of PAH-Contaminated Soils and Sediments: A ...

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in contaminated soils than uncontaminated soils (Carmichael <strong>and</strong> Pfaender,<br />

1997).<br />

Before discussing remediation techniques, it is important to identify the different<br />

microorganisms capable <strong>of</strong> degrading <strong>PAH</strong>s. Bacterial, fungal <strong>and</strong> algal species<br />

have been found to degrade <strong>PAH</strong> compounds, with bacteria constituting the most<br />

important group <strong>of</strong> degraders (Cerniglia et al., 1992; Kastner et al., 1994).<br />

Numerous bacteria genera <strong>and</strong> species can degrade 2- or 3-ring <strong>PAH</strong>s have<br />

been identified, but few genera have shown ability to degrade HMW <strong>PAH</strong>s (Table<br />

3). However, some Pseudomonas species have been found to degrade 4-ring<br />

<strong>and</strong> 5-ring <strong>PAH</strong>s (Juhasz <strong>and</strong> Naidu, 2000).<br />

Table 3. Some genera <strong>of</strong> <strong>PAH</strong>-degrading microorganisms (adapted from Frick<br />

et al., 1999).<br />

Bacteria<br />

<strong>PAH</strong> compounds degraded<br />

Acidovorax phenanthrene, anthracene<br />

Alcaligenes phenanthrene, fluorene, fluoranthene<br />

Arthrobacter benzene, naphthalene, phenanthrene<br />

Mycobacterium phenanthrene, pyrene, benzo[a]pyrene,<br />

Pseudomonas phenanthrene, fluoranthene, fluorene, benzo[a]pyrene<br />

Rhodococcus pyrene, benzo[a]pyrene<br />

Sphingomonas phenanthrene, fluoranthene, anthracene<br />

The following studies are examples <strong>of</strong> biodegradation research:<br />

� Liste <strong>and</strong> Felgentreu (2006) observed similar microbial species richness<br />

between a contaminated <strong>and</strong> pristine soil; however, <strong>PAH</strong> degraders<br />

(Alcaligenes piechaudii, Pseudomonas putida, <strong>and</strong> Stenotrophomonas<br />

maltophilia) were more abundant in the contaminated soil (1517 mg kg -1<br />

total petroleum hydrocarbons; 71.4 mg kg -1 total <strong>PAH</strong>s) compared to<br />

pristine soil.<br />

� Mueller et al. (1997) reported bacterial ability to degrade <strong>PAH</strong>s isolated<br />

from creosote-contaminated soils in the United States, Norway, <strong>and</strong><br />

Germany. Sphingomonas strains showed the most ability to degrade 4- &<br />

5-ring <strong>PAH</strong>.<br />

� Kanaly <strong>and</strong> Harayama (2000) found that Sphingomonas species used<br />

compounds like fluoranthene <strong>and</strong> phenanthrene as a sole carbon source,<br />

while a Mycobacterium strain from <strong>PAH</strong>-contaminated freshwater<br />

sediments was capable <strong>of</strong> using phenanthrene, pyrene, <strong>and</strong> fluoranthene<br />

25

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