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Production and mortality
of phytoplankton and sea-ice microalgae in the Southern Ocean By Dr. philos. Knut Yngve Børsheim and dr. scient.
Geir Johnsen* The Norwegian University of Science and
Technology, Laboratory of Biotechnology, N-7491
Trondheim, Norway. *Trondhjem
Biological Station. |
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Contents Project summary
Introduction
Description of woork
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| ![]() Literature cited Agusti, S., Satta,
M.P., Mura, M.P., and Benavent, E (1998) Dissolved esterase activity as a
tracer of phytoplankton lysis: Evidence of high phytoplankton lysis rates in
the northwestern Mediterranean.
Limnol. Oceanogr. 43:1836-1849. Børsheim, K.Y. (1990) Bacterial biomass and production rate in the Gulf Stream front regions. Deep-Sea Research 37:1297-1309. Børsheim, K.Y., Gerdts, G., and Schütt, C. (submitted). Proteolytic activity in experimental temperature gradients measured in four size fractions along a trophic gradient in the North Sea. Mar. Ecol. Progr. Ser. Børsheim, K.Y (submitted) Bacterial production
rates and concentrations of organic carbon at the end of the productive
season in the Greenland and the Norwegian Sea. Aquatic Microb. Ecol. Børsheim, K. Y. and Myklestad, S. M. (1997) Dynamics of DOC in the Norwegian
Sea inferred from monthly profiles collected during three years at 66oN,2oE.
Deep-Sea Research 37:1297-1309 . Christian, J.R. and Karl, D. M. (1995) Bacterial ectoenzymes in marine
waters: Activity ratios and temperature responses in three oceanographic
provinces. Limnol. Oceanogr. 1042-1049. Johnsen, G., Prézelin,
B. B. and Jovine, R. V. M. (1997)
Fluorescence excitation spectra and light utilization in two red tide
dinoflagellates. Limnol. Oceanogr. 42:1166-1177. Kirchman, D.L. (1999)
Phytoplankton death in the sea. Nature 398:293-294. Kroon,
B., Prézelin, B. B. and Schofield, O. (1993) Chromatic regulation
of quantum yield for photosystem II charge separation, oxygen evolution and
carbon fixation in Heterocapsa pygmaea (Pyrrophyta). J. Phycol. 29:453-462. Wheeler, P.A., Gosselin, M., Sherr, E., Thibault, D., Kirchman, D.L.,
Benner, R. and Whitledge, T.E. (1996) Active cycling of organic carbon in the
central Arctic Ocean. Nature 380:697-699. |
Project summary During the NARE
2000/2001 expedition, the project will measure primary production, mortality of
microalgae and microbial loop variables in samples from open ocean water
profiles and samples of algal communities collected from sea ice. Microalgal
production and mortality will be investigated by the introduction of two new
methods. A Pulse Amplitude Modulated fluorometer will be used to measure
primary production and pigment variables. Measurements of the concentration
and turnover of enzymes released from microalgae at death will be used to
estimate mortality. In addition, DOC and bacterial production, which are
identified as important microbial loop variables, will be measured using
already established methodology. Introduction The primary production
in the open ocean in the Antarctic regions is low compared to other ocean
areas, whereas sea ice to some extent represent sites of enhanced
productivity. Still, due to the vast extension of these regions, the
Antarctic water ecosystem as a whole supports large populations of pelagic
animals such as krill and marine mammals, and seabirds. These secondary
producers rely to a large extent on a healthy microbial food web, where
particulate production enter the higher levels by routes indicated in Figure
1. Microalgal primary production is a key component, but
only part of this production is directly transferred into the food chain by
grazing. Part is transferred to DOC, either by excretion from healthy cells,
or from lysis of cells by other mortality factors. Also other parts of the biota adds to the DOC pool through
losses of organic material , and the reutilization of DOC by heterotrophic bacteria is an
important component in the production scenario. Heterotrophic bacteria are
the principal consumers of DOC, and bacterial production represents the
pathway whereby the material in the
DOC-pool can be transferred into particulate form which can be available to
the food web by micro-zooplankton grazing. Present evidence demonstrates that
the flow of material through this microbial loop is especially important in
oligotrophic waters such as the Southern Ocean, and we will therefore include
bacterial production in our selection of measurements. The
presence of a high contribution of the microbial loop input to the grazing
food chain, suggest that microalgal mortality induced by factors other than
grazing may have a proportionally high impact in the oligotrophic waters of
the Southern Ocean. For this reason alone, it is very interesting to
introduce methods which can be used to quantify death rates. In
the present project we want to introduce new methods/approaches for on site
measurement of mortality and primary production of microalgae (phytoplankton
and sea-ice microalgae). Knowledge of mortality and production rates is
crucial for the understanding of
