The effect of Manganese on the native algal species Pseudokirchneriella subcapitata Emily Christine - PowerPoint PPT Presentation

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The effect of Manganese on the native algal species Pseudokirchneriella subcapitata Emily Christine

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Title: The effect of Manganese on the native algal species Pseudokirchneriella subcapitata Emily Christine


1
The effect of Manganese on the native algal
species Pseudokirchneriella subcapitataEmily
Christine SidersMarietta College
  • Methods
  • Three 50 ml flasks were used for each of the
    four concentrations. Each flask contained
  • 9 ml of ultra pure water
  • 2 ml of Pseudokirchneriella subcapitata
  • 9 ml of Alga-grow Medium
  • For the control condition, no MnCl2.4H20 was
    present in the Alga-grow Medium, while 5, 50, or
    500 ppm was present in each experimental
    condition. The Twelve flasks were stirred
    continuously on a shaker under a 12 hour
    light/dark cycle. Each concentration of the
    Pseudokirchneriella subcapitata cells were
    counted daily for five days with a hemocytometer
    then calculated for total number of cells in each
    flask. The formula is as follows
  • cells per milliliter n/10 x 250,000
  • where n total number of counted cells
  • A total of three replications were
    conducted and the data were analyzed using SPSS.
  • Introduction
  • Manganese is one of the main pollutants in
    the Marietta, Ohio area due to Eramet. Eramet is
    the leading producer of ferromanganese alloys in
    the world as well as producing manganese based
    products for the chemical industry. According to
    a 2005 investigation by the US Department of
    Health and Human Services, the Ohio River in
    Washington County, Ohio has a manganese
    concentration of approximately 5 parts per
    million. The elevated concentrations released
    into the environment may have an effect on
    organisms that inhabit the area.
  • Pseudokirchneriella subcapitata is a
    distinct crescent shaped green micro alga that is
    found in many freshwater aquatic ecosystems,
    including the Ohio River. Its short life cycle as
    well as the little space and care that is
    required for it to flourish makes
    Pseudokirchneriella subcapitata an ideal organism
    for laboratory use in toxicology studies as a
    bioindicator. Bioindicators are used to monitor
    the health of an environment or ecosystem.
  • The purpose of this experiment was to look
    at the effect of manganese on the growth of an
    algal species native to the Ohio River in
    Washington County, Ohio. Further, to develop an
    understanding of toxicology as well as build on
    basic lab techniques.
  • It was hypothesized that the lowest
    concentration of manganese (5 parts per million)
    will not have a significant effect on the
    population growth of Pseudokirchneriella
    subcapitata, while the higher concentrations of
    50 and 500 parts per million will have a
    detrimental effect on the population growth.
  • Results
  • The overall growth rates (in cells/ml/day)
    for each condition are shown in Table I. Figure
    I illustrates the cumulative daily averages for
    each condition throughout the trials.
  • A 4 (conditions) x 5 (day) Mixed Factor
    ANOVA was used to analyze the data. There was a
    significant main effect of condition F (3,32)
    26.71, p lt .001 as well as a significant
    interaction of condition and day, F (12,128)
    16.77, p lt .001. All conditions were
    significantly different except for the 50 ppm and
    500 ppm (p .312).
  • Discussion
  • The lowest concentration of manganese (5
    ppm) did not have a significant effect on the
    population growth of Pseudokirchneriella
    subcapitata, while the higher concentrations of
    50 and 500 ppm did have a detrimental effect on
    the population growth. This research suggests
    that increasing levels of manganese may cause a
    decline in native alga species, which has
    significant implications for the Washington
    County, Ohio area. In future research, more
    replications as well as concentrations under 50
    ppm should be used due to the significant decline
    of growth seen at the 50 ppm condition.
  • References available upon request.

Table I Overall growth rates (cells/ml/day)
Figure I Cumulative average cell counts for
trials I, II, and III
Acknowledgements Dr. Brown, Dr. Hogan, Mrs.
Jarrell, Biology senior capstone class, Dr.
McCabe, Dr. Pate, Dr. McKay, Dr. Tschunko,
Marietta College Biology Department, Andrea
Marion, Allison Rhea, Christiana Hilditch, and
David Borrelli.
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