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successful in reducing the spread of the contaminated sediments and
thereby significantly reduced the volume of capping sediments required.
The CLIS experience has provided insight on the procedures that his-
torically are recommended for a successful capping project. In the pre-
project planning, it is recommended to (a) completely characterize the
sediments to be disposed including sediment chemistry, bioassay, or bioac-
cumulation data and classify sediments using most recent information;
(b) estimate volumes of material to be disposed; (c) conduct site surveys
and choose a disposal area that is not vulnerable to natural or anthropo-
genic erosion; (d) schedule dredging and disposal operations ideally to
complete mound and cap well before a storm season to allow for consoli-
dation and surface stabilization; and (e) dispose the cap materials as soon
as possible after contaminated material. For the disposal operations, it is
recommended to (a) employ both accurate navigational techniques and a
taut-wired buoy to locate the designated disposal mound; (b) point dump
mound materials by directing the barge to unload as near to the buoy as
possible; (c) dispose approximately one-third of the cap sediments along
the radius of the contaminated mound; (d) maintain the preproject plan for
mound deposition followed by cap deposition; and (e) keep good records
of all disposal operations.
New York Bight
Experimental Mud Dump (EMD) mound
An evaluation of the 1980 LBC project at the Experimental Mud Dump
(EMD) site at the New York Bight apex (Figure 31) was reported by
O'Connor and O'Connor (1983), and excerpts from their report are used
to summarize this capping project. Contaminated dredged material from
the Hudson Estuary, Newark Bay, and contiguous waters were capped in-
itially with fine sediments from the Bronx River and Westchester Creek
and followed with sand from the Ambrose Channel. The resulting cap
was a 1-m-thick layer of sand overlaying contaminated sediment. Biologi-
cal, chemical, and physical investigations were completed to evaluate the
ability of the cap to remain intact and reduce the loss of organic and inor-
ganic toxicants from the contaminated material to the surrounding water.
Results showed the cap was successfully placed at the experimental
dump site, and it remained intact after 16 months. Erosion of the cap was
minor, and predictions of cap life were in excess of 20 years under normal
environmental conditions. However, it was predicted that major storm
events were capable of causing cap erosion and exposing the contaminated
material. The contaminated material volume decreased by 4 percent over
the 16-month study due partly to consolidation and partly to losses during
the disposal operation. Contaminant levels in the sand cap as measured
by chemical analysis were shown to be lower than those in contaminated
sediments. Bioaccumulation investigations indicated that contaminant up-
take was less than at uncapped dredged material sites. Therefore, it was
concluded that the New York Bight EMD capping project was successful
111
Chapter 10 Case Studies

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