population dynamics. A new method for the detection of esterases
released by algal lysis, will be used on board. Likewise, a new
method/approach for the estimation of primary production will carried out
using a Pulse Amplitude Modulated fluorometer (PAM) instead of the
traditional 14C incubation technique. The PAM technique measures
the electron transfer rate to photosystem II, the site of oxygen production
of the algae. The amount of electrons generated can be transformed to oxygen
units based additional irradiance measurements, the chl a-specific absorption
coefficients and the fraction of light received by photosystem II [scaled
fluorescence excitation spectra, unit: m2 mg (chl a)-1
, cf. Johnsen et al. 1997]. The pigment composition will also be measured to
discriminate between different algal groups, pigment functionality
(photosynthetic vs. photoprotective) and the corresponding degradation status
which then can be related to mortality. As
a pilot experiment, the PAM technique will
also be used to measure the gut (algal) content of crustacean
zooplankton by detecting chlorophyll a fluorescence using fiber optics. To
the best of our knowledge, this has never
been tried before. Description of work We propose to study
primary and secondary production rates, and the fate of microalgal production
in the food web by combining a set of new methods with classical methods. New methods & approaches: PAM A submersible Pulse
Amplitude Modulated fluorometer (DIVING-PAM) containing irradiance
(Photosynthetic Active Radiance, 400-700nm, ×mmol quanta m-2
s-1), temperature (ºC), pressure (atm), and fluorescence yield of
photosystem II for estimation of photosynthetic electron transfer rate (ETR)
will be used in situ (under ice)
and on deck. This submersible «mini-laboratory» can be controlled by a
two-way communication cable connected to a computer allowing time-series
(minutes, hours, days) of changes in photosynthesis, irradiance, temperature,
and pressure (depth). Samples
will be collected by means of Niskin bottles
for open water phytoplankton, and preferably by scuba diving for ice
algal communities. For later measurements in the laboratory of chlorophyll a
specific absorption coefficients, light transferred to photosystem II (scaled
fluorescence excitation spectra) and pigment composition (high pressure
liquid chromatography), preparations will be stored in liquid nitrogen. The
SCUBA diver in this project hold a class S certificate (certified scientific
diver issued from the Directorate of labour inspection, Norway). If SCUBA diving
will not be allowed, we will collect ice algae by ice core drilling and
eventual scraping of under ice floes. Measurements
of the gut turnover of krill by means of PAM fluorescence kinetics will be
performed using a 2 mm thin optical nylon fiber. Microalgae mortality by enzyme assay Direct measurements of
phytoplankton loss rates have been obstacled by the lack of methods, although
the importance of measurements of this process have been recognised for
decades (Kirchman 1999). Recently a new method has been published that
facilitates simple and reliable measurements of the rate of release of
intracellular products from phytoplankton cell death (Agusti et al. 1998).
Death of a cell, such as caused by senescence, UV radiation, viral lysis and
to some extend handling by gracing zooplankton will release intracellular
material into solution in the surrounding medium. Some of the intracellular enzymes are measurable by
extremely sensitive techniques which can easily be handled under shipboard
conditions (Christian and Karl 1995). Agusti et al. (1998)
demonstrated that intracellular esterases are suitable as tracers of
phytoplankton cell death, because they are present in stable amounts in all
phytoplankton, are released by death, and they are easy to measure. Moreover,
they showed that the turnover of esterases, once released into the medium, is
of a suitable time scale, so that turnover also is measurable, and
consequently the combination of concentration measurement and turnover
measurement yield production rates, i.e. cell death rate for each sample
investigated. Additional variables In order to
establish a set of essential data
within the framework depicted in Figure 1, we will include measurements using
a small selection of conventional methods which we have used successfully in
a large variety of environments. Concentrations of DOC will be measured by
high temperature combustion on samples which will be frozen and analysed
ashore (Børsheim and Myklestad 1997). Bacterial production rates will be measured
using 3H-thymidine incorporation rates (Børsheim 1990). Project size Manpower needed are two
persons on the cruise. With this we will be able to process 2 profiles per
day during the active part of the oceanographic expedition. With one profile we
mean 12 discrete water samples, either taken as vertical profiles (by Niskin
samplers mounted on a rosette) from the euphotic zone at open water
locations), or from samples collected in the viscinity of floes, including
samples of intrusion brine, floe pore
water, and vertical profiles below ice floes of selected age and condition.
