Jodie
Peers
Osua7b
Physical factors and nutrient availability the influence the
distribution of Dinoflagellates.
Introduction
The dinoflagellates form an exceedingly important part of the ocean, the source of primitive food supply in the sea, both in the number of the individuals and in the total mass of living substances produced.
As synthetic producers of carbohydrates, proteins and fats they hold high rank among the protists of the sea and of fresh water. In abundance they are second only to the diatoms in the marine plankton, while locally and in midsummer they may far outnumber even those abundant organisms. At their periodic maxima they may surpass the diatoms in the total mass of their substance produced and in the rapidity of their development.
The dinoflagellates are one of the most important members of the phytoplankton in our marine and freshwater ecosystems and represent a major constituent of food webs.
Members of the division Pyrrophyta are generally characterised by having chlorophylls a and c, ß-carotene, and one or more of the xanthophylls. The primary storage products are starch and oil. Total lipids make up from 5-28% of the dry weight of dinoflagellates. Hydrocarbons account for 0.5-20% of the dinoflagellate lipid fraction.
Ecology and distribution.
Perhaps the largest number of species is planktonic, swimming freely,
or floating, in the sea or in large bodies of water.
They are found in all latitudes from the
Many dinoflagellates occur in marginal
habitats. Some are confined to near-shore or neritic
waters which are probably more nutritious and of lower salinity than the open
oceans waters.
Plankton was collected from 5 sites
around
For nutrient analyses to be
carried out a CTD was deployed daily at each of the sites. The nutrients that
were collected were filtered through GF/F filters and then were frozen until
they could be analysed at a later date.
Results.
Figure 1
Abundance of dinoflagellates throughout the month of October.
Colours correspond to the different species and can be referred to in the key.

The graph shows that the species that is found in the greatest biomass
over the length of the research trip is C.
fusus, as can be seen, this species is present in
relatively high abundances.
Throughout the month of October, the species that has the highest
abundance is C. longpipes, this species
reaches an abundance high of 18.5 individuals per m-3.
Abundance of dinoflagellates at the 5 sites sampled during the field
course.

This graph also indicates
that C. fusus is the most distributed species over
the 5 sites. C. longpipes has the highest abundance
than all the other species found at the sites.
The dinoflagellates was the
lowest of all phytoplankton at less than 20 cells per dm-3 found at
the sites.
Table 1.
Physical properties of the
water around the 5 sites sampled.
|
Site |
Mean temperature (oC) |
Meandepth (m) |
Mean salinity |
|
Pier |
13.9 |
9.6 |
33.3 |
|
Puffin |
14.7 |
22.0 |
33.3 |
|
Llandonna |
11.8 |
14.5 |
33.4 |
|
Llandudno |
15.3 |
13.7 |
33 |
|
Offshore |
34.4 |
15.1 |
33.8 |
Temperature values were similar for all of the sites varying between 13.7-15.1˚C, the lowest temperature was seen at Llandudno and the highest at the offshore site. The salinity showed little variation at all sites. The depth was the lowest at Menai Bridge Pier and the greatest Offshore.
Nutrient analyses that were carried out at each of the five sites found that:
The phosphate concentration was similar
for all of the sites values range between 0.59-0.76 mg/l. The silicate
concentration varies the most with values ranging from 3.25-5.28 mg/l, the
greatest value being at Llandudno and the lowest being at
Table 2.
Spearmans rank correllation coefficient of chlorophyll and dinoflagellates.
Analysis was performed ate the 5% significance level.
|
|
P value |
R value |
|
C. longpipes |
0.279 |
-0.149 |
|
C. fusus |
0.132 |
0.204 |
|
C. furca |
0.037 |
0.280 |
|
C. macroceros |
0.716 |
-0.050 |
|
C. triops |
0.336 |
0.131 |
|
C. arcticum |
0.336 |
0.131 |
The data was tested for normality, but non was shown even after it was transformed, hence a Spearmans rank corellation was carried out instead.
All the values except for C. furca, show that data to be > 0.05, which means that there is no significant relationship between chlorphyll concentration and dinoflagellate numbers. C. furca value <0.05 which indicates that for this species there is a significant linear relationship between chlorophyll and the species abundance.
It would be expected that
where there is more chlorophyll, there should be a higher abundance of
phytoplankton present, which would indicate that there was a higher level of
nutrients to allow the phytoplankton to photosynthesis and produce chlorophyll.
Discussion.
The dinoflagellates are the second most
abundant phytoplankton group (Lalli & Parsons,
1997). In this study the dinoflagellates were found
to be the least abundant phytoplankton group. Dinoflagellate
blooms usually occur in the summer, after the blooms of other phytoplankton
have occurred, this is due to the dinoflagellates
having a preference for less turbulent water and warmer. Due to this it is
possible that the dinoflagellate numbers were
relatively low because they had already reached the bloom peak earlier in the
year and had the number had begun to reduce due to the weather being colder and
the water currents being more turbulent.
The offshore site had the lowest abundance of dinoflagellates,
this is because coastal waters are considerably richer in phytoplankton than
offshore oceanic waters.
In the month of October nutrients should be in high amount due to
degradation of the thermocline and the strong mixing
of the water column. This could contribute to why there are still numbers of dinoflagellates left in the water column after their bloom
has ceased, while there is still a nutrient availabilty,
then the phytoplankton can still thrive.
Llandudno was the site that had the highest values for all five
nutrients
Silicate is the nutrient that is present in the highest concentrations.
The concentration of the phosphate is lower than that of silicate.
Observing the physical facotrs that effect
the water masses at the five sites, I noticed there was some variation in the
depths. Menai Bridge Pier had the lowest depth, while the offshore site had the
greatest depth as it was the site that was the furthest away from the shore.
Temperature variations were noticeable. The offshore site was the warmest. This
would provide an explanation as to why the greatest diversity in dinoflagellates was seen at the sites furthest away from
the shore.
The salinity did not differ by much between the sites. It is the
amalgamation of these physical factors that also contribute to the distribution
and abundance of dinoflagellates, for they determine
the surrounding environment that these organisms need to live in.
The investigation that took place in the October of 2003, could be
extended so that a more accurate picture of the factors that control dinoflagellate distribution could be drawn up. The
experiments could be carried out throughout the year which will provide a
larger understanding not only of dinoflagellate
distribution but on the larger scale of phytoplankton and zooplankton
distributions. It would also allow for a closer examination of the temporal and
spatial variations of the plankton. A year round study would also allow
comparisons to be made of the different blooms that occur throughout the year.
Lalli, C. M. & Parsons, T. R.
1997. Biological Oceanography an Introduction, 2nd edition,
Butterworth-Heinemann, Oxford.
Sykes, J. B. 1981. An illustrated guide to the diatoms of British coastal plankton. Field Studies 5, Field Studies Council.
Harris, G. P. 1978. Photosynthesis, productivity and growth: the
physiological ecology of phytoplankton. E. Schweizerbart’
sche Verlagsbuchhandlung.
Spector, D. L, 1984. Dinoflagellates. Accademic Press
Inc.
Dodge, J. D, 1985. Atlas of Dinoflagellates.
Blackwell Scientific Publications.
