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Biological degradation of selected hydrocarbons in an old PAH/creosote contaminated soil from a gas work site.

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TLDR
An old PAH/creosote contaminated soil from a former gas work site in Stockholm, Sweden, has been treated at 20 °C with the addition of various nutrients and inoculated with bacteria to enhance the degradation of selected hydrocarbons.
Abstract
An old PAH/creosote contaminated soil (total ∼300 μg PAH/g soil) from a former gas work site in Stockholm, Sweden, has been treated at 20 °C with the addition of various nutrients and inoculated with bacteria (isolated from the soil) to enhance the degradation of selected hydrocarbons. Microcosm studies showed that the soil consisted of two contaminant fractions: one available, easily degraded fraction and a strongly sorbed, recalcitrant one. The bioavailable fraction, monitored by headspace solid phase microextraction, contained aromatics with up to three rings, and these were degraded within 20 days down to non-detectable levels (ng PAH/g soil) by both the indigenous bacteria and the externally inoculated samples. The nutrient additives were: a minimal medium (Bushnell-Haas), nitrate, nitrite, potting soil (Anglamark, Sweden), sterile water and aeration with Bushnell-Haas medium. After 30 days treatment most of the sorbed fractions were still present in the soil. Stirring or mechanical mixing of the soil slurries had the greatest effect on degradation, indicating that the substances were too strongly sorbed for the microorganisms. When stirring the choice of nutrient seemed less important. For the non-stirred samples the addition of nitrate with the bacterial inoculum showed the best degradation, compared to the other non-stirred samples. At the end of the experiments, accumulations of metabolites/degradation products, such as 9H-fluorenone, 4-hydroxy-9H-fluorenone, 9,10-phenanthrenedione and 4H-cyclopenta[def]phenanthrenone were detected. The metabolite 4-hydroxy-9H-fluorenone increased by several orders of magnitude during the biological treatments. Microbial activity in the soil was measured by oxygen consumption and carbon dioxide production.

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Journal ArticleDOI

Bacterial community dynamics and polycyclic aromatic hydrocarbon degradation during bioremediation of heavily creosote-contaminated soil.

TL;DR: This study shows that specific bacterial phylotypes are associated both with different phases of PAH degradation and with nutrient addition in a preadapted PAH-contaminated soil.
Journal ArticleDOI

Sources, Fate, and Toxic Hazards of Oxygenated Polycyclic Aromatic Hydrocarbons (PAHs) at PAH- contaminated Sites

TL;DR: Oxy-PAHs are important cocontaminants that should be taken into account during risk assessment and remediation of sites with high levels of PAHs, and should be included in monitoring programs at PAH-contaminated sites, even if a number of other toxicologically relevant compounds that may also be present are not monitored.
Journal ArticleDOI

Degradation of polycyclic aromatic hydrocarbons at low temperature under aerobic and nitrate-reducing conditions in enrichment cultures from northern soils.

TL;DR: Biodegradation of polycyclic aromatic hydrocarbons at low temperature and under anaerobic conditions is not wellunderstood, but such biodegradation would be very useful formediation of polluted sites and Ribosomal intergenic spacer analysis suggested that enrichment resulted in few predominant bacterial populations.
Journal ArticleDOI

Degradation and formation of polycyclic aromatic compounds during bioslurry treatment of an aged gasworks soil.

TL;DR: Investigation of the relative degradation rates of polycyclic aromatic compounds in contaminated soil found that low molecular weight PAHs and heterocyclics were degraded faster than the high molecular weight compounds, while oxy-PAHs degraded more slowly than the parent compounds, suggesting that they were formed during the treatment or that they are more persistent.
Journal ArticleDOI

Polycyclic aromatic hydrocarbons in soils: Sources, behavior, and indication significance (a review)

TL;DR: The main processes typical for PAHs in soils are defined; the sorption, degradation, and translocation features of polyarenes in the soil profile are shown; and attention is paid to the geographical features of the PAH distribution in soils.
References
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Journal ArticleDOI

Biodegradation of polycyclic aromatic hydrocarbons

TL;DR: The intent of this review is to provide an outline of the microbial degradation of polycyclic aromatic hydrocarbons, a catabolically diverse microbial community, consisting of bacteria, fungi and algae, metabolizes aromatic compounds.
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