Selection of floes and the amount of time spent at such sites could be
co-ordinated with other projects during the cruise, ideally the investigation
of 7-12 floes would be appropriate for the purposes of our study. Methods Production rates Pulse Amplitude Modulated fluorometry (PAM) and bio-optical measurements: The Pam will be used to measure the
fluorescence yield from Photosystem II and absorbed quanta to estimate photosynthetic
rate, PO2, mg O2 produced mg Chl a -1 h-1) according to Kroon et al. (1993)
and Johnsen et al. (1997) where:
PO2 = AQ
· FII · IIe· AQ = Absorbed quanta (unit: mmol
m-3 h-1) FII =
Fraction of AQ directed to Photosystem (PS) II (included its Light Harvesting
Complexes), unit: dimensionless. IIe = PAM yield [(Fm’-Fo’)/Fm’] = Operational quantum yield for
stable charge separation at PS II (mol charge separation mol quanta-1). IIe (ratio of oxygen evolved
per electron generated at PS II ): Since 4 stable charge separations are
needed at PS II to evolve 1 O2-molecule, i.e.: A: IIe (the PAM yield) must be divided by 4, i.e. to give mmol
O2 mmol quanta-1 B:
Multiply A with 0.032 to give mg O2 mmol quanta-1. Finally: [AQ (mmol m-3 h-1)
(mg O2 mmol quanta-1) / mg Chl a m-3 FII] gives us: PO2
(mg O2 produced mg Chl a -1
h-1) Chlorophyll
a specific absorption coefficients (total amount of light received by the
algae) and the corresponding fraction utilized by photosystem II (oxygen
production site) will be measured by means of spectrophotometry (Hitachi 150
spectrophotometer) and spectrofluorometry (Hitachi F3000 spectrofluorometer,
respectively (Johnsen et al. 1997). Pigment isolation will be carried out
using a Hewlett Packard Series 1100 high performance liquid chromatograph
using the method outlined in Johnsen et al. (1997). Phytoplankton
mortality
Assays of enzymes in
seawater depend on artificial substrates that leaves a fluorescent product
after cleavage of specific bonds in the substrate. There are several such
substrates that yield products which are easily measured in a spectrofluorometer.
For the measurement of esterases, fluorescein diacetate (FDA) is highly suitable for use in seawater
(van Boekel et al. 1992, Agusti et al. 1998). One important refinement introduced by Agusti et al.
(1998) was the added protocol for the estimation of esterase turnover in each sample. With this information the
utility of the activity measurement is transcended, because production rate
then can be calculated, and this will in the case of a strictly intracellular
component be proportional to cell lysis (death) rate. The
measurement of esterases has not before been reported in Antarctic
investigations, however several studies have shown that similar assays
(targeting proteases and lipases) have proven very useful and informative
when applied in microbial studies in the area (e.g. Christian and Karl 1995).
One of us has first hand experience with the shipboard use of such methods
(Børsheim et al. submitted). DOC and bacterial production There are several
reports that suggest that a large part of the production in Antarctic waters
are channeled through the microbial loop (Christian and Karl 1995). With our
approach we will be able to demonstrate if gradients in phytoplankton cell
death are parallelled by gradients in bacterial production, or whether these
processes are uncoupled in time and space. Another important gradient can be
found in the viscinity of ice-floes. Cell death and release of intracellular
material is one source of DOC. Recent studies have shown estimates of
turnover of semilabile DOC in polar
regions (Wheeler et al. 1996, Børsheim submitted). We therefore plan to
measure DOC and consumption of DOC. Bacterial production rate will be
measured useing thymidine incorporation rates according to Børsheim (1990),
and DOC will be measured using high temperature combustion of samples which
will be frozen and analyzed ashore according to Børsheim and Myklestad
(1997). |
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