Selection of disposal options
Under guidance from MAFF, CEFAS, SOAEFD and DOE(NI),
ports and harbours throughout the UK select the
Best Practical Environmental Option for a sea disposal
site which is considered carefully so as to avoid
adverse effects on marine organisms from occurring.
If the sediment is going to be disposed of on land,
an equal amount of consideration should be given
to the sediment type and the location and status
of the site under guidance of the environment agencies.
The benefits of returning dredged sediments back
to the estuary system are becoming increasingly
recognised. Disposal of fine sediments at suitable
locations within the estuary allows the dynamics
of the system to be maintained and the morphological
and ecological development of the estuary to be
conserved. Examples of the application of this disposal
option are given below. Disposal of dredged sediments
within the estuary or coastal cell system has the
additional benefit of reducing the costs incurred
transporting materials to deep-sea disposal sites.
Examples of the disposal of dredged
sediments within the estuary system
In the Humber the dredged channel
is maintained in such a way, feeding the whole estuary
as dredged material is disposed and redistributed
within the estuary. As much as 8 million tonnes
of fine sediments are disposed in this way each
year with little physical or biological effect as
the sediments are redistributed within the estuary
(Murray 1994b).
A similar approach is being proposed
in the Stour/Orwell Estuaries by Harwich Harbour
Authority to address the problems of intertidal
erosion caused by capital dredge operations, which
are being sustained by current disposal practices
(HR Wallingford & Posford Duvivier Environment
1998).
Fine dredged sediments have been
disposed and retained within the Medway Estuary
system in a manner that is not harmful to the environment
(Pethick & Burd 1996).
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