Addendum: An Assessment of 

Environmental Problems Associated with Recycling of 

Hazardous Secondary Materials

Appendix 1: Additional Damage Cases from Recycling of 

Hazardous Secondary Materials
June 2011

i

Appendix 1 Contents

Additional Damage Cases from Recycling of 

Hazardous Secondary Materials

Site Name State

Romic Environmental Technologies Arizona

Romic Environmental Technologies California

Hassan Barrel Company, Inc.* Indiana

American Iron Oxide Company (AMROX) Pennsylvania

Horsehead Resource Development Corporation Pennsylvania

Blue Ridge Solvents and Coatings, Inc. Virginia

* Damage cases are cited in An Assessment of Environmental Problems Associated with Recycling of Hazardous 

Secondary Materials (2007) and updated with new information.
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2

Site Name: Romic Environmental Technologies, Chandler (Romic 

Southwest)

EPA ID No.: AZD009015389

Address: 6760 West Allison Road, Chandler, AZ 85226

County: Maricopa

NPL Site: No

In CERCLIS Database: No

Site History and Description of Recycling Operation: Romic Environmental Technologies (Romic) 

operated an approximately three-acre hazardous waste storage, treatment, and recycling facility in the 

Lone Butte Industrial Park near Chandler Arizona. This industrial park is located within the Gila River 

Indian Community (GRIC), on lands held in trust for GRIC. 

The facility began operation in 1975 under ownership of Southwest Solvents. In 1988, Romic 

purchased the facility from Southwest Solvents and continued operations, which were primarily solvent 

recycling through distillation. The facility received on average about 13,000 tons of waste per year, 

about half of which was considered hazardous by the USEPA. Wastes received by the facility came 

from a variety of industries, including dry cleaning, paint manufacturing, aerospace, and automotive 

industries. The facility also received household hazardous wastes from collection events. In addition to 

solvent recycling, the facility acted as an intermediate facility, including consolidating solids for off-site 

transfer and disposal and conducting fuel blending. Other site activities included antifreeze recycling

and other management methods. No wastes were disposed on site; all wastes were transferred off site 

for disposal or re-use. 

In 1981, Southwest Solvents submitted Part A of a RCRA hazardous waste permit application and was 

granted interim status by the USEPA. The facility continued to operate under interim status until Romic 

acquired the facility in 1988. At that time, Romic submitted a revised Part A application as well as the 

more extensive Part B application for a permit. The facility remained under interim permit status 

pending further review by the USEPA. During this period, Romic complied with a number of RCRA 

requirements including completion of a number of remediation activities to clean up contamination, and 

conducted a remedial investigation (RI) in 2004. In 2005, Romic was fined $67,888 for multiple 

hazardous waste violations related to improper storage and labeling of hazardous waste and other 

violation. The company corrected the violations and also spent $100,800 on life-saving equipment for 

the Gila River Indian Community Fire Department and air monitoring and meteorological equipment 

for the Gila River Indian Community Department of Environmental Quality. 

Also in 2005, Romic submitted a final revised Part B application. However the landowner, GRIC, 

would not sign the application and therefore the permit application was denied in 2007. Romic then 

submitted a facility closure plan, which was approved in 2008. Romic is currently conducting site 

cleanup activities.

Description of Contamination: In 2007, the USEPA issued an Administrative Order of Consent 

(AOC) to Romic to investigate contamination on and around the site. It is believed that the groundwater 
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Recycling of Hazardous Secondary Materials

3

contamination at the Romic facility may be related to the operations of Southwest Solvents, which 

operated the facility prior to 1988 (3). 

In accordance with a 1988 Consent Agreement, Romic conducted extensive soil cleanup upon 

purchasing the facility. However, a 2004 Remedial Investigation Report completed for the GRIC 

Department of Environmental Quality (DEQ) indicated that trichloroethylene (TCE), 

tetrachloroethylene (PCE), and 1,1-dichloroethylene (1,1-DCE) contamination in groundwater was 

above U.S. EPA Maximum Contaminant Levels (MCLs) close to and down gradient from the facility. 

