The sensitivity of mud and sandflats
Intertidal mudflats and sandflats are submerged
at high tide and exposed at low tide. They form a major component
of estuaries and embayments in the UK but also occur along the
open coast. The physical structure of intertidal flats can range
from the mobile, coarse-sand beaches of wave-exposed coasts
to the stable, fine-sediment mudflats of estuaries and embayments.
This habitat type can be divided into three broad categories:
clean sands, muddy sands and muds, although in practice there
is a continuous gradient between them. Within this range, the
plant and animal communities present vary according to the type
of sediment, its stability and the salinity of the water.
Mudflat areas are exposed at low tide and may
extend for many square kilometres. Those mudflats which are
adjacent to saltmarsh areas provide important feeding grounds
for many shore and sea birds. They also offer important breeding
sites for over-wintering birds. The richness of the fauna contained
within the feature is a major determinant in the diversity and
number of birds which feed from mud and sand flats. However,
just as the macrofauna community is important for the species
of birds which populate mud and sand flats, so birds contribute
with other factors to the control of these communities through
predation.
One of the main factors influencing the environment
of intertidal areas is the degree of wave action. This is particularly
the case for mud and sand flat areas as the intensity of the
wave action will determine the sorting of the surface sands,
gravels and silts. This is highlighted by Elliot (1998) who
state that "increased littoral and tidal currents carry
away finer material and leave coarser, well sorted sands and
gravels whilst in more sheltered areas settlement of finer material
is possible, as found on intertidal mudflats."
As with many other coastal features, mud and
sandflats can be changed considerably by natural events. Periodic
increases in wave action can severely alter the appearance of
the intertidal region and storms can remove considerable amounts
of material from sandbanks. In addition, increased rainfall
can cause natural impacts on the feature including scouring
of intertidal areas.
In addition to the physical characteristics
of intertidal mud and sand flats, the biological communities
within these features are also important to feature stability.
Micro and macro biological species such as bacteria and polychaete
worms contribute to the long term stability of the feature.
Disturbance to the layering of the mud or sand flat can have
consequences for these species. In particular, although some
water breathing species have adapted to air exposure, such as
Scolelpis squamata, many need to burrow into the sediment to
avoid drying out and dying from air exposure.
There are a number of human pressures influencing
mud and sand flats including:
- land claim for development
- squeeze through sea level rise
- provision of recreation facilities
- recreational activities
- dredging
- pollution/nutrient stimulation
Other factors that can affect mud and sand
flat species include:
- salinity
- temperature
- dissolved oxygen content
It is unlikely that recreation could affect
any of these factors to such a degree that it would have a significant
effect on the feature or the species it supports.
The tables below summarise the potential threats
to mud and sand flats from land and waterborne processes.
Water based processes
|
Wave Erosion
|
Turbidity
|
Sediment mixing
|
Immersion
|
Waterborne Sound
|
Waterborne pollution
|
Waterborne litter
|
Mud and Sand flats
|
Potential
|
None
|
High
|
Potential
|
None
|
Potential
|
Potential
|
Land based processes
|
Natural/ human-induced erosion
|
Compaction
|
Litter
|
Sound
|
Mud and Sand Flats
|
Potential
|
Potential
|
Potential
|
None
|
Next Section
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