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TechData
Sheet
Naval Facilities Engineering Service
Center
Port Hueneme, California 93043-4370
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| TDS-ENV - October 1999 |
Asbestos - Polychlorinated Biphenyl Conversion System
Generation I: PCB - ACM
Destruction Mobile Unit |
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The
Naval Facilities Engineering Command, through its Engineering
Service Center (ESC) and Engineering Field Activity
are showing their commitment to ensure environmental
excellence by demonstrating new and innovative technologies.
This technical data sheet focuses on a thermochemical
process that mineralogically converts hazardous wastes
[asbestos-containing material (ACM) contaminated with
polychlorinated biphenyl's (PCBs)] to inert stable non-hazardous
material. A demonstration of this technology at the
Puget Sound Naval Shipyard (PSNS) is the result of a
congressionally mandated BAA award. Asbestos Recycling
Inc. (ARI) of Kent, Washington developed this technology
and is partnering with PSNS to demonstrate it for the
Navy.
Technology
Description - The Navy is required to properly dispose
of hazardous PCB-ACM waste generated from facility abatement
and ship maintenance and repair projects. This complex
problem is solved using heat and spraying the waste
with an alkaline mineralizing agent to convert PCB impacted
ACM into non-hazardous material. The waste reduction
is significant, a reduction of approximately 90%. Most
importantly, cradle-to-grave, liabilities associated
with PCB-ACM are terminated, all regulated wastes are
consumed. The thermochemical process is a cost effective
environmentally feasible alternative to landfill disposal,
endorsed by the United States Environmental Protection
Agency (EPA). The PCB-ACM Conversion System meets all
requirements of the National Emission Standard for Hazardous
Air Pollutants (NESHAP) for asbestos conversion processes
(40 CFR 61.155) and complies with (29 CFR 1910) OSHA
Health & Safety Standards. An integral part of the
permitting process includes an EPA-approved demonstration
test burn at PSNS. All operating parameters defined
by Federal, State and local permits for PCB-ACM processing
are monitored and reported via a programmable logic
control system developed specifically for this project.
An independent emissions testing company validates destruction
removal efficiency.
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Figure 1: PCB - ACM Destruction
Flow Diagram |
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Project
Description - Currently, the PCB-ACM Destruction
Mobile Unit is contained within two transportable trailer
units, approximately 45 feet long. The operations trailer
is a negative air chamber vented through HEPA filters.
While a secondary combustion chamber and afterburner
are housed in a separate trailer. This first generation
prototype will illustrate the capabilities of the technology
and acquire the additional data necessary to develop
and construct permanent, modular units for nationwide
implementation. Projections indicate that up to 900
pounds of PCB-ACM per hour can be processed through
this unit.
In
October to December, the demonstration test burn at
PSNS will begin. Approximately 18 tons of conventional
double-bagged ACM contaminated with 90% PCB transformer
oil will be processed. The process involves loading
steel bins containing 5 cubic yards of bagged PCB-ACM
into an interlock holding area, placing the bins onto
a transfer conveyer, discharging the waste into a rip
shear shredder, and reducing waste to a diameter of
less than one inch. The waste is then dropped into a
blender-mixer screw conveyer where an aqueous alkaline
mineralizing agent is sprayed over the PCB-ACM. The
waste is then transferred to a rotary hearth converter.
Within the converter, electric heating elements heat
the waste to temperatures of 2000 F to 2350 F. Typically
the ACM is exposed for approximately 20-60 minutes.
The end product, PCB-ACM free material is removed from
the hearth, cooled, de-watered, and transported to holding
bins. Bins are removed without breaking trailer air
seal integrity. Any gases generated from the process
are passed into a secondary combustion chamber. The
chamber promotes mixing of combustion air with the converter
exhaust gas products. The exhaust is more fully oxidized
by passing through an afterburner held in an operating
range of 2200 F to 2450 F. Exhaust gas exiting the afterburner
is then quenched with potable water converting the end
product temperature of 2300 F to 2500 F in less than
a second. Gas leaving the quencher enters the acid gas
absorber chamber followed by particulate removal in
a venturi scrubber.
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| Project Status |
For
more information please contact: |
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- Equipment mobilized to PSNS on 13 Sept. 99.
- System
assembly completed at PSNS, 8 Oct. 99.
- System
start-up and acceptance testing with ACM began
11 Oct. 99 ended 15 Oct. 99. Pre-test shake-down
of system with PCB began 18 Oct. 99 ended
22 Oct. 99.
- EPA
demonstration test burn began 25 Oct. 99 ended
5 Nov. 99.
- Operational period began 8 Nov. 99 ended 19 Nov. 99.
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Technical Support
NFESC, Port Hueneme, CA
(805) 982-1651; DSN: 551-1651 |
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Michael C.
Sargeant, CIH, CSP
NAVFAC Engineering Command EFA
Northwest, Poulsbo, WA
(360) 396-0256
e-mail: sargeantmc@efanw.navfac.navy.mil
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