Although the facility operated in an industrial park, its location is approximately 200 meters from a 

public drinking water well and up-gradient from irrigation wells. 

Due to the RCRA permit denial, Romic prepared a closure plan in 2008 for cleanup of surface 

contamination. Under this plan, Romic will remove all remaining wastes, clean and decontaminate 

remaining equipment and structures, and send the resulting waste offsite for treatment and disposal. 

The estimated cost of this portion of the site cleanup is $900,000 (8). Information about the costs of 

earlier site remedial activities is not available from the sources used for this damage case. Romic is 

working with U.S. EPA and GRIC DEQ to further investigate and implement corrective actions to 

address ground water contamination (8).

Sources of Information:

1. USEPA. Facility Registry System, Facility Detail Report. Romic Environmental Technologies

Corporation Southwest. Accessed Online. May 2011: 

http://oaspub.epa.gov/enviro/fii_query_dtl.disp_program_facility?pgm_sys_id_in=AZD009015

389&pgm_sys_acrnm_in=RCRAINFO

2. USEPA. Envirofacts, Multisystem, Romic Environmental Technologies Corp Southwest. 

Accessed Online. May 2011: 

http://iaspub.epa.gov/enviro/multisys2_v2.get_list?facility_uin=110000471249

3. USEPA. Region 9, Waste Programs. Romic Environmental Technologies Corporation 

Southwest Hazardous Waste Storage and Treatment Facility. Accessed Online. May 2011: 

http://www.epa.gov/region09/waste/romic/index.html#correctiveaction

4. USEPA. “Permit Series List.” RCRAInfo. May 2011.

5. USEPA. Region 9: Administrative Order On Consent. Romic Environmental Technologies 

Corporation. Accessed Online. May 2011:

http://www.epa.gov/region09/waste/romic/index.html#correctiveaction

6. USEPA. Notice of Intent to Deny a RCRA Permit Application for Romic Environmental 

Technologies Corporation – Southwest. August 2007. Accessed Online. May 2011:

http://www.epa.gov/region9/waste/romic/pdf/proposed-permit-decision.pdf
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7. USEPA. News Release: EPA fines hazardous waste company on Arizona tribal lands $67,888. 

August 2005. Accessed Online. May 2011: 

http://yosemite.epa.gov/opa/admpress.nsf/9e50770d29adb32685257018004d06fd/9da557d9afa

35dde852570d8005e178a!OpenDocument&Highlight=0,romic

8. Romic Environmental Technologies Corp. Romic Southwest Facility. Closure Plan. Submitted 

to US Environmental Protection Agency Region 9. August 2008. Accessed Online. May 2011: 

http://www.epa.gov/region09/waste/romic/pdf/RSW-Closure-Plan-final-August-2008.pdf
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Recycling of Hazardous Secondary Materials

5

Site Name: Romic Environmental Technologies, E. Palo Alto, CA

EPA ID No.: CAD009452657

Address: 2081 Bay road, East Palo Alto, CA, 94303

County: San Mateo

NPL Site: No

In CERCLIS Database: CAN000908403 

Site History and Description of Recycling Operation: The Romic Environmental Technologies 

(Romic) facility in East Palo Alto, California, is a 12.6-acre former hazardous waste management 

facility. It is located in an industrial area approximately half mile west of San Francisco Bay. The 

facility fence line borders tidal marshes and other industrial facilities. The nearest residences are about 

2,000 feet to the west, with the closest school being about a half mile. 

The site first began operation as a chemical storage facility under previous owners in 1956. Romic 

began operating the facility in 1963, purchased it in 1979, and continued to operate it until it closed in 

2007. Romic performed a combination of hazardous waste storage, treatment, and recycling operations 

and received hazardous waste from a number of industrial business, including wastes such as paint 

thinner and paints, antifreeze, oils, inks, adhesives, and solvents. Waste management methods included 

storage, solvent recycling using distillation, incineration, and other treatment. In addition, waste 

management method information included in the facility’s biennial hazardous waste reports indicate 

that the facility also served as an intermediate facility for some wastes. Prior to closure, the facility 

managed an estimated 35,000 tons of waste per year.

