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U.S. Environmental Protection Agency
U.S. EPA Technology Innovation and Field Services Division

Phytotechnology Project Profiles

Phytoremediation at the former tank farm and former dry cleaning facility in Alaska
Last Updated: January 2006
Site Information                                                      
Site Name, Location:   Former tank farm and former dry cleaning facility, Barrow, AK, United States
Site Type:   Dry Cleaner
Is this a Federal
Superfund Site?
  No
Is this a Federal or
Military Site?
  Yes
Entity Responsible for Cleanup:   Navy


Project Information                                                      
Project Name:   Phytoremediation at the former tank farm and former dry cleaning facility in Alaska
Site History and Background:   The facility was established in 1947 as a logistic supply center for petroleum exploration and was also used as a basic and applied research center, contributing to Navy operations in the Arctic. In 1987, The Navy signed a land-exchange agreement to transfer ownership of NARL to the Ukpeagvik Inupiat Corporation (UIC), a Barrow native village corporation. The complex is currently operated by the UIC, houses a local college, and provides office space for various borough departments and contractors performing projects for the North Slope Borough. Waste source: From operations related to a former dry cleaning facility and former bulk tank fuel farm; bulk fuel tanks contained diesel fuel, gasoline, Mogas and JP-5 jet fuel.
Scale:   Pilot/Field Demonstration
Project Status:   Complete
Project Start Date:   Summer 1999
Project Completion Date:   Not available
Media Treated:  
Media Qty. Geology Comments
Soil At this site, surface soils consist of mainly coarse sand and gravel marine beach deposits. Soil is silty in vegetated areas. A blue-black clay has been reported at depths of 10 to 60 feet. Estimated to be 7,000 cubic yards of petroleum contaminated soil present. Soils remain frozen through most of the year, but thaw to a maximum depth of 55 inches in August or September and refreeze by late October. Groundwater occurs only in the thawed zone above the permafrost, and there is no significant flow. Treatment depth was through the root zone, or approximately two feet.
Contaminants Treated:  
Contaminant Initial
Concentration
Depth Media Comments
Gasoline Soil
Lead 8.1-365 mg/kg Soil Present at Tank Farm.
Tetrachloroethene Soil Trace-levels.
Total petroleum hydrocarbons 47-9400 mg/kg Soil Present at Tank Farm. Averaged: 1278 mg/kg
Benzene-toluene-ethylbenzene-xylene (BTEX) Soil Present at Tank Farm.
Diesel oil Soil Diesel Range Organics (DRO), Gasoline Range Organics (GRO), Total Residual Petroleum (TRP), Halogenated aliphatics, phenolics, solvents, and inorganic compounds. Concentrations at the Dry Cleaning Facility - DRO: 230mg/kg to 810 mg/kg (average 504 mg/kg); GRO: below detection limit to 85 mg/kg (average 18.2 mg/kg). Concentrations at the Tank Farm - DRO: ranged from 200-260 mg/kg; GRO: 838 mg/kg 3 feet below ground; TRP ranged from 230-250 mg/kg.
Polycyclic aromatic hydrocarbons (PAH) Soil Present at Tank Farm.
Phytotechnology Mechanism(s):   Phytoremediation
Rhizodegradation
Plants and other Vegetation Used:   Clover
Rye Grass
Fescue
Planting Description:   A seed mixture containing three species of cold-tolerant grasses (10-15% Annual Rye Grass, 60-70% Arctared Red Fescue, and 20-25% White Clover) was used. There was minimal soil preparation prior to seeding. Seeds were surface-applied using handheld seeders and then pressed into the soil. The maximum permissible (less than 2,000 mg nitrogen/kg of soil) quantity of standard agricultural fertilizer was added. Two control areas were prepared: one with only fertilizer but no seeds; and one with seeds but no fertilizer.
Climate:   The area is very cold and dry. Temperature ranges from -19F in February to 40F in July. The average annual precipitation is 4.6 inches. High relative humidity (90 to 95%) in the summer leads to foggy conditions about 25% of the time.
O & M Requirements:   Site setup included initial site delineation; obtaining time-zero samples; collecting, compositing, preparing, and installing soil socks for later sampling; data-logger setup; and seeding and nutrient additions
Performance Data:   Contaminant concentrations were reduced (quantitative results were not available). Significant plant growth was observed in fertilized areas, and long term cleanup goals are anticipated to be achieved only after continued remediation during future thaw periods.
Cost of the Phytotechnology Project:   Capital cost - $7,250; O&M - $1,400/year; Other costs - $6,000/year (includes long-term monitoring, regulatory oversight, compliance testing/analysis, excavation, and disposal of residues); Total cost (based on 10,000 ft^2 treatment area, 2 ft treatment depth, and 10 year period of operation) - $27,250
Lessons Learned:   1. Plants have a positive effect on petroleum depletion relative to either nutrients alone or control treatments. 2. The effect is not uniform across all petroleum fractions. 3. The effect is not seen by standard monitoring techniques. 4. Nutrients alone can have an inhibitory effect on depletion of some petroleum fractions. 5. There are measurable microbial changes that support, and probably drive, the contaminant changes.
Comments:   Lessons learned during field demonstrations are applicable to applications at a larger scale. Though implementation is relatively straightforward, unfortunately, so are ineffective or incorrect implementation steps. Consideration should be given to altering the monitoring strategy to fit the technology being used; such as timing the sampling event with respect to the status of the system rather than the calendar, selecting an appropriate variable to monitor, and determining how to sample with respect to the selected monitoring variable. The appropriate variable may vary with the degree of "completeness" of the remediation process.

Point(s) of Contact                                                                      
    C. M. (Mike) Reynolds
Technical lead
ERDC-CRREL
72 Lyme Road
Hanover, NH United States
Telephone: (603) 646-4394
Fax: (603) 646-4561
E-mail: charles.m.reynolds@erdc.usace.army.mil

Information Source(s):   ESTCP Technology Demonstration Final Report: Field Demonstration of Rhizosphere-Enhanced Treatment of Organics-Contaminated Soils on Native American Lands with Application to Northern FUD Sites. Reynolds, C.M., ERDC-CRREL, Hanover, NH. Report No. ERDC/CRREL/LR-04-18, 97pp, June 2004
http://www.crrel.usace.army.mil/techpub/CRREL_Reports/reports/LR-04-18.pdf

Reynolds, C.M. 2004. ESTCP Technology Demonstration Final Report: Field Demonstration of Rhizosphere-Enhanced Treatment of Organics-Contaminated Soils on Native American Lands with Application to Northern FUD Sites. ERDC-CRREL, Hanover, NH. Report No ERDC/CRREL/LR-04-18, 97 p. Reported in Technology Innovation News Survey - February 16-28, 2005.
http://www.clu-in.org/products/tins/

EPA. Federal Remediation Technologies Roundtable. 2005. Technology Cost and Performance Report: Rhizosphere-Enhanced Bioremediation of Petroleum, Oil and Lubricant (POL)-Contaminated Soils at Three Sites in Alaska.
http://costperformance.org/pdf/20050614_367.pdf

EPA. Federal Remediation Technologies Roundtable. 2005. Technology Cost and Performance Report Summary: Rhizosphere-Enhanced Bioremediation of Petroleum, Oil and Lubricant (POL)-Contaminated Soils at Three Sites in Alaska.
http://costperformance.org/profile.cfm?ID=376&CaseID=376

 

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