sediment toxic effects on aquatic micro life by patrick ebbert, central catholic, pjas 2008
TRANSCRIPT
Sediment Toxic Effects on Aquatic
Micro LifeBy Patrick Ebbert, Central Catholic, PJAS 2008
Introduction Algal food production could be inhibited by a
variety of pollutants in the marine ecosystem. Some of this pollution can even be found in the runoff of our own parking lots into streams and rivers.
Algae populate the oceans as well as freshwater systems abundantly and provide a basis for the entire world’s food web due to their photosynthetic abilities.
Two different species of algae (Chlamydomonas and Euglena) were tested with two different parking lot sediment samples to examine the effects.
Sediment Effects on Marine Life There are two properties of sediment that
could be potentially dangerous to aquatic life.
1. The runoff into water ecosystems can cloud the water, making it harder for light to pass through and therefore harder for autotrophs to provide themselves with sufficient energy via photosynthesis.
2. The contents of the sediment, possibly abundant with chemicals leaked from cars or other industrial locations, could have some adverse affect on the organisms because of its foreign molecular structure.
Runoff Properties Runoff from parking lot sediment can contain
many chemicals harmful to life. May contain herbicides, pesticides,
polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons (PAHs) and more.
Location of Sediment and Possible Impacts Sediment A was taken
from a school parking lot. Chemicals from fuel or rubber particles from tires could have possibly leaked into the ground.
Sediment B was taken from the driveway of a public park, containing similar particles to Sediment A.
Both of these zones were located near woodland streams containing aquatic life.
Characteristics of AlgaeEuglena
Have one large flagellum Typically 35-55um long Over 100 species Survive best in rich organic
waste Contain many chloroplasts
Chlamydomonas Have two flagella Typically 10-30um wide Eyespot helps them
gravitate toward light Found in calm waters and
damp soil Contain only one
chloroplast
Purpose The purpose of this experiment was to see
how various concentrations of parking lot sediment affect the growth of euglena and chlamydomonas.
Hypotheses Null: The growth rates of the algae
exposed to parking lot sediments will not vary significantly from the controls.
Alternative: The growth rates of the algae will vary due to different concentrations of parking lot sediment.
Methods and MaterialsBasic Experimentation Four sets of each euglena
and chlamydomonas were put into test tubes with various concentrations of rock sediment and kept under favorable lighting conditions
Spectrophotometer set at blue-green wavelength (430nm) was used to measure absorbency of algae every 3 days for 2 weeks.
Materials Test tube rack (1) Test tubes (56) 200µl micro-pipette (1) 10ml macro-pipettes (3) 5ml macro-pipettes (3) Spectrophotometer (1) Permanent marker (1) 48ml of Euglena 48ml of Chlamydomonas 160ml of spring water Daphnia magna (At least
64) Mini pipette (1) Sediment from 4 different
parking lot locations
Procedure1. Arranged 48 test tubes in test tube rack; pipetted 2ml of
Euglena into 24, and 2ml of Chlamydomonas into 24.2. Pipetted sediment and spring water into each tube as
displayed in chart on following slide.3. Absorbance readings at 430nm were recorded on days 1,
4, 7, 10, and 13.
Procedure (cont.)Sed. A: 0%
Sed. A: 10%
Sed. A: 40%
Sed. B: 0%
Sed. B: 10%
Sed. B: 40%
Spring Water
3ml 2.5ml 1ml 3ml 2.5ml 1ml
Algae 2ml 2ml 2ml 2ml 2ml 2ml
Sediment 0ml 0.5ml 2ml 0ml 0.5ml 2ml
Total 5ml 5ml 5ml 5ml 5ml 5ml
*Repeat this table 4 times for Euglena and 4 times for Chlamydomonas
Algal Growth Curve
More Graphical Comparisons
Sediment Effects on Chlamydomonas Populations
-120
-100
-80
-60
-40
-20
0
0% 10% 40%
Concentration of Sediment
Perc
en
t C
han
ge in
Ab
so
rben
cy a
t 430n
m
Sediment A
Sediment B
Sediment Concentration Effects on Euglena Populations
-100
-50
0
50
100
150
0% 10% 40%
Concentration of Sediment
Per
cen
t C
han
ge
of
Ab
sorb
ency
at
430n
m
Sediment A
Sediment B
Sediment Effects on Chlamydomonas Populations
-250
-200
-150
-100
-50
0
0% 10% 40%
Concentration of Sediment
Pere
cen
t C
han
ge in
Ab
so
rben
cy a
t 430 n
m
Sediment B
Sediment A
Sediment Effects on Euglena Populations
-150
-100
-50
0
50
100
150
200
250
0% 10% 40%
Concentration of Sediment
Perc
wen
t C
han
ge o
f A
bso
rben
cy a
t 430n
m
Sediment B
Sediment A
ANOVA Statistical Analyses
ANOVA
Source of Variation SS df MS F P-value F crit
Sample 136.3308333 2 68.16542 1.344136 0.285716084 3.55455715
Columns 30.60041667 1 30.60042 0.603401 0.447371702 4.4138734
Interaction 28.01083333 2 14.00542 0.276169 0.761841588 3.55455715
Within 912.8375 18 50.71319
Total 1107.779583 23
2-Factor Comparison of Sediment on Chlamydomonas
ANOVA Statistical Analyses (cont.)
