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JP-4 (JET FUEL 4) 64-13<br />

solubility. The alkyl benzenes have higher water solubilities <strong>and</strong><br />

transport with infiltrating water may be important for these compounds:<br />

volatilization, on the other h<strong>and</strong>, may be less important. In saturated,<br />

deep soils (containing no soil air <strong>and</strong> negligible soil organic<br />

carbon), a significant percent of both aliphatic (particularly less<br />

than C,) <strong>and</strong> aromatic hydrocarbons is predicted to be present in the<br />

soil-water phase <strong>and</strong> available for transport with flowing ground water.<br />

In interpreting these results, it must be remembered that this<br />

model is valid only for low soil concentrations (below aqueous solubility)<br />

of the components. Large releases of JP-4 (spills, leaking<br />

underground storage tanks) may exceed the sorptive capacity of the<br />

soil, thereby filling the pore spaces of the soil with the fuel. In<br />

this situation, the hydrocarbon mixture would move as a bulk fluid <strong>and</strong><br />

the equilibrium partitioning model would not be applicable.<br />

Overall, ground water underlying soil contaminated with JP-4<br />

hydrocarbons is expected to be vulnerable to contamination by at least<br />

some of these components. The type of spill (surface vs. sub-surface)<br />

is of particular importance, since volatilization from the surface is<br />

expected to be a significant removal process for low molecular weight<br />

aliphatics. At this point, it should be mentioned that environmental<br />

fate/exposure/toxicology chapters for several of the components in<br />

Table 64-4 were included in Volume 1 of the IRP Toxicology Guide. T'he<br />

JP-4 components addressed in Volume 1 include: benzene, toluene,<br />

xylenes, ethyl benzene, <strong>and</strong> naphthalene.<br />

64.2.1.2 Transport Studies<br />

Due to the extensive use of JP-4 <strong>and</strong> other aviation fuels <strong>and</strong><br />

their potential for environmental release during use, storage or<br />

transport, several groups have addressed its fate. The fate of JP-4 in<br />

the soil environment is basically a function of the solubility, volatility,<br />

sorption, <strong>and</strong> degradation of its major components. The relative<br />

importance of each of these processes is influenced by the type of<br />

contamination (e.g., surface spill x. underground release, major vs.<br />

minor quantity), soil type (e.g., organic content, previous history of<br />

soil contamination), <strong>and</strong> environmental conditions (e.g., pH, temperature,<br />

oxygen content).<br />

Transport processes have been shown to be more significant than<br />

transformation processes in determining the initial fate of petroleum<br />

hydrocarbons released to soil/ground-water systems (1845,1848,1846).<br />

For JP-4 released to surface soils or waters, transport to the<br />

atmosphere through volatilization has been shown to be the primary fate<br />

pathway for most of the JP-4 hydrocarbons; subsequent atmospheric<br />

photolysis is expected to be rapid (1845). Using a model fuel mixture<br />

containing approximately fifteen compounds representative of major JP-4<br />

hydrocarbons, Spain & a. (1846) demonstrated that compounds having up<br />

to nine carbons are weathered almost exclusively by evaporation; larger<br />

compounds were weathered primarily by evaporation <strong>and</strong> biodegradation:<br />

dimethylnaphthalene <strong>and</strong> highly substituted aromatics (X,,) were shown<br />

to be persistent in these tests. Reduced temperatures tend to increase<br />

JP-4 persistence by retarding the rates of volatilization <strong>and</strong> biodegradation<br />

(1846.1822).<br />

6/87

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