The sensitivity of
Intertidal species
Reefs are widespread in Southern Europe and
occur widely around the UK coast. They are very variable in
form and in the communities that they support. Reefs are rocky
marine habitats or biological concretions that rise from the
sea bed. They are generally subtidal but may extend as an unbroken
transition to the intertidal zone, where they are exposed to
the air at low tide. Two main types of reef can be recognised:
those where the structure is created by the animals themselves
(biogenic reefs) and those where animal and plant communities
grow on raised or protruding rock.
Reef communities, or hold-fast
communities, need to harness wave energy to survive. The plant
and animal communities rely on turbulent conditions for nutrients,
oxygen and carbon supplies. They are therefore well adapted
to survive the extreme physical stresses imposed by waves and
currents.
For safety reasons, water-based recreation,
other than snorkelling, diving and the use of very shallow hulled
craft, is unlikely to take place in the vicinity of reefs. However,
land based recreation at low tide can have implications for
intertidal reef habitats and communities through:
- collection of species (rock pooling)
- trampling
- littering
Intertidal Species
Rocky shores are dominated by Fucales or rock-weeds,
represented by species in temperate climates such as, Ascophyllum,
Cystoseira and Fucus. However, all of these plant species experience
environmental stresses due to their location, which exposes
them to immersion, desiccation and changes in water temperature
and salinity.
It has been suggested that seaweeds and rock-weeds
may suffer from nutrient deficiency but Mann (1972) concluded
that some communities were able to overcome such natural limitations
by storing nutrients during periods of high availability and
using them for growth in the Spring and Autumn. These changes
to the typical seasonal growth timing may have implications
for recreational management as it suggests that the sensitivity
of the plant may be greatest in its spring and autumn growth
periods.
Intertidal and littoral ecosystems are exposed
to human impact more frequently than any other marine system.
However, it is difficult to determine generic sensitivities
because of the complex relief of rocky shores. Some locational
classifications do exist, which relate to where species are
found on the shore (upper, mid and lower) and the levels of
shading available. Alternatively species location may be determined
by available space, rather than any other environmental control.
These issues are considered in more detail by Hill et al (1998)
This problem with identification of sensitive
areas is heightened by the fact that the community structure
of some rocky shores is highly variable in time and space. Due
to this variability, and the natural stress applied to the system
as outlined above, impacts on one species can have serious community-wide
consequences. With such a variety of natural fluctuations, human
impacts may be difficult to determine without detailed and often
long term investigations at site level.
The tables below summarise the potential threats
to reefs from land and waterborne processes.
Water based processes
|
Wave Erosion
|
Turbidity
|
Sediment mixing
|
Immersion
|
Waterborne Sound
|
Waterborne pollution
|
Waterborne litter
|
Reefs
|
Potential
|
High
|
None
|
None
|
None
|
Potential
|
Potential
|
Land based processes
|
Natural/Human-induced Erosion
|
Compaction
|
Litter
|
Sound
|
Reefs
|
Potential
|
Potential
|
Potential
|
None
|
Next Section
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