Physico-chemical monitoring and mathematical modelling (made
at IBP SB RAS and ICS SB RAS): The
mathematical model of vertical stratification of sulphur cycle components
in LakeShira
was improved. In particular, for modelling of microstratification of
phototrophic bacteria observed in chemocline zones, the constant of
hydrogen sulphide concentration limit below which the growth stops was
introduced into the equation of specific growth rate of green sulphur
bacteria. The biological meaning of such modification is that obligate
anaerobic microorganisms are unable to grow in a microaerophilic zone,
which in model calculations corresponds to the depth of zero concentration
of hydrogen sulphide at the upper border of hydrosulphuric zone. As a
result, in model calculations the microstratification of phototrophic
bacteria in the chemocline zone was obtained, i.e. a more appropriate
description of the microstratification of bacterial population, which
increases the predictive capacity of the model. The one-dimensional (in vertical direction)
mathematical model was modified for the investigation of the annual
temperature and salt regimes of the water bodies taking into account
spring snow melting both at the lower and upper surfaces of the ice cover.
Calculations were made on the basis of the developed one-dimensional model
using field data. The results of calculations of the thermal and salt
regimes of lakes Shira and Shunet correspond to the field data.
Microbiological
investigations (made at IBP SB RAS, IMB RAS and IBIW RAS): Using a thin-layer multi-syringe sampler, the structure of species
diversity and spatial distribution of dominant bacterial forms was
analyzed in the chemocline zones of lakes Shira and Shunet. The analysis
of 16S rRNA fragments was made by PCR method with universal bacterial
primers and subsequent analysis using DGGE (Fig. 1). In the chemocline of Lake
Shunet,
7 unindentified dominant bacterial forms were revealed, which we
symbolically A,B,C,D,E,F,G. It was discovered that there is a clear-cut
vertical spatial separation of dominant bacterial forms along the gradient
of redox potential, as well as that the species composition in the
chemocline of LakeShunet
suffered a qualitative change during the investigated period - from May
to September. It became clear that the bacterial comminuty of the
chemocline of LakeShira
differs from the same of LakeShunet.
In particular, only two dominant species, E and G, were discovered in
Shira, these two species being among the dominant ones in Shunet, too.
Fig.
1:PCR/DGGE - analysis of
16S rRNA fragments of bacterial communities of the chemocline of lakes
Shira and Shunet. The meaning of symbols above the tracks: М - microaerophilic zone (traces of oxygen are present),
R - redox zone (zero concentrations of oxygen and hydrogen sulphide), S1,
S2, S3 - hydrosulphuric zone, with the increase of
number the depth increases by 5 cm. For all series of Shunet, except May,
the depth interval between the adjacent tracks is 5 cm. In the "Shunet
25.05.2005" series the difference between M and R is 15 cm, between the
rest - 5 cm. The depth in all series increases from right to left. The
track for Shira was obtained from the sample corresponding to the middle
of "pink" layer with traces of hydrogen sulphide. Below the tracks the
numbers of sampler syringes are indicated (they are necessary for exact
identification of samples in different analyses).
Protozoological
investigations (made at IBP SB RAS): The
monitoring of the seasonal dynamics of the protozoan community was
continued in the chemocline of Lake Shunet.
The number, biomass and production of the main components of
protozooplankton of the chemocline zone were calculated for the current
year. The
laboratory cultures of the most numerous (in the chemocline of Lake Shunet)
species of phytoflagellates and two species of infusoria were obtained.
The laboratory experiments aimed at cultivation of these species on
artificial media and various substrates were conducted. It was found out that the laboratory cultures of hydrocoles isolated from
the chemocline zone of Lake Shunet are able to grow and develop in aerobic
conditions in daylight, which is much more intense than the illumination
of their natural habitat. Thus, these organisms cannot be ascribed to
anaerobic ones, - on the contrary, thay apparently possess a high degree
of tolerance and are able to exist in the wide range of concentration of
hydrogen sulphide, oxygen and illumination. It was shown that the specific growth rates of Cryptomonas salina
population in natural environment varied from 1,15 to 3,15 h-1, the growth rates of the laboratory culture - 2,31-3,82 h-1.
Such high growth rates of Cryptomonas population in the lake under
light limitation conditions are possibly caused by the additional
nutrition of these organisms by way of mixotrophy. The specific growth rates of the laboratory cultures of infusoria Cyclidium
spp. and Euplotes spp. on the investigated substrates are
considerably higher than in the water body environment.
Investigations
of phyto- and zooplankton (made at IBP SB RAS and KSU): The
monitoring of C, N, P and PUFA (polyunsaturated fatty acids) of the seston
and zooplankton of LakeShira
was conducted in the epilimnion and in the oxic and anoxic zones of the
hypolimnion. For the estimation of the flow of biogenic elements and PUFA,
that are lost in hydrosulphuric zone, sediment traps were used.
It was found out that the average flow of biogenic elements being part of
dead zooplankton into the anoxic zone was 3.5 mg С/m2/day or 3.2% of
zooplankton daily production. The flow of nitrogen and phosphorus was 0.5
mg N and 0.07 mg Р /m2/day, correspondingly.
