DOE Mound Facility, Miamisburg, OH 

1997

James Johnson 937-847-5234 james.o.johnson@em.doe.gov 

Air Sparging

DOE Ohio Sites Technology Coordination Group (STCG) Miamisburg

Ground water VOCs In situ     Demonstrated Air Sparging/Vapor Extraction www.ohio.doe.gov/oh-stcg/ 
DOE Demo
Hanford Reservation, WA

Steve Stein
(206) 528-3340

Air Sparging Ground water VOCs In situ - In well air stripping Surfactants or catalysts added if needed Requires air-stream treatment Eliminates need for disposal or storage of partially treated water.
Amoco Petroleum Pipeline
Constantine, MI
Air Sparging, Dual Phase Extraction and GAC to recover free product and treat ground water. 775 million gallons of ground water 300,000 to 2 million gallons of gasoline, fuel oil, and kerosene In situ air sparging was subsequently added to treat the saturated zone. 4 extraction wells and 30 air sparging wells were installed. 2 GAC vessels in series 118,000 gallons of free product recovered   Capital Cost: $297,000 for ground water recovery and treatment, $375,000 for air sparging.
Annual Operating Cost: $475,000
$3 per 1,000 gallons of ground water treated.
Fort Drum,
Watertown, NY

Remedial Project Manager
Fort Drum Environmental Division

Air Sparging, Free product recovery and GAC Ground water   Full-scale remediation to recover free-phase petroleum product using ground water extraction and air stripping and GAC 2 recovery wells were installed and 2 GAC drums were used in series.   Total Capital Cost: $958,780; Total annual Operating Cost: $129,440.
Amcor Precast, Ogden, UT

Shelly Quick
Utah DERR

Density driven ground water air sparging and SVE Soil and Ground water Diesel and gasoline fuels TPH (51/190), benzene (1.3/4.7), toluene (2.4/9.4), ethylbenzene (0.78/2.7), total xylene (2.5/8.0), naphthalene (0.18/0.63). In situ 12 ground water sparging wells, 3 downgradient extraction wells, and 3 vertical extraction wells were installed.   Total Capital Cost: $156.950, Total Annual Operating Cost: $62,750.
DOE Integrated Demo,
DOE Savannah River Site, Aiken, GA

Terry Walton
(803) 725-5218

Air Sparging. Organics in soil and ground water at nonarid sites Soils, ground water at nonarid sites, emphasizing in situ remediation Volatile organics such as TCE and PCE Integrated demo includes many technologies - no specific parameters given Directional well drilling precedes the in situ air stripping Offgas treatments also being demonstrated 16,000 lb of chlorinated solvents removed at Savannah River site during a 20-week test period.
Denison Avenue Site, Cleveland, OH 1991

U.S. EPA Region 5 (312) 886-6143

Air Sparging Ground water BTEX       Gas Station
Wayne Reclamation and Recycling, IN

Duane Heaton (312) 886-6399

Air Sparging Ground water TCE, DCE, Vinyl Chloride, BTEX Injection and extraction - In situ Installation of injection wells. Volatilization and vapor extraction. Municipal Landfill, oil reclamation. In operational stage since June 1995.
Rochester Property, SC

Sherri Panabaker (404) 347-7791

Air Sparging Ground water TCE, Bis-2- ethylhexyl- phthalate       Disposal site. Average depth of treatment approximately 30 ft. Project is in operational stage.
Fairchild AFB, Priority 1 Ous (OU 2) FT-, WA

Cami Grandinetti (206) 553-8696

Air Sparging Ground water BTEX   Vapor extraction system installed in conjunction with an air injection well. Volatilization and vapor extraction Fire training area. Pilot system is in place; may change full-scale design.
South Municipal Water Supply Well, NH

Roger Duwart (617) 573-9628

Air Sparging Ground water PCE, TCA, TCE       Ball bearing manufacturing. Installed. Average depth of treatment approximately 20 feet.
Applied Environmental Services, OU 1, NY

