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PHYTOPLANKTON & ZOOPLANKTON ANALYSIS
Throughout the transect, zooplankton community composition varies, with some types
not being present at various depths and stations. However, the one consistency that
remains throughout is the large amount of copepoda. These tiny crustacea continued
to remain the dominant zooplankton throughout the transect, portraying their adaptability
to a range of abiotic and biotic factors, regardless of well-mixed or stratified
waters. The data here was log transformed on account of the heavy influence of copepods,
which occurred in numbers several magnitudes of volume higher than other zooplankton.
The highest abundance of zooplankton occurs at site 37. There doesn’t appear to be
a significant trend between site and total abundance. Likewise, there appears to
be no correlation between depth and total abundance. With only 5 samples however,
it is difficult to draw any informed conclusions. To better assess the effect of
depth on zooplankton distribution, a continuous plankton recorder could be used.
This would allow us to sample larger areas in smaller depth ranges.
Diversity
The pie charts for deepest waters show a dominance by copepods. This is likely due
to their variety of feeding types and mobility, allowing them to cover large areas,
increasing their prey encounter rate and consume falling detritus from the more productive
surface waters whereas other species such as Noctiluca only appear to be present
in the upper 15m of water around high phytoplankton abundance, suggesting they are
less mobile and rely on larger blooms to sustain them. Site 35 is the most diverse,
however all sites maintain a level of diversity largely equivalent to each other.
The shallower depths have a large amount of sunlight, allowing for phytoplankton
bloom, a useful resource that can be utilized by this large variety of species. All
in all, it appears as though greater diversity correlates with shallower depths.
Many of the species observed in these areas are in their larval stages. The copepod
nauplii as an example, are present in the highest abundance in the upper 20m. It
is also important to note that some species appear early on in the transect, but
stop appearing at later sites. Types of plankton that fall into this category include
Noctiluca and decapoda larvae, perhaps indicating their inability to survive in more
stratified waters.
Figure 45: A graph depicting the types of plankton (y axis) and their abundance (x
axis) found at various sites and depths (coloured bars) along the offshore transect.
Figure 46: A graph depicting the total abundance of zooplankton seen at each depth
and site where a sample was taken, on the offshore transect.
Figure 47: A graph depicting the types of plankton (y axis) and their abundance (x
axis) found at various sites and depths (coloured bars) along the offshore transect.
Figure 48: A graph depicting the total abundance of phytoplankton seen at each depth
and site where a sample was taken, on the offshore transect.
Much like zooplankton abundance, species composition of phytoplankton varies throughout
different depths and sites along the offshore transect. The species found to have
the highest abundance overall was Ceratium lineatum (figure phytoplankton pie chart)
but unlike copepoda (figure zooplankton), this consistency is not constant with every
site, such as the species only being dominant at two depths at site 35, but not being
seen at 29m, perhaps caused by the lower light attenuation. This pattern continues,
whereby when this species is present, it is found to dominate, but only at shallow
depths. Some mid depths of around 15-30m show dominance by Chaetoceros. However,
this species is absent from site 35 at the equivalent depth. Instead at this depth,
Ceratium furca dominates. The highest total abundance of phytoplankton can be found
at 16.9m deep at site 40. This corresponds to where we found the strongest evidence
of a thermocline, supporting the idea of a deep chlorophyll maximum occurring where
the upper light rich surface waters meet and mix with the lower nutrient rich waters.
At this depth we observed large amounts of Mesodinium, a highly mobile ciliate which
thrives in low nutrient surface waters by actively moving between shallow and deeper
waters, gathering nutrients from depth and photosynthesizing in surface waters (Lips
and Lips 2017). Aside from site 40, the highest levels of chlorophyll are found in
surface waters, suggesting that in these well mixed waters, light availability is
the main factor influencing bloom dynamics.
