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health and safety plan solid waste management unit assessment

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FUEL OILS 66-15<br />

Natural ecosystems have considerable exposure to petroleum<br />

hydrocarbons from natural emissions, accidental contamination through<br />

oil spills <strong>and</strong> storage tank leaks, <strong>and</strong> deliberate application to l<strong>and</strong><br />

in <strong>waste</strong> disposal activities such as l<strong>and</strong>-farming; therefore, their<br />

biodegradation is of environmental importance. Numerous authors have<br />

observed the biodegradation of petroleum hydrocarbons, <strong>and</strong> several<br />

extensive reviews <strong>and</strong> reports are available (1846,2252,2255,2249,<br />

2253). An extensive <strong>and</strong> diverse group of petroleum hydrocarbondegrading<br />

bacteria <strong>and</strong> fungi are widely distributed in the environment.<br />

Although the microbiota of most non-contaminated soils include many<br />

naturally occurring hydrocarbon-degrading populations, the addition of<br />

petroleum selectively enriches that sector able to adapt <strong>and</strong> utilize<br />

the'new substrate. Other environmental factors shown to have a major<br />

effect on biodegradability are availability of oxygen <strong>and</strong> moderate<br />

temperatures. The reader is referred to Chapter 64 for a more detailed<br />

summary of the biodegradation of petroleum hydrocarbons,<br />

The qualitative hydrocarbon content of petroleum mixtures largely<br />

determines their degradability. In general, microorganisms exhibit<br />

decreasing ability to degrade aliphatic hydrocarbons with increasing<br />

chain length: aromatics are generally more rapidly biodegraded than<br />

alkanes. The composition of diesel oil suggests that some of the<br />

aromatic species will be biodegradable: biodegradation of the high<br />

molecular weight aromatics expected to be present in residual oils will<br />

be slower (2339).<br />

In s-ary , biodegradation of the petroleum hydrocarbons<br />

comprising diesel <strong>and</strong> fuel oils may occur under conditions favorable<br />

for microbial activity <strong>and</strong> when fuel components are freely available to<br />

the microorganisms. Degradation may be limited <strong>and</strong>/or slow in<br />

environments with few degrading organisms, low pH. low temperatures,<br />

<strong>and</strong> high salinity (e.g., arctic environments). It should be mentioned<br />

that Walker s a. (2257) state that even under optimum conditions,<br />

total <strong>and</strong> complete biodegradation is not expected to occur except<br />

possibly over an extremely long time period.<br />

66.2.3 Primary Routes of Exposure from Soil/Ground-water Systems<br />

The above discussion of fate pathways suggests that pure fuel oils<br />

have low vapor pressure but that their components vary in their<br />

volatility from water. The components are strongly or very strongly<br />

sorbed to soil. The polycyclic aromatic hydrocarbons in fuel oils have<br />

a moderate or high potential for bioaccumulation, while the<br />

longer-chain aliphatic compounds have low potential for<br />

bioaccumulatfon. These fate characteristtcs suggest that the various<br />

components may have somewhat different potential exposure pathways.<br />

Volatilization of fuel oils from a disposal site or spill would<br />

not be expected to result in significant inhalation exposures to<br />

workers or residents in the area. Gravity would tend to carry bulk<br />

quantities of the oil down towards the water table leaving only a<br />

6/87

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