Gerald Ridder (518) 457-0927 Jon Maria (212) 637-3967

Air Sparging Ground water Non-halogenated VOCs, Halogenated VOCs, Non-halogenated SVOCs, PAHs, BTEX   In situ   Bulk petroleum and hazardous waste storage facility, fuel blending. Operational as of June 1995. Completion date unknown.
Mystery Bridge Road/Highway 20, OU 2, WY

Dan Thorton (303) 312-6215

Air Sparging Ground water Benzene, Ethyl benzene, Xylenes 54 wells operated 8 to 15 at a time, 120 cfm, 0.7 - 1.0 inches of water.   Off-gas vented to atmosphere under WDEQ discharge permit. Natural gas compressor station. Depth of treatment approximately 20 ft. Benzene - 9 ug/l to 0.0004 ug/l, ethyl benzene - 0.003 ug/l, and xylenes - 0.008 ug/l. Had to swab wells frequently because of plugging.
Installation Restoration (IR) Site 11, NAS Northern Island, San Diego, CA Terra Vac pilot  SVE/ Air Sparging/ Catalytic Oxidation Systemging Soil Up to 250 pounds (33 gallons) per day of VOCs was effectively removed from the vadose zone  and subsequently destroyed.        
NAS Fallon, NV 1994

U.S. Navy, Public Works Department (702) 426-2772

Bioslurping Ground water TPH       Fuel Farm
Island of San Diego Garcia
AFCEE/PA
3207 North Road
Brooks AFB, TX 78235-5363
Tel: (210) 536-4228
Bioslurping Ground water Fuel (JP-5) It has pulled out over 2,000 gallons of fuel during the first month of operation and about 1,000 gallons every month In situ   Total cost of the system including installation was $60,000
Naval Air Station, Fallon, Nevada

NFESC, 560 Center Drive., Port Hueneme, CA 93043-4301

Bioslurping Ground water Fuel (JP-5) An average of 24 gallons of fuel per day during operation, with a maximum removal rate of 60 gallons per day. Ground water removal has averaged 0.46 gallons per minute In situ   Removed 6,500 gallons of Fuel in 1993
Dry Cleaning Facilities, Hutchinson, KS 

1997 

Douglas Dreiling 316-941-3921

Leo G. Henning 785-296-191

Chemical Oxidation 

Burns & McDonnell Wichita, KS  Kansas 

Kansas Dept. of Health & Env.

 

Ground water PCE   In situ   In Situ Chemical Treatment: Technology Evaluation Report GWRTAC TE-99-01 (p 35) 
Keesler AFB, MS 

1997 

James R. Gonzales 210-536-4324 james.gonzales@hqafcee.brooks.af.mil 

In situ air stripping with horizontal wells

AFCEE/ERT Technology Transfer Div. 3207 North Rd.—Bldg. 532 Brooks AFB, TX 78235

Ground water Ground water In situ      Field Applications of In Situ Remediation Technologies: Ground-Water Circulation Wells EPA 542-R-98-009 (p 6) 
Dry Cleaning Facilities, Hutchinson, KS 

1997

Douglas Dreiling 316-941-3921 

In situ air stripping with horizontal wells

Burns & McDonnell 3839 Dora Wichita, KS 67213

 

Ground water PCE  In situ      Field Applications of In Situ Remediation Technologies: Ground-Water Circulation Wells EPA 542-R-98-009 (p 28) 
DOE Demo
Savannah River Site, SC

7/90-12/90

Mike O'Rear
(803) 725-5541

In situ air stripping with horizontal wells Soil & ground water TCE & PCE Initial concen- trations: 5,000 ppm; stabilized to 200-300 ppm In situ (horizontal wells)

Extraction average 110 lb of VOCs/day

Air injection below aquifer - air extraction above. Off-gas stream $20/lb contaminant removed.
DOE Demo, Seattle, WA