2-Factor Comparison of Sediment on EuglenaANOVA
Source of Variation SS df MS F P-value F crit
Sample 1172326.603 2 586163.3 2.773092 0.089159558 3.55455715
Columns 110215.7067 1 110215.7 0.521422 0.479512608 4.4138734
Interaction 264199.7433 2 132099.9 0.624954 0.546505665 3.55455715
Within 3804757.025 18 211375.4
Total 5351499.078 23
2-Factor Comparison of Sediment on Euglena
Results and Conclusions The null hypothesis that the euglena would not
vary due to sediment concentrations was accepted (P-value >.05).
Also, the null hypothesis that the chlamydomonas would not vary due to sediment concentrations was accepted (P-value >.05).
In conclusion, the alternative hypothesis was rejected because there was no significant difference between either of the sediments when compared to their effects on both euglena and chlamydomonas.
Limitations and Extensions The sediment could have slightly clouded the test
tube solution, giving false readings of absorbency.
The algae also may have been an unhealthy sample (as indicated by the decline in population density)
More trials could have been used, or maybe trying the readings on more than one spectrophotometer.
Other algal samples, including natural aquatic samples could be tested.
Further Research: Daphnia Magna
For an external experiment, the water-flea Daphnia Magna was tested with the rock sediment in only one trial.
Daphnia were put in tubes of water and sediment and compared by survival percentage
Daphnia 1st-Trial Results & Conclusions Daphnia were compared in eight
total tubes, four with Sediment A, four with Sediment B.
The concentrations of sediment used were 0%, 10%, 20%, and 40%.
To the right is a graph showing the survival percentage of each tube of daphnia over a period of one week.
The Daphnia exposed to no sediment appeared to have a slower decline rate compared to the ones with 10-30% concentration.
This experiment could be expanded further to test more effects of sediment on aquatic animal groups rather than plant groups such as algae.
Sediment Effects on Daphnia Survivorship
0%
20%
40%
60%
80%
100%
120%
Day 1 Day 2 Day 3 Day 4 Day 5 Day 6 Day 7
Time
Pere
cnta
ge o
f Dap
hnia
Aliv
e
A-0
A-10
A-20
A-30
B-0
B-10
B-20
B-30
References “Chlamydomonas reinhardtii”. Wikipedia.org.
<http://en.wikipedia.org/wiki/Chlamydomonas_reinhardtii>. Dec. 16, 2007. “About Chlamydomonas”. Chlamy.org. <http://www.chlamy.org/info.html>. Jan. 7,
2008. “Euglena”. Wikipedia.org. <http://en.wikipedia.org/wiki/Euglena>. Jan. 21, 2008. “Structure of a Euglena”. Infovisual.info.
<http://www.infovisual.info/02/001_en.html>. Jan. 21, 2008 Newcombe, C.P., Macdonald, D.D. “Effects of Suspended Sediments on Aquatic
Ecosystems.” North American Journal of Fisheries Management. <http://afs.allenpress.com/perlserv/?request=getabstract&doi=10.1577%2F15488675(1991)011%3C0072%3AEOSSOA%3E2.3.CO%3B2&ct=1>. Dec. 4, 2007.
Dr. John Wilson, Biostatistician, University of Pittsburgh. Clare, John, PhD. “Daphnia”. Caudata.org. <http://www.caudata.org/daphnia/>. Jan.
23, 2008. “Contaminated Sediment in Water”. EPA.gov.
<http://www.epa.gov/waterscience/cs/>. Dec. 4, 2007.