The Romic facility has a history of violations and incidents including a 2006 tanker truck spill, 

employee burn incidents in 2004 and 2006, and a 2007 transporter incident. The 2006 spill involved 

4,000 gallons of used, mixed organic solvents, including hydroxylamine, monoethanolamine, toluene, 

and acetronitrile. The solvents began reacting inside the tanker truck resulting a release of a fine mist 

that settled over an empty lot owned by Romic, portions of Bay Road, and adjacent parcels that 

included a Pacific Gas and Electric (PG&E) substation and nearby wetlands. In both of the burn 

incidents, employees were burned by ignitable vapors that were not properly drained from tanks other 

equipment. In the 2007 transporter incident, a highway exit ramp in Bakersfield, California, was shut 

down for several hours due to leakage from a truck containing drums shipped from the Romic facility.

The facility also was subject to a 2005 settlement with the California Department of Toxic Substances 

Control (DTSC) for a number of violations that occurred from 1999 to 2004. Because of this history of 

violations, in 2007 the DTSC ordered Romic to close the facility and implement its cleanup plan. The 

facility stopped accepting waste in 2007, and all stored hazardous waste was removed from the site that 

year. 

Description of Contamination: DTSC and U.S. EPA site investigations concluded that Romic’s 

operations contaminated soil and groundwater across most of the site and to a depth of at least 80 feet. 

The primary contaminants are volatile organic compounds (VOCs), such as the solvent trichloroethene. 

The soil and groundwater contamination is primarily attributed to the spills, overflows, flooding events, 
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Recycling of Hazardous Secondary Materials

6

and other accidental releases around the central process area. A groundwater extraction and treatment 

system was operated as a site remediation strategy from 1993 until 2005. From 2003 – 2005 Romic 

conducted enhanced reductive dechlorination to remediate groundwater.

Following closure in 2007, the DTSC, U.S. EPA, and Romic agreed to a closure and cleanup plan for 

the facility consisting of two phases. Phase 1, which was overseen by DTSC and was completed in 

2010, involved the closure, cleaning, and removal of the aboveground waste management units and 

equipment, as well as and cleanup of surface contamination. Phase 2, which is underway with U.S. EPA 

supervision, addresses the remediation of subsurface soil and groundwater. The Final Remedy to 

address soil and groundwater contamination will use enhanced biological treatment, monitored natural 

attenuation, excavation, and removal of contaminated soils, land use restrictions, and maintenance of 

the existing site cover. The estimated cost for closure and cleanup of the facility is $2.5 million. 

Sources of Information:

1. USEPA. Facility Registry System, Facility Detail Report. Romic Environmental Technologies 

Corporation. Accessed Online. May 2011: 

http://iaspub.epa.gov/enviro/fii_query_dtl.disp_program_facility?pgm_sys_id_in=CAN000908

403&pgm_sys_acrnm_in=CERCLIS

2. USEPA. Superfund Site Information. Romic East Palo Alto. Accessed Online. May 2011: 

http://cumulis.epa.gov/supercpad/cursites/csitinfo.cfm?id=0908403

3. USEPA. Pacific Southwest, Region 9, Waste. Romic Environmental Technologies, East Palo 

Alto, CA. Accessed Online. May 2011: http://www.epa.gov/region9/waste/romiceastpaloalto/#moreinfo

4. USEPA. “Permit Series List.” RCRAInfo. May 2011.

5. California Department of Toxic Substance Control. Fact Sheet. Romic’s Draft Closure Plan 

Open for Public Comment. April 2008. Accessed Online. May 2011: 

http://www.dtsc.ca.gov/HazardousWaste/Projects/upload/Romic_FS_DClosurePlan_0408.pdf

6. USEPA. US EPA Selects Final Cleanup Plan for Former Romic East Palo Alto Facility. July 

2008. Accessed Online. May 2011: http://www.epa.gov/region9/waste/romiceastpaloalto/pdf/Romic-Final-Decision-FactSheet-Eng-0708.pdf

7. Final Draft: Comprehensive Site-Wide Sampling and analyses Plan, Former Romic 

Environmental Technologies Corporation Facility. Prepared for Bay Enterprises, Prepared by 

Iris Environmental. March 2011. Accessed Online. May 2011: 

http://www.epa.gov/region9/waste/romic-eastpaloalto/pdf/romic-epa-samp_anal-plan.pdf

8. California Department of Toxic Substance Control. Romic Environmental Technologies 

Corporation, Enforcement Order. 2007. Accessed Online. May 2011: 

http://www.dtsc.ca.gov/HazardousWaste/Projects/upload/ROMIC_ENF_EO_2007.pdf
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9. Official Announcement and Shut-down order on Romic. Palo Alto Online. May 2007. 

