Marine
Pollution
(Adapted
from the Duke University's Connected Curriculum Project)
Background
Tributyltin
(TBT) is a chemical that is acutely toxic to many species of marine animals.
For this reason, it effectively inhibits the growth of marine organisms when
used in marine paints (e.g., on boat hulls) and in other
"antifoulants." However, because of concern about the adverse effects
on marine life of TBT leaching from treated surfaces, strict controls on the
use of TBT have been implemented in France, the United Kingdom, the US, and
other jurisdictions.
Maine,
a state with a low population density, is perceived as having a relatively
unpolluted coastline, but there are activities that do pose pollution threats.
Activities such as shipyards, pleasure craft, commercial ship traffic, and wood
and fishing net preserving are all potential sources of TBT. Because of this,
members of the Bowdoin College Hydrocarbon Research Center and the Marine
Research Laboratory conducted a study to learn about the extent of TBT inputs
in Maine locations; learn about TBT in mussels from various field locations;
and relate TBT in mussel tissues to an overall indicator of stress. Mussels were used in this study because they
are an effective organism for detection of marine pollutants.
Data
Collections
of blue mussels, Mytilus edulis, were sampled from 15 coastal Maine intertidal
locations (plus one location in England) at various times between October 1987
and November 1989. Six of the samples in 1987 formed three pairs, with one
member of each pair in an area of high marine activity and the other in the
same general vicinity but more remote from such activity. As part of this study, chemistry professor
David Page and undergraduate student Tamara Dassanayake analyzed the relationship
between mussel shell thickness (as an indicator of stress) and the
concentration of TBT found in the cell tissues of the organisms.
Shell
thickness index (TI) was determined on the shells of 12 to 25 animals collected
from each site. TI is a dimensionless quantity defined as 100 times shell depth
(i.e., "thickness") divided by shell length. The concentration of TBT
in the cell tissues (abbreviated below as TBT) was measured in micrograms (mg) per gram of tissue. (The measurement of
this quantity required a complicated analytical procedure whose description we
omit.) The results are given in the following table.
Results of TBT
and Thickness Index analyses in tissue samples of mussels
|
TBT (mg/g) |
TI |
TBT (mg/g) |
TI |
|
0.04 |
0.40 |
1.66 |
0.50 |
|
0.11 |
0.42 |
3.56 |
0.56 |
|
0.50 |
0.43 |
0.27 |
0.48 |
|
0.60 |
0.43 |
0.45 |
0.45 |
|
0.73 |
0.46 |
0.74 |
0.44 |
|
0.77 |
0.46 |
1.75 |
0.48 |
|
1.75 |
0.48 |
0.04 |
0.42 |
|
4.31 |
0.53 |
0.04 |
0.39 |
Problems
1.
Plot
the data on TBT concentration and thickness index. What sort of relationship seems to exist between the
concentration of TBT in the cells of the mussels and the thickness of their
shells?
2.
Compute
the regression line for the data. How
good is the fit between the line and the data?
3.
Plot
the residuals for your regression line.
What does this plot tell you about your linear model?
4.
Give
physical interpretations for the slope and intercept of the line.
5.
What
conclusions can you draw from your results?
Is there reason to be concerned about TBT pollution (i.e. who cares
about thick-shelled mussels, anyway)?