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During hydraulic dredging, the bottom material is fluidized, lifted via
pipeline by a centrifugal pump, and transported as a slurry. Material
dredged by hopper dredges is also considered hydraulic dredging because
of the fluidization process required to lift the material to the hoppers. Hy-
draulically dredged material is typically transported via pipeline to the dis-
posal site and discharged with large amounts of entrained water. For
hopper dredges, the material is transported in the hopper similar to a barge
or scow as with the mechanical dredging, but excess water that is en-
trained during dredging remains with the material, thereby making the ma-
terial less dense than when in situ or mechanically dredged. For both
cases of hydraulic dredges (pipeline and hopper), the less dense material
is more susceptible to stripping and creates a flatter feature covering a
larger area on the bottom (Sanderson and McKnight 1986).
Alternatives are available to increase the mounding potential of mate-
rial dredged by hydraulic means. For pipeline dredges, diffusers can be
employed to reduce the material exit velocity from the pipe and reduce dis-
persion. Pump-down pipes can be added to transfer the material closer to
the bottom and reduce losses due to stripping as the material falls through
the water column. For hopper dredges, the spread of material on the bot-
tom can be reduced by having the dredge come to a stop during placement.
Dredged material characteristics also contribute to mounding potential.
Cohesive and noncohesive materials will tend to mound when dredged us-
ing mechanical means and point dumped (i.e., from a barge). Both cohe-
sive and noncohesive material will tend to flow if hydraulically dredged
and point dumped (i.e., discharged from a pipe). In cases where a pump-
down pipe is incorporated for hydraulically dredged material, noncohesive
material tends to mound, while cohesive material tends to flow.
Table 2 summarizes available information on the mounding or flowing
characteristics of cohesive versus noncohesive sediments for various
dredging and placement methods. This information can be used in evaluat-
ing various equipment and placement techniques for a given set of site
conditions.
Considerations for Contaminated Material
Dredging and Placement
Placement of contaminated material for a capping project should be ac-
complished so that the resulting deposit can be defined by monitoring and
effectively capped. Therefore, the equipment and techniques for dredging,
transport, and placement must be compatible with that of the capping mate-
rial. Since capping is a contaminant control measure for potential benthic
effects, the contaminated material should be placed such that the exposure
of the material prior to capping is minimized. In most cases, the water col-
umn dispersion and bottom spread occurring during placement should also
be reduced to the greatest possible extent. This minimizes the release of
contaminants during placement and provides for easier capping. If the
placement of the contaminated sediment has potentially unacceptable
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Chapter 5 Equipment and Placement Techniques
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