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

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Composting<br />

Composting is a form <strong>of</strong> biostimulation because it consists <strong>of</strong> nutrient additions,<br />

moisture <strong>and</strong> oxygen control in a contained system. In a properly-maintained<br />

compost pile, temperatures in excess <strong>of</strong> 55˚C are reached which kills most<br />

pathogens (Eweis et al., 1998) <strong>and</strong> is a technique most commonly used for<br />

treatment <strong>of</strong> municipal solid wastes. In applications for hazardous waste,<br />

contaminant organic compound concentrations <strong>and</strong> extremely high temperatures<br />

(>55˚C) cannot support microbial activity in a composting environment <strong>and</strong><br />

additional organics must be added <strong>and</strong> temperatures controlled (Eweis et al.,<br />

1998).<br />

Like all bioremediation techniques, composting is effective only if implemented<br />

properly. Optimization <strong>of</strong> four parameters is necessary for successful <strong>PAH</strong><br />

degradation during composting; aeration, temperature, moisture <strong>and</strong> pH.<br />

Composting is a generally aerobic process with microsites <strong>of</strong> anaerobic activity;<br />

therefore, the pile must be aerated through mechanical mixing or additions <strong>of</strong><br />

bulking agents to improve structure <strong>and</strong> porosity. Temperature <strong>of</strong> the pile must<br />

remain between 30 <strong>and</strong> 60˚C for optimal microbial community structure, solubility<br />

<strong>and</strong> mass transfer rates (Eweis et al., 1998). Addition <strong>of</strong> organic material, while<br />

maintaining a C:N ratio for 25:1, facilitates higher temperatures in compost piles<br />

<strong>and</strong> biodegradation. Moisture must be manipulated through water <strong>and</strong><br />

amendment additions. Most compost piles are able to reach high temperatures<br />

with low moisture contents. To obtain optimum moisture content in the pile (50-<br />

80%), a bulking agent (wood chips <strong>and</strong> sewage sludge) can be added (Epstein<br />

<strong>and</strong> Alpert, 1980).<br />

There are three types <strong>of</strong> composting systems; windrow, static piles <strong>and</strong> closed<br />

reactors (Eweis et al., 1998). Open systems (windrow <strong>and</strong> static piles) are more<br />

commonly used than the closed reactors. In a windrow system, the compost<br />

mixture is placed on an impermeable layer to prevent leaching <strong>of</strong> contaminants.<br />

The cross section <strong>of</strong> the pile must be such that high temperatures are maintained<br />

on the interior <strong>of</strong> the pile with minimal heat losses on the outside <strong>of</strong> the pile.<br />

Aeration is achieved through mechanical mixing (front end loader or turner). If<br />

the pile is too large to mix, pipes can be installed to increase aeration in the pile.<br />

Windrow piles are <strong>of</strong>ten covered with a high density, polyethelyne material or<br />

wood chips in outside environments to prevent leaching from the pile during<br />

rainfall events (Eweis et al., 1998). In static piles, compost material is placed on<br />

an impermeable platform with perforated pipes connected to a blower system.<br />

Piles are aeriated at either a fixed rate or variable rate depending on the<br />

microbial activity. Static piles are also covered with plastic sheeting, but the<br />

cover must allow air to enter the pile. Closed reactors are the least used<br />

systems because <strong>of</strong> size limitations, but are the most controlled. Closed systems<br />

are constructed as the name implies <strong>and</strong> contain mixing devices through drum<br />

rotation or mixing instruments within the tank (Eweis et al., 1998).<br />

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