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ERDC TN-DOER-T7
October 2004
Mechanical Dewatering of Navigation Sediments:
Equipment, Bench-Scale Testing, and Fact Sheets
mechanical dewatering at dredged material placement sites. This document introduces the basic
pieces of equipment that make up a dewatering circuit or train, some advantages and
disadvantages of different equipment options, the state of the practice in bench-scale testing,
discussions of performance specifications and cost, and several fact sheets on various process
technologies and their applications.
BACKGROUND: The fundamental objective of the Innovative Dredging Technology Focus
Area of the Dredging Operations and Environmental Research (DOER) Program is to identify
and catalog innovative dredging operations, processes, or equipment and techniques developed
by domestic and international dredging entities. A number of technologies developed within the
U.S. Army Corps of Engineers (USACE) are currently undergoing evaluation for potential
demonstration under the DOER Program. Among these is the mechanical dewatering of dredged
material at confined disposal facilities (CDFs).
INTRODUCTION: The solids content of a typical dredge discharge slurry ranges from roughly
100 to 200 g/l, as compared to the in situ solids content, which may range from 250 to 1800 g/l,
depending upon the grain size distribution of the in situ sediment. Conventional upland
placement of dredged material involves discharge of the slurry into a CDF, where clarification
and settling take place. Clarified water is normally returned to the originating water body. Large
areas are required for upland placement of hydraulically dredged sediments, and CDFs must be
in relatively close proximity to the shore in order to economically manage return flows. Over
time, the material placed in the CDF continues to dewater and consolidate, making room for
additional "lifts" from subsequent dredging cycles. Surface trenching and weir management are
typically the only active dewatering efforts that take place.
Mechanical dewatering uses special equipment to reduce the water content of the dredge slurry at
the time of placement. There are a number of possible motivations for considering mechanical
dewatering, including:
Remaining storage capacity in the CDF is insufficient for clarification and water
management.
Sediments are very contaminated and must be transported to a permitted landfill for disposal.
Conditioning of the material is needed to facilitate handling and transport and to reduce
transport costs.
Water content must be reduced to meet disposal or beneficial use specifications.
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