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Chapter 7 : Bioremediation of Marine Oil Spills

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Abstract:

Bioremediation offers an environmentally appropriate and cost-effective response to marine oil spills that reach shore and is deservedly part of the "tool kit" available to spill responders. This chapter provides an overview of the composition of crude oil and the refined fractions that may be spilled at sea, discusses the diversity of organisms able to degrade oil components, and describes strategies for encouraging the growth of such organisms. It describes how bioremediation can be integrated with physical techniques to deliver an optimal cleanup and also discusses the environmental harm that might be done if bioremediation were applied carelessly and how this potential can be minimized. Crude oils are principally hydrocarbons, molecules composed of only carbon and hydrogen, and the hydrogen-to-carbon ratio is typically between 1.5 and 2. Fertilizer is typically applied to the surface of oiled sediments. Although bioremediation by addition of fertilizers will speed the biodegradation of an oil spill and thereby diminish its environmental impact, it is important to bear in mind that careless application of fertilizers may have unwanted negative impacts on the environment, and they should be used with care. In conclusion, bioremediation is not the panacea for mitigating oil spills-but it is an important tool in reducing the ecological impact of some oil spills.

Citation: Prince R, Atlas R. 2005. Bioremediation of Marine Oil Spills, p 269-292. In Atlas R, Philip J (ed), Bioremediation. ASM Press, Washington, DC. doi: 10.1128/9781555817596.ch7

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Figures

Image of FIGURE 7.1
FIGURE 7.1

Representative hydrocarbons in the principal molecular classes in crude oils.

Citation: Prince R, Atlas R. 2005. Bioremediation of Marine Oil Spills, p 269-292. In Atlas R, Philip J (ed), Bioremediation. ASM Press, Washington, DC. doi: 10.1128/9781555817596.ch7
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Image of FIGURE 7.2
FIGURE 7.2

Representative structures for resin and polar components found in crude oils.

Citation: Prince R, Atlas R. 2005. Bioremediation of Marine Oil Spills, p 269-292. In Atlas R, Philip J (ed), Bioremediation. ASM Press, Washington, DC. doi: 10.1128/9781555817596.ch7
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Image of FIGURE 7.3
FIGURE 7.3

An overview of the initial reactions of aromatic hydrocarbon activation in hydrocarbon- degrading microorganisms and in animals. In polycyclic aromatic hydrocarbons ( ), the aromatic ring shown would be part of a multiring structure. More details can be found elsewhere ( ).

Citation: Prince R, Atlas R. 2005. Bioremediation of Marine Oil Spills, p 269-292. In Atlas R, Philip J (ed), Bioremediation. ASM Press, Washington, DC. doi: 10.1128/9781555817596.ch7
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Image of FIGURE 7.4
FIGURE 7.4

Some representative data obtained in a field trial of bioremediation on a beach near Sveagruva, on Spitsbergen in the summer of 1997. (A) Amounts of “fixed nitrogen” (nitrate plus ammonium) in interstitial water taken from fertilized and unfertilized portions of the beach. Note that the scale is logarithmic and that the line drawn through the data is merely to guide the eye. Error bars represent standard errors for each point, and those at 1 µM are estimates of the lower detection limit of the colorimetric test kits used. Further details can be found in reference . (B) Measurements of dissolved oxygen in that interstitial water. Again, the line is merely to guide the eye, and the error bars are estimates of standard error. (C) Measurements of the rate of CO evolution from undisturbed beach. Data were collected on only four days, but the timescale is the same as for the other panels to allow ready comparison. The dotted lines are shown merely to guide the eye; we have no evidence that the data follow a straight line, but numerous measurements of unoiled, unoiled but fertilized, and oiled unfertilized plots ( ) led us to extrapolate to equivalent rates for all sections before fertilizer application. We note that these data demonstrate the variability typically seen in the field and that the simplistic statistical treatment here was verified with more rigorous approaches in the cited references.

Citation: Prince R, Atlas R. 2005. Bioremediation of Marine Oil Spills, p 269-292. In Atlas R, Philip J (ed), Bioremediation. ASM Press, Washington, DC. doi: 10.1128/9781555817596.ch7
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Image of FIGURE 7.5
FIGURE 7.5

Some representative data obtained during the bioremediation of the spill in Alaska in 1990. (A) Representative radiorespirometry data ( ). (B) Representative data using hopane as a conserved internal analyte ( ) from the same beach. Error bars represent estimates of standard errors, and again we note that these data demonstrate the variability typically seen in the field and that the simplistic statistical treatment here was verified with more rigorous approaches in the cited references. GC, gas chromatography.

Citation: Prince R, Atlas R. 2005. Bioremediation of Marine Oil Spills, p 269-292. In Atlas R, Philip J (ed), Bioremediation. ASM Press, Washington, DC. doi: 10.1128/9781555817596.ch7
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