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Bioremediation Field Evaluation Eielson Air Force Base, Alaska

Bioremediation Field Evaluation Eielson Air Force Base, Alaska

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prompting additional studies at Hill<br />

and Tyndall AFBs. <strong>Base</strong>d on successes<br />

in these warm-weather sites,<br />

the <strong>Air</strong> <strong>Force</strong> and the U.S. Environmental<br />

Protection Agency’s (EPA’s)<br />

National Risk Management Research<br />

Laboratory (NRMRL) became<br />

interested in the possibility<br />

of using bioventing in cold climates.<br />

Microbial degradation occurs<br />

slowly, if at all, however, at low<br />

temperatures. The <strong>Air</strong> <strong>Force</strong> and<br />

NRMRL decided to study the use of<br />

soil warming measures to enhance<br />

the effectiveness of bio-venting<br />

in a cold climate. They selected<br />

<strong>Eielson</strong> AFB in Fairbanks, <strong>Alaska</strong>, as<br />

the study site. In winter, soil temperatures<br />

at this site drop to about 0°C.<br />

The field evaluation at <strong>Eielson</strong> AFB<br />

was undertaken to determine<br />

whether and to what degree soil<br />

warming can enhance the effectiveness<br />

of bioventing jet fuel contaminated<br />

soil in a cold climate. The<br />

evaluation also aimed to determine<br />

whether soil warming promotes<br />

high-rate, year-round bioremediation<br />

at a lower overall cost than prolonged<br />

low-rate bioremediation at<br />

ambient temperatures. The results of<br />

the evaluation are summarized below.<br />

They have also been discussed in<br />

other publications (6-8); see those<br />

publications for additional information.<br />

Site History<br />

<strong>Eielson</strong> AFB is an active base<br />

located in the <strong>Alaska</strong>n interior,<br />

about 25 miles southeast of Fairbanks<br />

(see Figure 2). The base serves a wide<br />

variety of aircraft and maintains a<br />

high volume of traffic. The climate is<br />

subarctic, with an average annual<br />

temperature near 0°C. Ambient temperatures<br />

range from below -30°C in<br />

the winter to above 30°C in the summer.<br />

Permafrost is present in some<br />

areas on <strong>Eielson</strong> AFB, but not in Site<br />

20, the area selected for this field<br />

Figure 2. Location of <strong>Eielson</strong> AFB.<br />

evaluation. Site 20 is a 1-acre area<br />

of land centered over two pressurized<br />

lines that intersect the site.<br />

The pressurized fuel lines are suspected<br />

to be the source of the fuel<br />

release because the area where<br />

the lines intersect is the most highly<br />

and uni-formly contaminated part of<br />

the site.<br />

The <strong>Air</strong> <strong>Force</strong> conducted a site<br />

characterization in July 1991,<br />

which revealed that the surface<br />

soil at Site 20 is a mixture of sand<br />

and gravel, with silt concentration<br />

increasing to about 6 ft. The soil<br />

was contaminated with JP-4 jet<br />

fuel from a depth of roughly 2 ft to<br />

the water table at 6 to 7 ft. Total<br />

petroleum hydrocarbon (TPH) levels<br />

ranged from 100 to 3,000 mg/kg,<br />

depending on soil depth and area.<br />

A hydrocarbon sheen was visible in<br />

the ground-water monitoring wells<br />

subsequently installed, and<br />

5<br />

ground-water samples showed TPH<br />

levels of 15 to 20 mg/L.<br />

In summer 1991, the <strong>Air</strong> <strong>Force</strong> and<br />

NRMRL installed and began operating<br />

an in situ soil bioremediation<br />

system: a bioventing system consisting<br />

of an air blower plumbed to<br />

air injection/extraction (bioventing)<br />

wells. The system could operate as<br />

an injection or extraction bioventing<br />

system; the <strong>Air</strong> <strong>Force</strong> and<br />

NRMRL conducted most of the<br />

study in the injection mode, which<br />

is the generally preferred method<br />

of bioventing. Operating the<br />

bioventing system involved using<br />

the blower to inject atmospheric<br />

air into the contaminated subsurface<br />

at a rate of 25 cubic feet per<br />

minute (ft 3 /min). <strong>Air</strong> injection/extraction<br />

wells were distributed uniformly<br />

at 30-ft intervals to provide<br />

relatively uniform aeration. The <strong>Air</strong><br />

<strong>Force</strong> and NRMRL constructed

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