DOE; Michael Lubrecht, Marketing Manager, FlowMole Environmental Services Corp., Kent, WA; Hart Crowser, Seattle, WA (Consulting firm)

Directional Wells Ground water Chlorinated solvents: Tetrachloro- ethylene Two 100 mm diameter stainless-steel, pre-packed ground water extraction wells. In situ Sent to on-site treatment facilities. A 50 mm diameter, pipe-based well screen inside a 100 mm wire-wrapped screen, with graded silica sand filling the annulus between the screens. This allowed excellent filtatration but difficult installation due to stiffness. TCE - 500 to 1000 ppm.
Buchanan, MI 1994

Billings & Associates (505) 345-1116 National Risk Management Research Laboratory (513) 569-7797

Subsurface Volitization & Ventilation System Ground water BTEX, PCE, TCE        
March Air Force Base, CA 1995

Michelle Simon (513) 569-7676 Jeff Bannon (818) 596-6900

UVB - Vacuum Vaporizing Well Ground water TCE - >94% removal, DCE The UVB system consists of a ground water well, a negative pressure stripping reactor, an aboveground mounted blower, and a waste air decontami- nation system.     DCE's removal was not established due to a very low concentration (<4 ug/L).
Lockheed Aeronautical Systems Co.
Burbank, CA

David Bluestein (415) 227-0822

Dual Phase Extraction
AWD AquaDetox/ SVE
System
Soil & Ground water 2.2 ppm TCE; 11 ppm PCE; 6,000 ppm total VOC soil gas. Attained 98-99.99 % removal In situ     $3.2-5.8M capital;
<$1.5M yearly O&M.
Major Car Rental Agency, Los Angeles, CA

Terra Vac Corporation, James Keegan (714) 252-8900

Dual Vacuum Extraction (Dual Phase Extraction) Ground water, Soil Hydrocarbons, TPH Vadose zone soil permeability range of 0.001 to >100 millidarcies Vacuum extraction well includes a screened section in the vadose zone of contaminated soils and ground water. Hydrocarbon product - disposed, re-used, or purified and then re-used. Hydrocarbons - removal of 17,000 lbs., TPH - up to 1,400 ppm. Operation completed in 8 months. Cost - $85K to $500K.
Navy Fuel Farm

Mike Radecki
SOUTH WEST DIV

Free product recovery Ground water 0.5-2.5 ft free product.   Captured in pit and pumped out with skimmers and french drains   $300,000
Privately Owned Gasoline Station Near Urban Drinking Water Source

Connecticut DEP
(203) 566-4630

Free product recovery Ground water Gasoline, BTEX Immediate response from recovery wells and air stripping      
Navy Demo
Seal Beach Navy Weapons Station, CA

1991

Vern Novstrup
(805) 982-2636

Rebecca Coleman-Roush
(805) 644-5892

Ground water vapor recovery system Ground water VOCs In situ - air permitting Injection & extraction wells are placed inside and outside of contami- nation area Waste hydrocarbons to internal combustion engine Treatment requires combustible contaminants. Air permits may be required.

Capital - $70K to $100K.

McClellan AFB Pilot-scale fluid/vapor extraction demonstration. Soil & Ground water VOCs. 1,200 lbs/year for contaminants removal. In situ 95% of the ground water VOCs were transferred to vapor phase.   $160 per pound.
EPA Demo
San Fernando Valley Ground water Basin Superfund Site, CA

1990

Norma Lewis
(513) 569-7665

Integrated vapor extraction & steam vacuum stripping Soil & ground water Initial concentration: up to 2.2 ppm TCE
up to 11 ppm PCE

Removal:
up to 99.9% VOCs

Ground water:
1,200 gpm

Soil gas:
300 ft/min

Ground water:
Steam stripping in tower

Soil: SVE

Carbon should be regenerated every 8 hours Operating for more than 3 years.
Airfield, Lemoore, CA 1994