Accessed Online. May 2011: http://www.paloaltoonline.com/news/show_story.php?id=5146
Addendum Appendix 1 June 2011

Additional Damage Cases from

Recycling of Hazardous Secondary Materials

8

Site Name: Hassan Barrel Company Inc

EPA ID No.: IND078902202

Address: 1605 Summer Street, Fort Wayne, IN, 46857

County: Allen

NPL Site: No

In CERCLIS Database: INN000509942 

Site History and Description of Recycling Operation: From 1954 to 2003, the Hassan Barrel 

Company in Fort Wayne, Indiana, operated as a barrel recycling facility that cleaned and repainted used 

industrial barrels. During its years of operation, the seven-acre facility received barrels, many 

containing hazardous wastes, from at least 400 companies. The facility closed in 2003 and the facility 

owner abandoned thousands of barrels and other hazardous waste on the site. 

Management of waste at the site included disposal in open pits and manmade lagoons, both in drums 

and discharges of liquids (l). The company did not have a RCRA Treatment, Storage and Disposal 

permit, and the State of Indiana had cited the company for a number of state violations between 1982 

and 2003. Citations had been issued by the state for improper records, lack of emergency planning, and 

improper container marking or labeling, among other issues. 

Description of Contamination:

The facility was located in a residential area, surrounded primarily by private homes and two schools 

only a few blocks away. EPA’s site investigation found hazardous wastes at locations around the site, 

including wastes in leaking barrels, dumpsters, and open pits. EPA testing of soil and water in an onsite 

ditch that flowed to a nearby stream were contaminated with a number of hazardous materials including 

barium, cadmium, chromium, lead, and traces of PCBs. EPA also determined from seized records that 

testing on the site while still in operation had found dichloroethene, tetrachloroethane and 

trichloroethene in soil. EPA commenced emergency cleanup of the facility under CERCLA authority, 

spending $1.7 million between 2004 and 2008, and removing 10,000 barrels, about half of which 

contained hazardous waste. As of 2008 EPA expected at least another $1.3 million to removing up to 

10,000 cubic yards of contaminated soil and other waste. 

 

In 2008 Alan Hersh, the president of Hassan Barrel Company, pleaded guilty to one felony RCRA 

violation for the illegal storage and management of hazardous wastes on the site. This sentence included 

15 months in prison and a $1.7 million dollar fine for the EPA for cleanup costs. In addition, EPA is 

seeking additional funding for cleanup costs from about 400 companies that sent materials to the 

facility.

Sources of Information:

1. Iacone, Amanda. Waste has property over a barrel: County Not Jumping to buy Chemically 

Tainted Site. The Journal Gazette. May 24 2009. Accessed Online. May 2011: 

http://www.journalgazette.net/article/20090524/LOCAL/305249918/1002/LOCAL
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2. Stockman, Dan. Used-barrel business leaves Toxic Legacy. The Journal gazette. March 8 2009. 

Accessed Online. May 2011:

http://www.journalgazette.net/apps/pbcs.dll/article?AID=/20090308/LOCAL10/303089920

3. Fort Wayne Recycler Gets Jail Time. Wane.com. March 3 2009. Accessed Online. May 2011: 

http://www.wane.com/dpp/news/local_ap_toxic_waste_sentencing_200903030725_rev1

4. USEPA. Superfund Site Information. Hassan Barrel Site. Accessed Online. May 2011: 

http://cumulis.epa.gov/supercpad/cursites/cactinfo.cfm?id=0509942

5. USEPA. Region 5 Enforcement and Compliance. March 2009 Significant cases. Accessed 

Online. May 2011: http://www.epa.gov/region5/enforcement/cases/cases200903.html#fort

