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treatment train is assembled and pilot-scale testing is conducted in the field.
Costs to contract intermediate and pilot testing are typically high given that
mobilization/demobilization and equipment costs are relatively insensitive to the
volume being processed, and most vendors cannot accept contaminated
sediments for pilot testing in-house. Availability of a mobile hydrocyclone unit
could result in significant cost savings for feasibility evaluations and small-scale
projects, and ultimately facilitate full-scale implementation of this technology.
The long-term goal is assemble a mobile physical separation plant suitable for
separation of sediments and dredged material to serve the Great Lakes CDFs.
Questions remaining to be addressed before full-scale implementation is
feasible include the following:
a. The degree of bulking of residual materials, with and without flocculants,
and the short- and long-term effects on CDF capacity recovery.
b. Alternatives for dewatering residual materials to minimize bulking
effects, and their cost, effectiveness, and effect on suitability of residual
materials for beneficial uses.
c. The relative benefit and feasibility of making finer separations (silt/clay)
to recover additional material from CDFs.
d. Evaluation procedures for determining the potential contaminant levels
in fine residuals and the effect on the regulatory classification of these
materials.
e. Development of cost/benefit algorithms incorporating all of these
considerations for economic feasibility evaluations.
Project Objectives
Identification and purchase of a portable hydrocyclone unit suitable for
conducting separation feasibility evaluations and a small-scale field
demonstration was the principal objective of this project. While the predominant
focus is coarse material recovery for beneficial use as beach nourishment and
construction fill (typically requiring the material to contain less than 10-
15 percent fines), some beneficial uses will accommodate higher percentages of
fine material. The silt/clay separation is expected to be an important long-range
objective in maximizing material recovery from CDFs for material in which the
silt fraction is substantially less contaminated than the clay fraction. Separation
capability at the sand/silt interface (approximately 75 microns) with the
additional capability of a silt/clay separation (at 2-3 microns) were therefore the
principal operating specifications. Additional criteria were (a) level of expertise
required for operation, (b) auxiliary equipment required to support operation, and
(c) material preparation required. The equipment may also be used to address
other information gaps, as previously described.
2
Chapter 1 Introduction
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