(805) 982-4191

Steam Injection and Vacuum Extraction Ground water JP-5 (Jet Fuel)        
EPA Demo Huntington Beach, CA

Paul dePercin
EPA RREL

Hot Water or Steam Flushing/ Stripping 45,000 yd³ of soil & goundwater Diesel fuel, TPH, and TRPH

20-40% removal attained

In situ results not good, probably because of poor application rather than technology delivery ineffective- ness   About $40/yd³
EPA SITE demo
Pennsylvania Power & Light
Stroudsburg, PA

Eugene Harris
EPA
(513) 569-7862

Hot Water or Steam Flushing/ Stripping with CROW            
Lawrence Livermore National Laboratory Gasoline Spill Site
Livermore, CA

Kathy Kaufman
University of California (510)422-2646

Hot Water or Steam Flushing/ Stripping Ground water Benzene level in soil greater than 50 ppm. Over 7,600 gallons of gasoline removed during demonstration. In situ 6 steam injection/ electrical heating wells, 3 electrical heating wells, 3 ground water and vapor extraction wells were installed.   Total Treatment Cost: $8,740,000; Before- treatment Cost: $1,700,000
Xerox Facility
Oak Brook, IL
Hydro- fracturing Soil & Ground water VOCs In Situ SVE of organic solvents. 10 times increase in vapor extraction; 30 times increase in area covered; pore water infiltration decreased   $950 - 1,425 per fracture
UST site, Dayton, OH Hydro- fracturing Soil & Ground water BTEX In Situ In situ bio- remediation of BTEX/UST site. 100 times increase in water flow; 75% increase in bio- remediation rate    
Fuel Dispensing Area 1595, Watertwon, NY 1994

Fort Drum Environmental Division, Watertown, NY

Ground water Extraction & Air Stripping Ground water BTEX       Underground Storage Tanks
Lawrence Livermore National Laboratory
1993
(510)422-2646 UCA, Office of Tech Transfer (510) 748-6595
Dynamic Underground Stripping Groundwater BTEX, FHC, Benzene       Gasoline Spill Site, Underground Storage Tanks
Site Demo
March AFB, CA

Michelle Simon
EPA RREL
(513) 569-7469
Jeff Bannon
WESTON
(818) 556-5226

In-Well Air Strippings: air lift pumping, in situ vapor stripping, and air sparging Soil & Ground water 30 ppb TCE at well inlet

Attained < 1 ppb of TCE

In Situ      
Installation Restoration (IR) Site 9, NAS Northern Island, San Diego, CA EG&G  NoVOCsTM  in-well stripping technology Ground water          
Savannah River Site, GA 1994

National Risk Management Research Laboratory (513) 569-7631

High-Energy Electron Irradiation Ground water Chlorinated Solvents and Fuels        
Westinghouse Savannah River Site, Aiken, SC 

1997

Mark Phifer 803-725-5222 mark.phifer@srs.gov 

Passive Treatment Wall

Westinghouse Savannah River Co. Aiken, SC

Ground water TCE, cDCE, CT, NO(III)  In Situ     TNX GeoSiphon Cell Phase I Deployment/Demonstration WSRC-TR-98-00032
Former Plating Facility, NY 

1997

Diane Clark 315-655-8161 diane.clark@stearnswheler.coom 

Passive Treatment Wall

Stearns & Wheler One Remington Park Dr. Cazenovia, NY 13035

Ground water TCE, cDCE, VC  In Situ     Field Applications of In Situ Remediation Technologies: Permeable Reactive Barriers EPA 542-R-99-002 (p 37) 
Lowry AFB, CO

1997

William A. Gallant 303-452-5700 gallabil@versar.com 

Passive Treatment Wall

Versar, Inc. 11990 Grant St., Ste. 500 Northglenn, CO 80233

Ground water TCE In Situ     Field Applications of In Situ Remediation Technologies: Permeable Reactive Barriers EPA 542-R-99-002 (p 27) 
NAS Moffett Field, CA  