The treatment of samples that are necessary fot the calculation of lost
biogenic elements being part of the dying phytoplankton is not finished
yet. However, according to literature data, about 20-25% of phytoplankton
primary production settles in lakes with temporary hydrosulphuric zones (Veronesi
et al., 2002), the loss of P beingdisproportionately
lower. Thus, stratified lakes show an extremely high degree of closing of
carbon and biogenic elements on the level of pelagic oxic zone. About
75-80% of phytoplankton primary production and up to 96% of zooplankton
production mineralizes in the oxic zone. It was revealed that the
plankton community retains not only biogenic elements, but also a part of
PUFA. Acids that are indispensable for animals - a18:3w3 (0.36 mcg/l),
18:3w6 (0.12 mcg/l), and hardly synthesizable 20:5w3 (0.61 mcg/l), 22:6w3
(0.07 mcg/l) were observed in the oxic hypolimnion and were absent in the
hydrosulphuric zone. The essential acid 18:2w6 was an exception, but its
concentration, with the transition to the hydrosulphuric zone, became
almost 2 times as lower (0.26
mcg/l - oxic hypolimnion and 0.16 mcg/l hydrosulphuric zone). The
proportion of PUFA in the seston and bodies of crustaceans A.salinus is represented in the table.
Table. The
proportion (%) of essential polyunsaturated acids (PUFA) in the seston and
zooplankton of lakeShira
on different horizons.
PUFA
Seston
Zooplankton (A.salinus)
Epilimnion
Oxic hypolimnion
Anoxic hypolimnion
Epilimnion
Oxic hypolimnion
Anoxic hypolimnion
18:3w6
0.00
0.99+0.14
0.00
0.21+0.07
0.24+0.03
nd
18:2w6
0.00
2.17+0.49
1.40+0.19
3.21+0.31
3.60+0.34
nd
a18:3w3
0.00
2.91+0.47
0.00
7.06+0.60
8.59+0.68
nd
20:5w3
0.00
3.98+1.05
0.00
7.98+0.87
9.52+0.78
nd
22:6w3
0.00
0.43+0.16
0.00
4.15+0.78
5.06+0.78
nd
It is evident that the synthesis of essential acids is limited by the
hypolimnion oxic zone, while in zooplankton they are present on all
horizons. Hence, the retention (accumulation) and spatial redistribution
of PUFA in the lake is realized through zooplankton. Thus,
it was revealed that in a stratified water body with a hydrosulphuric zone
the cycle of not only biogenic elements, but also of essential biochemical
compounds (PUFA) becomes more complete within the bounds of the pelagic
oxic zone due to the specific organization of plankton community
functioning.
Bioluminescent testing of lake water (made at IBP
SB RAS): The
sensitivity of the following bioluminescent test-systems was investigated:
1) bioluminescent system with quinone, 2) enzymes of bioluminescent
bienzymatic system immobilized into starch gel, 3) jointly immobilized
enzymes and substrates of bienzymatic system - with a view to the effect
of the water of LakeShira.
It was shown that the water samples taken along the shoreline of the lake
inhibited the intensity of luminescence of the soluble bienzymatic system
NADH:FMN -oxidoreductase-luciferase to the extent of 20% on average, while
they didn't affect the immobilized bienzymatic system. The intensity of
luminescence of the bienzymatic system NADH:FMN -
oxidoreductase-luciferase in solution and in immobilized state in the
presence of the water samples taken from the depth of the lake decreased
with the depth in the range of 4-6 metres. The difference in sensitivity
between the soluble and immobilized bienzymatic systems is explained by
the fact that the polymer carrier used for immobilization prevents toxic
substances of water samples from penetration into enzymes. As
a result of investigations, a modification of the bioluminescent system
with quinone was made, and the qualitative and quantitative composition of
reaction mixture components was selected. With the aim of detection of
sensitivity of the modified system to redox active compounds by the
example of model compound solutions, the effect of sulphur compounds and
phenols on the kinetics of bioluminescent system with quinone was studied.
The dependencies of changes in the kinetic parameters of bioluminescence
from the redox characteristics of model solutions were established. It was
shown that the most sensitive parameters of the bienzymatic system with
quinone affected by a reducing agent are the parameters of luminescence
detention. The efficiency of diminishing of the induction period and the
time of reaching of bioluminescence maximumin the presence of a reducing agent is determined by the
concentration and reducing properties of exogenous compounds. The
comparison showed that the bioluminescent bienzymatic system with quinone
is specific to the effect of reducing agents, its sensitivity being higher
than the same of the bienzymatic system without quinone. A
new system was adapted to the conditions of water testing of natural water
body. The water samples taken along the shoreline and from the depth of
lakes Shira and Shunet were studied. It was demonstrated that the
bioluminescence of the bienzymatic system with an oxidant is highly
sensitive to the redox characteristics of the water from natural water
bodies. High correlation coefficients were noticed between the changes in
the kinetic parameters of bioluminescence and the characteristics of the
lake water (redox potential, oxygen and hydrogen sulphide content). The
obtained results allowed to make conclusions about the possibilities and
advantages of using the new bioluminescent system with an oxidant for
ecological monitoring of natural water ecosystems with distinct redox
characteristics.