6. USEPA. “Permit Series List.” RCRAInfo. May 2011.

7. USEPA. On Scene Coordinator, Pollution Report Profile. Hassan Barrel Company. Accessed 

Online. May 2011: 

http://www.epaosc.org/site/polrep_profile.aspx?site_id=1136&counter=1846
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Site Name: American Iron Oxide Company (AMROX)

EPA ID No: PAR000008367

Address: 2 Wheeling Pittsburgh Steel Drive, Allenport, PA 15412

County: Washington

NPL Site: No

In CERCLIS Database No

Site History and Description of Recycling Operation: The AMROX facility in Allenport, 

Pennsylvania, began recycling spent pickle liquor from steel manufacturing in 1995 and the facility 

currently continues this operation. Pickle liquor contains hydrochloric acid and is used in steelmaking 

to remove iron scale buildup from the surface of the steel. AMROX recycles spent pickle liquor into 

hydrochloric acid and iron oxide.

AMROX uses a pyrohydrolysis to generate an 18% by weight hydrochloric acid solution. AMROX 

also uses an IROX process to remove silica and metals from the spent pickle liquor in order to produce 

a higher purity iron oxide. 

From 1995 until 1999, AMROX accepted spent pickle liquor under two regulatory mechanisms: Spent 

pickle liquor from designated generators that met certain chemical parameters was deemed a 'coproduct' and was exempt from Pennsylvania Department of Environmental Protection’s (PADEP) 

requirements pertaining to solid and hazardous waste. Spent pickle liquor that was not deemed a coproduct, either because it did not meet the designated chemical parameters or was not produced by a 

designated generator, was accepted by AMROX as a hazardous waste pursuant to a 'hazardous waste 

storage permit-by-rule.' 

PADEP adopted most of the EPA RCRA regulations in 1999, eliminating the regulations under which 

AMROX had been operating. At that point, PADEP allowed AMROX to continue recycling spent 

pickle liquor under a variance authorized under 40 CFR 260.31(b). 

Although the PADEP believes that the facility would qualify as a recycler of hazardous secondary 

materials, AMROX has not submitted a notification for this designation. However, the variance only 

allows AMROX to accept spent pickle liquor from specific generators, rather than any "hazardous 

secondary materials." The variance requires that to qualify as legitimate recycler AMROX must 

demonstrate that it sells the produced iron oxide and returns the regenerated acid back to the steel 

plants. 

Description of Contamination: In September 1997, AMROX allowed hazardous waste sludge from 

their IROX process to spill onto the ground. Instead of properly containing and collecting this release, 

AMROX washed the waste into an adjacent railroad bed. PADEP fined AMROX $55,000 for this 

violation. In 2004, AMROX's two storage tanks failed and spilled the spent pickle liquor into the 

surrounding asphalt-paved area and into the storm drain. The storage tanks are located only 50 feet 

from a playground (see Figure 1). DEP was also concerned about air pollution from metals in the spent 

pickle liquor which is why the variance contains limits on metal concentration in the spent pickle 

liquor. PADEP entered into a consent order and agreement with AMROX in August 2005 under which 

AMROX agreed to resolve various tank and waste issues, including establishing an inspection/repair 
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schedule the remaining acid tanks. In 2006, PADEP fined AMROX $150,000 for outstanding air, 

waste, and water violations involving the release of acid and iron oxide into the environment.

On Aug. 11, 2009, PADEP discovered a 32,000-gallon discharge of pickle liquor during a routine site 

visit. The discharge mixed with process water and stormwater to flood the containment unit beneath 

the tanks. Tests taken around the tanks at the time of the discovery indicated pH levels ranging from 

zero to one, a range consistent with hydrochloric acid, which is a major component of the pickle liquor 

AMROX manages.

Figure 1. Ruptured Tank at the AMROX Facility and Nearby Community Playground

PADEP reviewed the company’s inspection records and learned of multiple and persistent leaks from 

five of the ten tanks in operation from May 23 to August 6, 2009. These issues were in addition to 

defects that have required repair over the previous four years, including interior and exterior cracks and 

patch failures. 

