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Li, S. 1997. Spatial variability in diatoms and
charophyte oospores in a coastal lagoon, The Fleet,
Dorset, England.
Diatom oospore population characteristics can be
used to indicate past variations in salinity from
cores taken in deep waters only. In shallow waters,
water currents affect the distribution of diatom
oospores, such that interpretation of past variations
in salinity is affected.
Lamprothamnium papulosum mainly distributed
in shallow water (10-40cm depth) around Langton
Ferry and Herbury (eastern part of the West Fleet)
on fine sand with relatively little water disturbance.
Some adult plants also found between Top Ferry and
Rodden Hive Point) during present study (full spatial
study of distribution in Fleet not carried out -
investigation based on distribution data from Holmes
1985 and >95).
Investigation of Lamprothamnium papulosum
oospore distribution with depth and with distance
from parent population centre & salinity (2.0
to 5.5 gl-1).
No clear change in diatom population assemblages
with longitudinal (E-W) salinity gradient observed.
But gradient with depth observed - more fresh and
fresh-brackish species found in shallow waters,
more brackish and brackish-marine species found
in deeper waters. Deeper channels in Fleet very
organic-rich compared to shallower bays - accumulate
fossil diatoms from both shallow and deeper waters,
therefore diatoms will represent >average=
salinities for whole Fleet over time, not local
variations. Most diatom species found in Fleet were
euryhaline - therefore not much use for indicating
salinity fluctuations.
Lamprothamnium papulosum is confined to
four sites on the south coast of England in Dorset,
Hampshire and the Isle of Wight, and one site in
Scotland, on North Uist [Loch Maddy]. A substantial
population occurs in the Fleet, but populations
are small at the other sites (Church, 1992). It
grows in natural and artificial brackish lagoons
with salinities in the range 10-30 gl-1,
usually on sand, gravel or pebbles in <2m water
depth, and is intolerant of strong water currents
or wave action. It usually occurs with tasselled
pond weeds (Ruppia spp.), but does not compete
well with dense vascular plant growth. Often found
where there is some disturbance from birds or animals,
or in shallow water where fluctuations of water
level result in more open vegetation (Round 1981).
Salinity gradient along Fleet under different precipitation
conditions are described. Fleet is divided into
two regions - East and West, with transition area
between. East Fleet (approx.6.5km from Abbotsbury
to Smallmouth) salinities are close to marine values,
about 30-35 gl-1 . The transition zone
is from approx. 4.5 - 6.5 km from Abbotsbury, where
salinity drops dramatically from 30-15 gl-1
within 2km distance in average runoff conditions.
West Fleet, from Abbotsbury to 4.5 km east, the
salinity is quite stable from 13-15 gl-1
under average runoff, and 5-12 gl-1 under
high runoff conditions (Robinson, 1992). Salinities
recorded for this project varied along a transect
in main part of lagoon from 2.0 gl-1
at Berry Knap, to 5.5 gl-1 at the west
end of Herbury headland (east end of Langton Ferry
bay).
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