1997

Charles Reeter 805-982-4991 reetercv@nfesc.navy.mil 

Passive Treatment Wall

U.S. Navy - NFESC 1100 23rd. Ave., Code 411 Port Hueneme, CA 93043-4370

Ground water TCE, PCE, DCE  In Situ     “Permeable Reactive Wall Remediation of Chlorinated Hydrocarbons in Groundwater: NAS Moffett Field, Mountain View, California,” After the Rain Has Fallen: 2nd International Water Resources Engineering Conference. 1998. (p 153-158)
Tonolli Corporation, PA (Battery Recycling/ Disposal)

Linda Dietz, USEPA, 215-597-6986

Passive Treatment Wall Ground water Heavy Metals: Lead        
Lowry Air Force Base, CO

Richard Muza (EPA Region 8) (303) 312-6595

Iron Reactive Walls Ground water Trichloro- ethylene (1,260 ppb A subsurface wall of iron filings through which the contaminant plume migrates under natural ground-water flow   Degradation products - ethene, ethane, and methane An estimated potential porosity loss of 13 to 14 percent per year due to carbonate and hydroxide precipitate formation.
Somersworth Sanitary Landfill Site, NH (Industrial Landfill/ Municipal Landfill)

Roger Duwart, USEPA, 617-573-9628

Passive Treatment Wall Ground water Non- halogenated volatiles        
Brown's Battery Breaking Site, OU 2, PA (Battery Recycling/ Disposal)

Richard Watman, USEPA, 215-597-8996

Passive Treatment Wall (limestone barrier) Ground water Heavy metals: Lead        
Tonolli Corporation Permeable Reaction Wall

 

Ground water Lead
Cadmium
Arsenic 
Zinc
Copper 
Trench

Limestone

 

Operational    
Somersworth Sanitary Landfill
Permeable Reaction Wall Ground water Trichlorethene (0.005 mg/L)
Vinyl Chloride (0.005 mg/L)
Funnel and Gate

Zero-Valent Iron

Operational    
Rocky Flats Plant (USDOE) - Buffer Zone Permeable Reaction Wall Ground water Carbon Tetrachloride 
Tetrachloroethene 
Trichloroethene 
Funnel and Gate

Zero-Valent Iron

Operational    
Monticello Mill Tailings (USDOE) - Operable Unit 3 Permeable Reaction Wall Ground water Arsenic (0.05 mg/L)
Molybdenum (0.183 mg/L)
Radium 226 (5 pCi/L)
Selenium (0.05 mg/L)
Uranium (1.1 mg/L)
Funnel and Gate

Zero-Valent Iron

Operational    
Lake City Army Ammunition Plant (NW Lagoon) - Operable Unit 3 Permeable Reaction Wall Ground water 1,1-Dichloroethene (0.007 mg/L)
Trichloroethene (0.005 mg/L)
Vinyl Chloride (0.002 mg/L)
Funnel and Gate

Zero-Valent Iron

Operational    
F.E. Wareen Air Force Base - Operable Unit 2 Permeable Reaction Wall Ground water Trichloroethene   Operational    
Brown’s Battery Breaking Site Permeable Reaction Wall

 

Ground water Beryllium (1.9x10-4 mg/L)
Cadmium (8.8x10-4 mg/L)
Lead (<0.003 mg/L)
Manganese (0.05 mg/L)
Nickle (0.0029 mg/L)
Sulfate (0.027 mg/L)
Calcium Hydroxide
Magnesium Hydroxide
Design    
Arrowhead Associates/Scovill Corporation Permeable Reaction Wall

Trench
Ground water Chromium 
Cyanide
Zero-Valent Iron
Design
Design    
Uranium Mine Tailings Site, Fry Canyon, UT