On or about April 18, 2011, an aboveground storage tank at the facility split open, releasing 

approximately 27,300 gallons of regenerated hydrochloric acid solution, with a pH of less than 1.0. At 

the time of the release, the emergency containment area at the facility contained accumulated water and 

was not able to contain the released volume of hydrochloric acid, and hydrochloric acid overflowed 

from the emergency containment area.

PADEP issued an Administrative Order on April 27, 2011, requiring AMROX to evaluate several acid

tanks at the facility. Among other things, the April 27, 2011 Administrative Order required AMROX to 
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12

reduce the volume by half within eight remaining tanks, and demonstrate that it would be safe to allow 

the tanks to continue in operation. AMROX did reduce the contents of the tanks to 50% of their 

capacity, but failed to document the integrity and fitness for operation of the tanks. On May 11, 2011, 

PADEP and a retained expert inspected the failed tank and could not identify an obvious cause for the 

failure. On May 5 and May 11, 2011, the PADEP observed acid continuing to leak from various tanks, 

as well as deteriorated concrete supports beneath one or more of these tanks. On May 12, 2011 PADEP 

ordered AMROX to empty several older acid tanks. AMROX subsequently provided an engineering 

analysis that with the installation of additional reinforcing bands around each tank that the tanks would 

remain structurally sound at 50% capacity. PADEP issued a third order on May 18, 2011 requiring an 

accelerated series of tank inspections and a failure analysis of the damaged tank.

Sources of Information:

1. AMROX Commonwealth Court Decision. Excerpt provided by EPA.

2. AMROX EHB decision. Excerpt provided by EPA.

3. Commonwealth of Pennsylvania Department of Environmental Protection. “American Iron 

Oxide to Pay $150,000 to Settle Outstanding Violations.” 24 October 2006. 

http://www.portal.state.pa.us/portal/server.pt/community/newsroom/14287?id=1040&typeid=1

4. Commonwealth of Pennsylvania Department of Environmental Protection. “DEP Orders 

AMROX to Allow Independent Above Ground Tanks Inspections.” 31 August 2009. 

http://www.portal.state.pa.us/portal/server.pt/community/newsroom/14287?id=2348&typeid=1

5. Commonwealth of Pennsylvania Department of Environmental Protection. Order in the matter 

of American Iron Oxide Company, Allenport Borough, Washington County, Storage Tank and 

Spill Prevention Act, Enf. Id No. 270438. 12 May 2011.

6. Leadbetter, Honorable Bonnie Brigance. Opinion in the Commonwealth Court of 

Pennsylvania, Wheeling-Pittsburgh Steel Corporation and American Iron Oxide Company, 

Petitioners v. Department of Environmental Protection. 6 August 2009. 

http://www.aopc.org/OpPosting/Cwealth/out/1297CD08_8-6-09.pdf

7. Spadaro, Carl. Commonwealth of Pennsylvania Department of Environmental Protection. 

Personal communication (email) with Amanda Geldard, U.S. Environmental Protection 

Agency, March 12, 2010.
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Site Name: Horsehead Corporation

EPA ID No: PAD004372363, PAD981110570

Address: 300 Frankfort Road, Monaca, PA 15061

County: Beaver

NPL Site: No

In CERCLIS Database PAD981110570 (Archived site)

Site History and Description of Recycling Operation: The Horsehead Corporation’s facility in 

Monaca, Pennsylvania, operates as a secondary zinc smelter. Located 28 miles north of Pittsburgh, the 

electrothermic zinc smelter at this facility began operation in the 1920's to produce zinc metal and zinc 

oxide, including recycling materials containing zinc. For several years to the present, this facility only 

uses secondary zinc materials such as dross and skims from galvanizing operations as well as recycled 

K061 electric arc furance dust as feedstock for zinc smelting. In 1996, PADEP clarified that these zinc 

secondary materials would be classified as coproducts under the current PADEP waste regulations. At 

present, those secondaries that might exhibit a hazardous characteristic for lead or cadmium leachability 

would be classified as by-products being reclaimed (40 CFR 261.2(c)(3)). Horsehead’s zinc secondaries 

outdoor storage area has been subject to periodic wind dispersal and contaminated run-off problems. 

