NB - Many of the attributes will be able to be
monitored at the same time or during the same survey.
The frequency of sampling for many attributes may
need to be greater during the first reporting cycle
in order to characterise the site and establish
the baseline.
Feature
|
Sub-feature
|
Attribute
|
Measure
|
Target
|
Comments
|
Lagoon |
|
Extent
|
Area (ha) of lagoon
basin, measured once per reporting cycle. |
No decrease in extent
from an established baseline, subject to natural
change. |
Extent is an attribute
on which reporting is required by the Habitats
Directive. The Fleet is a large lagoon, thus
size (including the length:width ratio) will
critically influence the hydrography of the
site. Natural gradual reduction in area of the
lagoon is inevitable, however, as a result of
the natural progression of Chesil Bank. |
|
|
Salinity
|
Seasonal averages
encompassing the east-west salinity gradient
measured periodically throughout the reporting
cycle (frequency to be determined). |
Average seasonal
salinity, and seasonal maxima and minima, should
not deviate significantly from an established
baseline, (to be derived from the Environment
Agency monitoring programme), subject to natural
change. |
Salinity is a key
structuring factor within lagoons and in the
Fleet, the gradient from west to east is particularly
notable. Note should be made of natural fluctuations
that occur according to year on year variations
in rainfall. |
|
|
Water clarity
|
Average light attenuation
measured periodically throughout the reporting
cycle (frequency to be determined). |
Average light attenuation
should not deviate significantly from an established
baseline, subject to natural change. |
Water clarity is
important for maintaining the extent and density
of algal and plant dominated communities. Clarity
decreases through increases in amounts of suspended
organic/inorganic matter. |
|
|
Nutrient status -green algal mats
|
Extent across whole
or parts of site, measured during summer months,
annually. |
No increase in extent
of green algal mats from an established baseline,
subject to natural change. |
Nutrient status is
important for the structure and functioning
of the lagoon and its communities. The Fleet
is probably naturally hypertrophic. Opportunistic
green algae compete with other vegetation and
affect the associated species. A late spring/early
summer increase in filamentous green algae may
be a related natural phenomenon or may indicate
eutrophication. |
|
|
Characteristic species - Rissoa membranacea
membranacea
|
Population size -
average abundance (number of individuals/m2),
measured during the summer twice per reporting
cycle. |
Average numbers should
not deviate significantly from an established
baseline, subject to natural change. |
Algal grazers (largely
gastropods) affect the structure of the lagoon
communities by consuming benthic and epiphytic
growth. R.membranacea is the only species
amenable to quantitative survey and can be used
as a surrogate for grazers as a whole. |
|
|
Characteristic species - Lamprothamnium
papulosum (foxtail stonewort)
|
Density (number of
plants/m2) and westward extent, measured
during summer, twice per reporting cycle. |
Average density should
not deviate significantly from an established
baseline (to be derived from Holme (in press),
Martin (pers. comm.) and 1999 seagrass survey)
subject to natural change.
No eastward movement in westward limit.
|
The foxtail stonewort
(L. papulosum) is a species characteristically
found in lagoons which requires low nutrient
conditions, particularly of phosphates, and
therefore provides a possible indicator of nutrient
status. It is a nationally scarce species. |
|
|
Fish species assemblage
|
Number of composite
species
measured during mid-summer from the inlet
channel, once per reporting cycle
|
Average number of
composite species should not deviate significantly
from an established baseline, subject to natural
change. |
Diverse fish community
characteristic of large, inlet type lagoons,
the sheltered conditions providing a nursery
for a number of species. The fish community
as a whole provides an integrated measure of
the quality and functioning of the Fleet as
well as indicating populations of the main predators. |
|
Seagrass bed communities
|
Extent |
Total area (ha) of
seagrass measured during peak growth period
(Aug), twice per reporting cycle. |
No decrease in extent
from an established baseline (to be derived
1991 and 1999 surveys), subject to natural change.
|
Seagrass (including
tasselweeds) contribute to the overall community
structure within the Fleet and both are characteristic,
to varying degrees, of lagoons. The area of
seagrass provides a long-term integrated measure
of environmental conditions. |
|
|
Characteristic species - density of Zostera
marina and Ruppia spp.
|
Density (number of
shoots/ m2) measured during peak
growth (Aug), twice per reporting cycle. |
Average shoot density
should not deviate significantly from an established
baseline, subject to natural change. |
Reduction in the
density of plants is an early indicator of seagrass
under stress and reflects changes in biomass.