1999

David L. Naftz 801-975-3389 dlnaftz@usgs.gov  

Permeable Reaction Wall

USGS District Office - Salt Lake City, UT

 

Ground water In Situ      
Bodo Canyon Disposal Cell Mill Tailings Site, Durango, CO 

1999

Brian Dwyer 505-845-9894 BPDwyer@sandia.gov 

Permeable Reaction Wall

Sandia National Laboratory Albuquerque, NM

Ground water U, As, Se, Zn, Ra-226, Mo, Mn  In Situ     “In Situ Remediation of Uranium Contaminated Groundwater,” Containment 1997 DE98-001967 (p 835-843) 
Launch Complex B, Cape Canaveral Air Center, FL 

1999

Major Edward Marchand 210-536-4364 

Permeable Reaction Wall

U.S. Air Force Center for Environmental Excellence Brooks AFB, TX

Ground water TCE, DCE, VC  In Situ     Permeable Reactive Barrier Installation Profiles www.rtdf.org/ 
Westing- house Savannah River Site, Aiken, SC 

1998

Mark Phifer 803-725-5222 mark.phifer@srs.gov 

Permeable Reaction Wall

Westinghouse Savannah River Co. Aiken, SC

Ground water TCE, cDCE, CT, NO(III)  In Situ     TNX GeoSiphon Cell (TGSC-1) Phase II Single Cell Deployment/ Demonstration Final Report WSRC-TR-98-00432 
X-231A Site, Portsmouth Gaseous Diffusion Plant, OH 

1998

R.L. Siegrist rsiegris@mines.edu 

Permeable Reaction Wall

ORNL/Colorado School of Mines

Ground water NAPLs, DNAPLs  In Situ     X-231A: A Demonstration of In-Situ Remediation of DNAPL Compounds in Low Permeability Media by Soil Fracturing with Thermally Enhanced Mass Recovery or Reactive Barrier Destruction: Dense Non-Aqueous Phase Liquids ORNL/TM-13534 
LEAP Permeable Barrier Demonstration Facility, Portland, OR

1998

Robert Bowman 505-835-5992 bowman@nmt.edu 

Permeable Reaction Wall

New Mexico Tech Socorro, NM

Ground water PCE, Cr(VI)  In Situ     Field Applications of In Situ Remediation Technologies: Permeable Reactive Barriers EPA 542-R-99-002 (p 39) 
100 HR-3 Operable Unit, Hanford Reservation, WA 

1998

John Fruchter, PI 509-376-3937 js_fruchter@pnl.gov 

Permeable Reaction Wall

PNNL

Ground water Cr(VI)  In Situ     In Situ Redox Manipulation [fact sheet] 
Canadian Forces Base, Canada 1993

Waterloo Centre for Ground Water Research (519) 885-1211 Centre for Excellence (416) 323-4476

Permeable Reaction Wall Ground water TCE, PCE, DCE        
Borden Aquifer, Canada 1994

Waterloo Centre for Ground Water Research (519) 885-1211 Centre for Excellence (416) 323-4476

Permeable Reaction Wall Ground water BTEX, Benzene and Toluene        
Air Force Demo Hill AFB, UT

Maj. Mark Smith USAF
Tyndall AFB, FL
(904) 283-6126

"Funnel and Gate" Passive Treatment Wall Ground water          
Los Alamos
National Laboratory

Ken Bostick
Mail Stop J495 Organization EES-15
Los Alamos National Laboratory

Passive Treatment Wall Barriers and post-closure
monitoring completion
Ground water         $1.2M cap.
$670K O&M
in FY93

Sources: Innovative Treatment Technologies: Annual Status Report ( Eighth and Tenth Editions, Nov. 1996 and Feb. 2001). Innovative Remediation Technologies: Field-Scale Demonstration Projects in North America (1st and 2nd Editions, Aug 1996 and Jun 2000).