Description of Contamination: On July 22, 2010, there was an explosion at the zinc refinery resulting 

in the death of two people. No fire or offsite contamination has been documented as result of this 

incident. The cost of repairs and cleanup totaled $6.8 million for the refinery explosion. Following the 

explosion, the zinc refinery was shut down for repairs and an investigation and assessment of the 

damage. The cause of the explosion is still under investigation. Each of the ten columns used to produce 

zinc oxide and refined zinc metal in the refining facility have since been redesigned and rebuilt, and 

production resumed in the fourth quarter of 2010. As stated above, Horsehead’s zinc secondaries 

storage area has had periodic wind dispersal and run-off problems.

Sources of Information:

1. Horsehead Corporation. Monaca, PA. Retrieved May 24, 2011, from 

http://www.horsehead.net/facility_content.php?ID=12

2. SEC Filings. (2011, March 16). Horsehead Holding Corp. Retrieved May 24, 2011, from 

http://www.sec.gov/Archives/edgar/data/1385544/000095012311025813/l42109e10vk.htm

3. WTAE. (2010, July 26). Explosion at Horsehead Zinc Plant Kills 2; Victims Identified. 

WTAE.com. Retrieved May 24, 2011, from http://www.wtae.com/r/24357952/detail.html
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Site Name: Blue Ridge Solvents and Coatings, Inc.

EPA ID No: VAR000503656

Address: PO Box 759, Henry, Virginia 24102

County: Franklin

NPL Site: No

In CERCLIS Database No

Site History and Description of Recycling Operation: Established in 2002, Blue Ridge Solvents & 

Coatings, Inc., manufactures and delivers industrial chemicals, paints, lacquers, thinners, powder 

coating, and water treatment chemicals. The company also recycles solvents using distillation and thin 

film evaporation. The facility contains storage and mixing tanks and solvent recovery equipment. 

On April 7, 2010 the Commonwealth of Virginia Department of Environmental Quality (VADEQ) 

conducted a compliance evaluation of the facility, and found that the facility had failed to maintain 

records required under its permit. These records include monthly inspections for the fabric filter, logs of 

monitoring device observations for the thin film evaporator and microwave distillation unit, monthly 

and annual Hazardous Air Pollutant and Volatile Organic Compound (VOC) emissions, and scheduled 

and non-scheduled maintenance and operator training. The facility agreed to pay a $7,826 fine to settle 

the violations. A fire occurred at the facility on June 4, 2010, causing property damage and requiring 

the evacuation of nearby homes. 

Description of Contamination: On June 4, 2010 a fire started occurred in a mixing room, resulting in 

explosions from propane cylinders and chemicals. Firefighters extinguished the blaze within two hours. 

No injuries were reported. The fire was contained to the mixing room, which is a block and concrete 

building with a steel roof. A portion of the roof collapsed, but the storage tanks inside the room held 

their contents. Adjacent sections of the building sustained smoke and water damage. 

Twenty residents who lived within a quarter-mile of the facility were evacuated from their homes and 

taken to emergency shelters for about two hours while firefighters battled the fire.

USEPA Region III and VADEQ are considering whether additional information or sampling at the 

facility is required or if corrective action is required by the facility. 

Sources of Information:

1. Commonwealth of Virginia Department of Environmental Quality. State Air Pollution Control 

Board Enforcement Action – Order by Consent Issued to Blue Ridge Solvents & Coatings, Inc. 

24 June 2010. 

http://www.deq.virginia.gov/export/sites/default/enforcement/finalordersII/BRSCJune282010.p

df

2. Wagoner, K.A. The Franklin News Post. “BREAKING NEWS: Fire forces evacuation of 20 

Henry residents.” 4 June 2010. http://www.thefranklinnewspost.com/article.cfm?ID=16449
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3. U.S. Environmental Protection Agency. “Blue Ridge Solvents and Coatings.” 28 June 2010. 

http://www.epa.gov/reg3wcmd/ca/va/pdf/vad003124625.pdf