LAKE AND POND ECOSYSTEM FIELD COURSE IN WINTER ECOLOGY 2006 University of Joensuu - PowerPoint PPT Presentation

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LAKE AND POND ECOSYSTEM FIELD COURSE IN WINTER ECOLOGY 2006 University of Joensuu

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Title: LAKE AND POND ECOSYSTEM FIELD COURSE IN WINTER ECOLOGY 2006 University of Joensuu


1
LAKE AND POND ECOSYSTEM FIELD COURSE IN WINTER
ECOLOGY 2006 University of Joensuu
A presentation by Antti Kokkonen, Clara Moreno,
Elena Bonet, Elodie Philippe, Harri Eerilä, Heidi
Weber, Heikki Leitala, Robert Klinger, Nadinja
Hettinga, Jonas Linke
2
INTRODUCTION
  • Overall, two different water bodies were
    studied Lake Mekrijärvi and the pond Iso-Suokko
  • located around Ilomansti (6241'N 3057'E, 157m
    above sea-level)
  • both drain into the Koitajoki drainage basin
  • Data
  • Lake Mekrijärvi Mean depth 1.7m, Surface
    area 894 h
  • Iso-Suokko Mean depth 7m deep, Surface area
    26 ha

3
INTRODUCTION
  • Different environmental conditions in winter
    time, e.g. ice cover and low temperature
  • Physical, chemical and biological parameters
    were observed (in situ measurements, analyses of
    water samples)
  • thickness of the ice cover
  • depth colour and transparency of the water
  • temperature
  • oxygen concentration and saturation
  • pH-value
  • conductivity
  • zooplankton and zoobenthos composition

4
INTRODUCTION
  • water is dark and humic (particulated and
    suspended organic substances)
  • Oligotrophic - low productivity and low amounts
    of macronutrients (P and N)
  • located in the boreal climate zone
  • dimictic

5
METHODS
  • water and sediment samples were taken with a
    Ruttner Sampler and a Sormonen Sampler
  • physical and chemical water features were
    measured
  • samples of sediment, zoobenthos and zooplankton
    were taken
  • Snow depth and ice depth were measured with a
    measure stick.
  • depth of the water body was determined
    (echo-sounder)
  • temperature of the water each two meters
    (transect)
  • samples of the surface water layer and the bottom
    layer for determination of the parameters

6
TEMPERATURE
  • Lake Mekrijärvi 1,50 m (only one measurement,
    cause of total depth 2 m)
  • In Lake Iso-Suokko
  • Temperature was measured at the surface and at 5
    different depths
  • In both lakes the surface temperature at a depth
    of 1,5 meters is between 0,5 C and 1C. the
    temperature is increasing in lake Iso-Suokko
    towards the bottom. In the depth of 10 m it is
    2,3-2,4C.
  • Lake Mekrijärvi is very shallow, thus the whole
    water body is rather cool, little stratification

7
TEMPERATURE RESULTS
Water temperature profile of Lake Mekrijärvi
8
OXYGEN SATURATION
  • To determine the oxygen saturation, the
    Winkler-method was applied.
  • In Lake Mekrijärvi four water samples in a depth
    of 1,5m were taken, while in Iso-Suokko each
    three samples in a depth of 1,5m and in 10m were
    taken.
  • In the laboratory the oxygen content was analyzed
  • The oxygen content and the percentage of
    saturation were calculated

9
OXYGEN SATURATION RESULTS
  • oxygen saturation differ largely between the
    days of measure-ment

Oxygen saturation in of Lake Mekrijärvi and
lake Iso-Suokko
10
CONDUCTIVITY
  • conductivity is a measure of the waters capacity
    to convey an electronic current
  • related to nature and concentration of ionized
    substances and temperature
  • Conductivity increases when the amount of
    dissociated substances in water increase, e.g. in
    case of eutrophication or pollution
  • average concuctivity of Finnish lakes is 6,9 mS
    m-1
  • conductivity of each water sample was measured
    with a conductivity meter

11
CONDUCTIVITY - RESULTS
12
COLOUR
  • Water of almost all lakes in Finland are brown,
    due to humic and iron compounds
  • colour is measured in mg Pt /l
  • average value for Finnish lakes is about 90 Pt
    mg/l

