Beneficial use case studies
Port of Truro: beneficial
use of silts as capping material
Harwich Harbour Authority: intertidal
recharge using dredged sands and silts for coastal
defence and habitat creation
Medway Port: intertidal recharge
(trickle charge) using silts
Port of Truro,
beneficial use of silts as capping material
Good practice in using dredged materials for construction
purposes, can be illustrated by recent beneficial
use schemes undertaken by the Port of Truro in the
Fal and Helford SAC (Brigden 1996). The Port of
Truro has been investigating the feasibility of
mixing de-watered dredged material with china clay
waste sands and other waste substances for composting
(sewage sludge and green wastes) to cap derelict
land on the site of former arsenic works. Two derelict
experimental sites are already underway, the first
of which used basic dredged spoil and was left to
colonise naturally, the other where the dredged
material mix was used and sown with grass seeds.
Vegetation has become established at both sites
where no plants had grown before the placement of
dredged material, with the first site taking just
three years to become established through wind borne
seeding of native grasses, and the second sown site
developing considerably quicker.
Adoption and adaptation of this beneficial use
of dredged silts for ‘composting’ derelict sites
may provide a number of benefits to other ports
and harbours with a supply of silt, nearby storage
places for dewatering dredgings, and access to suitable
waste materials for mixing. However, the project
has not been without its problems, for example the
experimental site needed licensing by the Environment
Agency under the Waste Management Licensing Regulations
1994 because the material was classed as a waste,
despite the fact that the material was providing
a beneficial use to create land of greater quality
(less contaminated) than much of the existing derelict
land.
Unfortunately, the licensing requirements
introduce a cost which may act as a disincentive
to undertaking such beneficial use schemes. If such
beneficial use schemes are to be encouraged in the
future there is a need for all of the relevant regulatory
bodies involved to work together and reach consensus
over ways that current regulatory disincentives
may be removed, wherever possible.
Harwich Harbour Authority, intertidal
recharge using dredged sands and silts for coastal
defence and habitat creation
Harwich Harbour has been responsible for more beneficial
use schemes than any other port in the UK. Dredged
sands and gravels from channel deepening works have
been used in a number of varied schemes, including
intertidal recharge for coastal defence in the Stour,
Orwell and Blackwater Estuaries and Horsey Island,
reclamation works for port development at Felixstowe,
construction of low water berms for foreshore stabilisation,
and the creation of shellfish and crustacea habitat.
Harwich Harbour committed to a programme of beneficial
use research and monitoring under the guidance of
an agreement with English Nature, RSPB and the Wildlife
Trusts following the consent for the 1994 channel
deepening consent.
Numerous experimental intertidal recharge schemes
were undertaken in 1993 and 1994 with the objective
of using the coarse dredged sediments to protect
eroding saltmarshes and the infrastructure behind
them. At Parkeston Marshes Copperas Bay on the north
bank of the Stour Estuary, with funding from the
Environment Agency, 250,000m3 of dredged
sands from Harwich Harbour were sprayed onto the
intertidal mudflats using rainbow discharge, raising
them approximately 2m in height (Mark Dixon Environment
Agency, personal communication 1996).
Post-scheme monitoring of the shore profile, sediments
and animal communities has indicated that erosion
of the foreshore has been arrested and the wetland
is naturally being restored. Within two years a
diverse benthic community is reported to have colonised
the dredged material, however, due to the coarser
nature of the dredged sands these communities are
different to those previously inhabiting the intertidal
flats with a reduction in typical mud dwelling animals.
This change in benthic community is often accompanied
in reduced food supplies for feeding birds and foraging
fish, but conversely the new material may provide
alternative habitats for breeding and roosting birds.
Costs of undertaking such beneficial use schemes
are greater than the alternative of disposal to
sea, because of the higher costs involved with using
smaller vessels and rainbow discharge techniques
(Murray 1994a).
In addition to schemes using sand and gravels,
a number of schemes have been undertaken to investigate
the feasibility of using fine maintenance dredged
material for intertidal recharge, whilst providing
both the benefits of coast protection and habitat
restoration. The first experimental scheme undertaken
on Horsey Island in Hamford Water was unsuccessful
in that material sprayed on to a small area of saltmarsh
was washed off the recharge site by Spring tides
(Carpenter and Brampton 1996). In Trimley Marshes
on the Orwell Estuary, fine muds and sands were
sprayed on to the intertidal mudflats in between
gravel groynes placed perpendicular to the eroding
shoreline with fencing and straw bales used to retain
the material on the site.
Harwich Harbour have recently carried out two experimental
intertidal recharge trials, each using over 20,000m3
of maintenance dredged muds (HR Wallingford
& Posford Duvivier Environment 1998; Woodrow
1998). In the North Shotley scheme in the lower
Orwell Estuary, 22,000m3 of maintenance
material was pumped through a pipeline into a gravel
bunded area to protect sea wall and the internationally
important freshwater wetlands behind. In the Horsey
North and Horsey Beach scheme, 20,000m3
of silt has been placed on a degraded marsh at Island
Point to protect and regenerate saltmarsh.
Further initiatives for the future use of maintenance
materials are being investigated by Harwich Haven
Authority plan, as part of their proposals to provide
a beneficial use for dredged material arising from
the deepening of approach channels for the Ports
of Felixstowe and Harwich. These schemes include
intertidal recharge, dispersion of muds within the
estuary system (trickle charge) and the placement
of material behind seawalls to raise to intertidal
levels (HR Wallingford & Posford Duvivier Environment,
1998).
Medway Port, intertidal
recharge (trickle charge) using silts
An intertidal recharge experiment using maintenance
dredgings from the port was undertaken in 1996 in
a tributary of the Medway Estuary which is an SPA
(Environmental Tracing Systems Ltd 1996; Pethick
and Burd 1996). The objective of the scheme was
to dispose of fine dredged material within an area
of outstanding nature conservation interest and
to retain the dredgings within the estuary system
in a manner that is not harmful to the environment.
The experiment was jointly funded by Medway Ports,
MAFF’s Flood and Coastal Defence Division, the Environment
Agency and English Nature.
The 4000m3 of fine dredged materials
taken from Cadnam Basin were placed on the lower
intertidal by split bottom barges and were left
for natural hydraulic processes to gradually move
it up the foreshore (trickle charge/feed). This
approach enables the sediments to be redistributed
within the intertidal system and promote the natural
evolution of intertidal habitats. Early results
from this experimental recharge scheme indicates
that bottom dumping and trickle feeding is a success
for relatively small infrequent volumes of fine
dredged material. Around 50% of the material is
estimated to have been retained at the recharge
site.
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