New Bedford Harbor Superfund Site, Massachusetts
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Area D Bulkhead Project
By: Erik W. Matthews, United States Army Corps
of Engineers and
Charles M. Wilk, Portland Cement Association
Cement-based
solidification/stabilization (S/S) treatment technology is enabling
the U.S. Environmental Protection Agency to clean up the New Bedford
Harbor Superfund site while reusing the treated material to build
a dewatering facility.
The New Bedford, Mass., site, located in an 7,300-hectare (18,000-acre)
urban estuary, is highly contaminated with polychlorinated biphenyls
(PCBs) and heavy metals. PCBs are man-made, odorless, and colorless
chemicals used in the manufacture of electrical transformers and
capacitors. PCB wastes were discharged directly into the harbor
as well as indirectly through the city's sewer system. PCB levels
are highly variable throughout the site, with concentrations as
high as 40,000 parts per million (ppm) in wetland and mudflat sediments.
The New Bedford Harbor Superfund cleanup plan called for dredging
approximately 340,000 m3 (450,000 cu yd) of PCB-contaminated
sediment from 69 hectares (170 acres) of harbor and wetlands, dewatering
the sediment, and disposing it at a licensed offsite disposal facility
or in a confined disposal facility. The dewatering process removes
excess amounts of water from dredged sediment, greatly reducing
the volume of sediment needing disposal.
Construction plans for the dewatering facility and rail car loading
area included building an industrial grade waterfront bulkhead to
create approximately two acres of new land at the port. Locating
the dewatering facility along the waterfront provides docking facilities
for the harbor cleanup operation and access to a new rail spur for
transport of the dewatered sediment.
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| Steel arcs connecting circular
bulkhead cells. |
Creating the two acres of useable land for construction of the
dewatering facility was called the Area D Bulkhead project. It required
the installation of a series of seven circular steel sheet pile
bulkhead cells connected together with steel arcs. Dredging of soft
harbor sediment at the location of the cells was required prior
to installation of the cells. If left in place the soft sediments
would cause structural instabilities in the completed bulkhead.
This dredged sediment was contaminated with PCBs at concentrations
less than 50 ppm.
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Dredged sediment placed directly into pugmill
mixer.
Foreground: Treated sediment
compacted to form new land. |
Cement-based S/S treatment of the sediment dredged from the area of
the bulkhead cells was done ex-situ. After all of the sheet pile for
each bulkhead cell were driven, the soft harbor sediments were dredged
from within the completed cell and placed directly into the hopper
of a pugmill. A pugmill is a continuous mixer, processing material
placed into its hopper at one end of its mixing chamber and then discharging
treated material from the output end of the chamber. Computer-controlled
weigh belts from the hopper and reagent feed systems from cement silos
measured incoming sediment and amount of reagent mixed in, ensuring
a 13% addition rate of portland cement. The treated sediment was stockpiled
and left to cure until it reached a workable consistency (minimum
24 hours, but in some cases as much as three months). The cured material
was spread in lifts and compacted behind the completed bulkhead to
create new land.
S/S treatment changed the physical and chemical properties of the
sediment. Treated sediment had no free water and improved construction
characteristics. The unconfined compressive strength of the compacted
cured material showed strengths as high as 1.0 megapascal (150 pounds
per square inch) after 14 days, significantly higher than the required
0.3 MPa (40 psi). Significant cost savings were realized by using
the treated material as structural fill behind the bulkhead rather
than disposing of it offsite. About 9,000 m3 (10,000 cu yd) of sediment was treated. Reuse of the treated material created
new useable land for the construction of the dewatering facility
critical to the completion of the rest of the Superfund project.
Credits
Design and Oversight:
U.S Environmental Protection Agency, Region 1, Boston, Mass.
U.S. Army Corps of Engineers, New England District, Concord, Mass.
Contact: Erik Matthews, 978.318.8365, erik.w.matthews@usace.army.mil
General Remediation Contractor:
Foster Wheeler Environmental Corporation, Boston, Mass.
Sub-Contractor for Dewatering Facility:
R. Zoppo Corporation, Stoughton, Mass.
Solidification/Stabilization Contractor:
United Retek Corporation, Medway, Mass.
Contact: Russ Sattler, 508.478.5500, sattler@unitedretek.com
Photographs:
U.S. Environmental Protection Agency
United Retek Corporation
For an electronic copy of this case study, click
here.
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