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ERDC TN-DOER-T2
December 2000
Solidification/Stabilization.
The solidification/stabilization technology presented was
developed and used by the OENJ Cherokee Corporation, Bayonne, NJ, for cover at an old city
landfill in Elizabeth, NJ, using dredged sediment. This technology is a nonthermal, mixing process
using chemical additives to transform dredged sediments into a structural-cover product. During the
process, contaminants are not destroyed, but their mobility is reduced due to chemical stabilization
and incorporation in the physical matrix of the product. Reduction in mobility is dependent on the
contaminant and the type and amount of chemical additives used.
In operation, the dredged sediment is screened to remove large debris and then transferred to a pug
mill. Solidification additives (portland cement was used for this particular project) are added and
mixed into the sediment. The resulting mixture is transported to the work site where it is allowed to
dry and gain strength as a result of hydration of the additives. The material is then spread and
compacted to provide a smooth, hard surface.
SUMMARY: The focus of the Specialty Conference was on technologies that are generally
applicable to contaminated sediments and that have the potential to process large amounts of
sediments, that is, sediment quantities in excess of 764,555 cu m (1,000,000 cu yd). Essentially all
dredged material decontamination and treatment technologies that are capable of processing in
excess of 764,555 cu m (1,000,000 cu yd) of dredged material fall into one of two basic categories,
destruction technologies and technologies that separate/extract or stabilize contaminants.
Most destruction technologies are essentially thermal, since nonthermal-based destruction
technologies are generally not available for some contaminants. Sediment decontamination
technologies that are capable of processing large volumes of dredged material are designed to avoid
disposal costs of product materials. They are designed to produce a salable product material.
EVALUATIONS: The important information and features of the eight technologies presented
during the workshop are summarized in Table 1. Some of the information is incomplete because it
was not presented by the TDFs. In comparing technologies, it should be noted that the technologies
vary in their maturity and scale of demonstration. Capital and operation and maintenance costs are
highly dependent on specific site conditions, dredged sediment characteristics, and the product
produced.
Among the separation and stabilization technologies that have been proposed for contaminated
sediments are sediment washing and processes that seek to produce fill material in which the
contaminants are effectively contained. Soil washing technologies serve to reduce contaminant
levels by partial removal of fines and organic material containing contaminants. The net result is
contaminant reductions, by factors of 2-10, of the more soluble constitutents in the sediments.
Reductions in contaminant levels of less soluble components, such as polychlorinated biphenyls
(PCBs) or high-molecular-weight polycylic aromatic hydrocarbons (PAHs), are likely to be less
than a factor of two. In many situations, this may be insufficient to allow significantly expanded uses
of the treated material over the untreated dredged material. The goal of most soil washing
technologies is production of a soil for beneficial use.
Stabilization technologies introduce additives to the dredged material to produce flowable or solid
fill material. The contaminant levels are normally unchanged except for dilution due to the additives
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