Zostera marina, Ruppia cirrhosa
and R. maritima co-occur in many parts
of the Fleet. Monitoring both Zostera and
Ruppia may be justified as they have
different salinity range preferences and therefore
would provide an indication of conditions in
different areas along the Fleet. |
|
Tide-swept communities
|
Tide-swept communities
- species composition |
Presence and abundance
of composite species, measured during summer,
once per reporting cycle. |
Presence and abundance
of composite species should not deviate significantly
from an established baseline, subject to natural
change. |
Tide-swept communities
are characteristic of inlet lagoons and are
therefore integral to the structure of such
lagoons. The bedrock biotope, which includes
a number of rare or southern species such as
the sponge Suberites massa, is the most
notable part of the community and potentially
provides a long-term integrated indication of
tidal flow of the Fleet and therefore of a key
functional process. |
|
Subtidal coarse sediment (gravel, cobbles,
pebbles) communities
|
Extent |
Area (ha) of submerged
coarse sediment (gravel, cobbles & pebble)
communities, measured once per reporting cycle. |
No decrease in extent
from an established baseline, subject to natural
change. |
Extent of sediments
in this part of the Fleet indicates proportion
of a habitat that adds to the structural diversity
of the site and is likely to reflect hydrological
conditions. |
|
|
Characteristic species - density of Anemonia
viridis
|
Density (number of
animals/m2), measured during summer
once per reporting cycle. |
Average density should
not deviate significantly from an established
baseline, subject to natural change. |
The stability of
the sediments enabling a diverse community to
develop is notable. Monitoring of the community
indicates condition of a distinct section of
the Fleet and of water movement etc between
the mouth and the Narrows. Unusually, the anemone
Anemonia viridis occurs in high numbers
and can therefore be readily measured. The species
should be used as a surrogate for the community
as a whole and indicator of a change in conditions. |
|
Intertidal sediment communities
|
Extent |
Area (ha) of intertidal
sediment between the Narrows and Smallmouth,
measured once per reporting cycle. |
No decrease in extent
from an established baseline, subject to natural
change. |
Extent of sediments
in this part of the Fleet indicates proportion
of a habitat that adds to the structural diversity
of the site and is likely to reflect hydrological
conditions in the entrance to the Fleet. |
|
Intertidal sediment communities
|
Species composition |
Presence and abundance
of composite species, measured during summer
once per reporting cycle. |
Presence and abundance
of composite species should not deviate significantly
from an established baseline, subject to natural
change. |
The infaunal community,
which includes a number of rare and/or lagoonal
specialist species, eg A.cirrhosa, is
indicative of sheltered, fully saline conditions
and is likely to change in relation to a number
of factors including hydrological conditions
in the entrance to the Fleet. |
|
Shingle spring line communities
|
Extent and distribution |
Frequency and distribution
of shingle springline communities, measured
during summer, once per reporting cycle. |
No decrease in extent
from an established baseline, subject to natural
change. |
The spring line community
is unusual and reflects both the stability of,
and percolation through, the shingle bank. The
extent of the community (as measured by distribution)
will be indicative of saline seepages along
much of the Chesil Bank |
|
|
Species composition
|
Presence and abundance
of composite species, measured during summer
once per reporting cycle. |
Presence and abundance
of composite species should not deviate significantly
from an established baseline, subject to natural
change. |
The spring line community,
which includes notable species such as Caecum
armoricum (De Folins lagoon snail), is unusual
and reflects both the stability of, and percolation
through, the shingle bank. As such the community
adds to the diversity (structure) of the lagoon
and will reflect processes in relation to both
the shingle and percolation of sea water into
the lagoon. |
NB .Extreme events (such as storms reducing or
increasing salinities, exceptionally cold winters
or warm summers) also need to be recorded as they
may be critical in influencing ecological issues
in the Fleet and may well be missed by routine monitoring
Glossary of terms used in the favourable condition
table
Feature The habitat or species for which the site
has been selected.
Sub-feature An ecologically important sub-division
of the feature.
Comments The rationale for selection of the attribute.