Diversity
Depths with highest species diversity are those that are shallow. In the shallow
waters at site 40 however, large amounts of Dactyliosolen fragilissimus are present
in isolation to any other species. This species is known to occupy stratified surface
waters (Lotocka 2006) and is absent from any other sites. This perhaps is evidence
of the formation of the thermocline and the corresponding temperature and nutrient
mixing changes leading to completely different bloom formations. Another exception
occurs at a depth of 29m, having 4 different species present, and a substantial number
of each, whereas site 37, at a depth of only 1.3m more, only 3 species were present,
and were found to be fewer in abundance. This would most likely imply that again,
a differing amount of stratification is causing a change in nutrient distribution
in the water column, leading to slower growth rates and a loss of diversity.
Figure 49: Key for Figure 50-54
Figure 55: Key for Figure 56-68
DCM
Subsequent to spring blooms as irradiance increases and nutrients become depleted
at the surface a deep chlorophyll maximum forms, as observed at station 40, furthest
offshore, at 16.9m. The deep chlorophyll maximum (DCM) is a subsurface layer enriched
in chlorophyll (Chl), that typically develops coinciding with the thermocline/nutricline
enabling phytoplankton to meet their growth requirements from cool, nutrient rich
deep waters below and high irradiance surface waters above (Latasa et al.). Here
diatoms are likely to be the most successful phytoplankton group, such as Chaetoceros
at station 40 due to adaptations allowing them to thrive in productive regions including
high growth rates, low Kn values and grazer defence mechanisms (Widdicombe et al.)
(Merzouk et al.).
DAPI MICROSCOPY AND IMAGE ANALYSIS
META DATA:
DATE: (09/07/19)
STATION 40: (50° 05.953, 004° 14.918)
FILTER 4 (43.2m)
FILTER 10 (7.7m)
FILTER 14 (16.9m)
Having DAPI-stained micro-organisms from station 40 samples, furthest offshore (50°
05.953, 004° 14.918) onto three filters the cells were visualised using epifluorescence
microscopy and image analysis which in turn aided in obtaining total microbial cell
abundances and photosynthetic abundances in the samples.
The epifluorescence microscope (courtesy of the Marine Biological Association), excited
fluorophores in the sample at approximately 475nm using a dichroic mirror. In response
they emitted light at a specific wavelength which was longer and lower energy which
allows individual fluorophores, in this case chlorophyll, in the sample to be detected.
Using a DAPI (which binds to DNA) overlay – we can assess which of these fluorophore
emissions are representative of true phytoplankton cells in the sample. If there
is no overlap, this provides potential evidence of heterotrophic cells or cyanobacterium
in the sample that absorb different wavelengths of light. Five sets of images (DAPI
and autofluorescent) were taken for each of the three filters and loaded into ImageJ
software in which mean cell counts were conducted and total cell counts were obtained
via the following equations.
A total microbial biomass was then obtained by multiplying the mean cell abundance
by 5Cml-1-assuming that this is the lowest cell-specific carbon content (Whitman
et.al, 1998).
The graph illustrating the estimated microbial biomass demonstrates that phytoplankton
cells, represented via chlorophyll biomass, were most abundant at 16.9m (398.148
fg C ml-1) at station 40. This would be expected due to the respective requirements
of phytoplankton cells for higher irradiances are corresponds with the location
of the DCM as shown via CTD profiles. Consequently, chlorophyll biomass was extremely
lower at 43.2m (Alternatively, the highest DAPI biomass is located at 43.2m (1189.3625
fg C ml-1), perhaps due to a lower requirement of heterotrophic bacteria and cyanobacteria
for high irradiances. It is also plausible that the heterotrophic bacteria locate
at the base of phytoplankton activity to obtain raining dissolved organic matter
via marine snow and phytoplankton detritus (Branco et.al, 1996).
At station 40, three samples were taken to undergo flow cytometry in the lab. Cyto
82 was taken at 17.7m depth, Cyto 89 at 16.9m and Cyto 87 at 4.6m. Cytometry is used
to count both the number of cells in a sample, as well as the red fluorescence seen,
which can be used to indicate chlorophyll levels. The Cyto 82 and Cyto 89 represent
samples which were taken either side of the chlorophyll maximum, as seen in the depth
profile for station 40.
What can be seen from the results in figures 73 and 74 is that for all depths, the
nanoplankton have a much higher value for both the cell numbers and the red fluorescence.
As well as this, 16.9m has the highest values for all nanoplankton and total counts,
yet for microplankton both higher values occur at 17.7m