Areas near dredging site may be of
conservation significance or important nursery
and feeding grounds for commercially
valuable species e.g. Queen Scallop
(Aequipecten opercularis) and edible crab
(Cancer pagurus).
Full restoration of fauna and sediments can take
2-3 yrs from cessation of dredging - short term
dredge areas. But in the UK most licensesfor 15
years
Changes in sediment composition,
associated communities change.
Organisms can be associated with certain
sediment types/particle size (Warwick &
Uncles 1980, Severn Estuary)
Different faunal composition
of silty sand to coarser sand
Increase in the proportion of fine
sands on increase in gravel
Long term effects not
known but areas around
UK still not recovered after
7 years
Recovery often only
assessed on parameters
of biomass, abundance
and diversity
But restructuring of biomass
dominants and age
structures could take longer
than other community
attributes, perhaps 15-20 yrs
(Newell et al, 2004)
Newell et al,
2004.Studied impacts of
dredged sites,
surrounding areas and
axis of transport of
discharged materials
Impacts on
bathymetry
and sediment
composition
Significant differences
in sediments in heavily
and lightly dredged sites
Benthic communities
significantly different
between dredged and
undredged sites
Major suppression of species
richness, population density,
biomass and average body
size
Decreased
'equilibrium' species
e.g. bivalves &
echinoderms
More 'opportunistic
species well adapted to
disturbed sediments
An impoverished
community dominated
by polychaetes
A 'footprint' of the
impacts of dredging and
screening in surrounding
areas
Majority of sediments settle
within 500m but evidence of
2km
'Footprint' can extend 2-3km along
axis of net sediment transport
Distance depends on net
sediment transport at the
seabed
Immediate loss of
fauna in extraction
area
Impacts on Marine Life
Direct -
removal of
sediment
Severe physical disturbance of
seabed. Physical effects seen for
up to 7 years after dredging ceased
(at a moderate energy site)
Weathered dredge tracks -
marks the seafloor
Indirect -
Sediment
resuspension
Indirect impacts may
be more important than
direct impacts. Can
result in reduced
species richness, low
densities & reduced
biomass
Plumes of suspended
material from action of
dredge head itself -
underwater
1) Outwash of material from spillways
from vessel generate much more. 2)
Rejection of unwanted sediment
These two termed "surface plumes"
Extent depends on particle size,
volume, speed of discharge and local
hydrodynamics
Sand particles usually within few 100m,
finer particles transported much greater
distances from point of discharge
Impact depends on
habitat type
Low levels of natural
disturbance - more significant.
Encrusting epifaunal taxa
affected by abrasive action of
suspended sediment
Levels of natural
disturbance high with high
levels of suspended
sediment due to waves
and tidal action - less
impact
Suggested Mitigation Measures
Reduction of overboard screening; material accumulates
at dredge site, means more dredging and more discharge
required in the exploited area over time
Adjustment of time for
exploitation; dredging only
when tidal stream will carry
sediments away
Establishment of refuge
areas to enhance
recolonisation;
non-dredged areas left
between areas of
dredged seabed
Measures need to be
cost effective to really be
implemented
21% of the sand and
gravel used in England
and Wales is extracted
from the marine
environment
Extracted using huge ships - in UK usually trailer
dredging, sometimes static suction hopper dredging
Useful materials are washed and screened, rest thrown
back overboard