13
COLOUR RESULTS
14
TRANSPARENCY
  • Measurement of spectral quality and light
    extinction in water
  • measured by Secchi-Method Secchi value is the
    depth at which the disc cannot be seen any more
  • Median in Finnish lakes is 3m
  • depth is relative to light reflection from disc
    and governed by light absorption of the water,
    dissolved compounds and particles

15
TRANSPARENCY RESULTS
  • Very low Secchi values of only 50 and 55cm on all
    four days
  • values, due to high amounts of iron and humic
    compounds, implied by the measured colour values
  • low values might also be affected by other
    dissolved compounds and particles
  • The light reflection from the disc must have been
    very low as well, as both lakes were covered by
    thick ice and snow layers, which avoided light
    penetration into the lakewater

16
pH - VALUE
  • pH is a measure of acidity negative dec.
    logarithm of concentration of free H - ions in
    a liquid
  • reflects the possibility of the water to exchange
    CO2 and its biological activity
  • Ice cover (and with it the temperature) influence
    this factors strongly
  • pH of finnish lakes is from 6 to 9
  • Acidity of lake depends on surrouding and
    substrates (biotic and abiotic factors e.g.
    silica rocks and boreal vegetation) but as well
    on possible pollutants (acid rain)

17
pH VALUE RESULTS
  • Lake Mekrijärvi pH value of 6
  • Pond Iso-Suokko pH of 5,6
  • pH at the bottom seems to be slightly higher in
    lake Iso-Suokko


18
DIFFERENCES WITHIN THE LAKES
  • Temperature Stratification due to depth
  • Oxygen content higher in Iso Soukko
  • Conductivity at same level
  • Colour and transparency at same level
  • pH lower in Lake Iso-Suokko

19
ZOOPLANKTON
  • We studied density of zooplankton in Boreal lake
    and pond
  • Samples were taken with ISO standarded
    watersampler from different layers
  • Surface samples from Mekrijärvi
  • Surface and bottom samples from pond Iso-Suokko

20
METHODS
  • Samples were taken from depths 1,5 m and 11 m
  • Water was filtered through plankton net
  • Mesh size 55 µm
  • Zooplankton was treated with formalin to settle
    down to counting cuvette
  • The number of individuals were counted with light
    microscope

21
RESULTS
22
RESULTS
23
CONCLUSIONS
  • Annual changes in numbers of individuals vary a
    lot
  • Populations of those few common species express
    high variation
  • Possible reasons
  • Chemical and physical factors
  • Biological factors

24
ZOOBENTHOS INTRODUCTION
  • Extremely diverse assemblage, both taxonomically
    and ecologically
  • Invertebrates larger than 0,5 millimeters, living
    in the sediments and mud
  • The presence of this group depends on the depth,
    the oxygen concentration and the quality of the
    sediments
  • They are important for the food chain
  • They are bioindicators of the water quality

25
ZOOBENTHOS METHODS
  • Samples from two lakes Mekrijarvi and Iso
    Suokko
  • With a Kajak-sampler, three lifts of sediments
    for each subsamples, and five subsamples per
    sample

26
ZOOBENTHOS RESULTS
  • Table Zoobenthos density (individuals per m2) in
    lakes Mekrijarvi and Iso Suokko

27
ZOOBENTHOS CONCLUSION
  • Diversity in Mekrijarvi is greater than Iso
    Suokko, because it is shallower.
  • Mekrijarvi has more oxygen than Isu Suoko, better
    for spreading of zoobenthos.
  • Most abundant taxon Chironomidae
  • Dominant species
  • Mekrijarvi Copepoda, Oligochaeta and Hydracarina
  • Iso Suokko Chaoboridae and Sphaerium

28
ZOOBENTHOS SUMMER/ WINTER
  • Increase of total density in both lakes
  • Bigger increase in Mekrijarvi
  • There is the same diversity during winter and
    summer, but lower density in winter
  • Effect of the temperature and of the predation on
    density

29
THANK YOU FOR YOUR ATTENTION!
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