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Tory Olson Graduate Student, Biology
Introduction
Invasive species are a problem in many ecosystems. Bythotrephes longimanus,
an invasive zooplankton originating from Eurasia, invaded the
Laurentian Great Lakes in the 1980s (Lehman 1987; Berg and Garton 1988).
Bythotrephes has since been observed in inland Minnesota lakes (Branstrator et al. 2006). Bythotrephes is a predacous Cladoceran that preys upon and depletes native zooplankton populations, such as Daphnia. Zooplankton diversity is also depleted with the introduction of the spiny water flea.
Two major morphological features of Bythotrephes
are its large, dark compound eye and long, stiff caudal spine which
serves as a postcontact morphological defense against fishes
(Branstrator 2005). Due to the high visibility of Bythotrephes from their large body size and eyespot diameter, fishes larger than 100 mm in body length seem to have a strong preference for Bythotrephes, even when they are the least abundant prey (Mookerji et al.1998; Coulas et al. 1998). In fact, Bythotrephes
has often become the dominant food source for fish planktivores once
they have established themselves in a lake (Bur and Klarer 1991; Berg
and Grimaldi 1966). Research has been done regarding this matter of
visibility; however, either linear weight or eyespot diameter regression
models were used to determine visibility. No methods have been
developed to analyze total body visibility. Using software in the VDIL
gave me the opportunity to analyze whole specimens in an attempt to
quantitatively determine if Bythotrephes were more visible than Daphnia, based on total body grayness.
Methods
Photos were taken at several magnifications (1-5x) of multiple Daphnia and Bythotrephes under a dissecting microscope in Donn Branstrator’s laboratory (UMD). Photos of first, second, and third instar Bythotrephes
were taken. The color photos were converted to black and white in Adobe
Photoshop (Version 9.0). The background noise was reduced in Photoshop
by using the magic wand function to select the organism. The selected
organism was then pasted into a new blank page. Sometimes similarly
colored background would also be selected because the magic wand could
not differentiate between the organism and the similarly colored
background. If this occurred, the eraser tool was used to delete as much
background gray as possible. Finally, the pictures were saved as *.tif
files to be compatible with SCION (Figure 1).
Figure 1 Photos of Daphnia sp. and Bythotrephes longimanus. Photos were converted to black and white in Adobe Photoshop (Version 9.0) to analyze total grayness in SCION.
The free version of SCION was downloaded from the SCION website (http://www.scioncorp.com/). The grayscale of Daphnia and Bythotrephes were compared using 3 Bythotrephes individuals for each instar and 3 Daphnia
total. First, I had to select “Options” > “Threshold” to allow for a
histogram to be created. By selecting “Analyze” > “Show histogram,”
the pixel histogram was created as a means to quantify the total
“grayness” of an individual. I summed the pixel count at each gray level
from 106 to 250 (i.e., sum of level*pixel count) of the total gray
scale ranging from 0 to 255. Magnification was corrected for by dividing
the sum by the square of the magnification (e.g., if 2x, divide by 4;
if 3x, divide by 9). The mean and variance of total grayness for each
group of organisms was then calculated and graphed in Microsoft Excel
2003.
Results
As seen in Figure 2, Daphnia had the lowest
total grayness [sum of (gray level) x (pixel count at that level)], with
a mean of 21.08 and a variance of 1.55 (all results in millions). First
instar Bythotrephes had a total grayness mean= 24.22 (variance= 58.44), while second instar Bythotrephes total grayness mean equaled 65.32 (variance= 6.29). Finally, third instar Bythotrephes had the greatest total grayness, with a mean of 83.48 and a variance of 5.48. Thus, third instar Bythotrephes are approximately 4 times more visible than Daphnia based on total grayness. Second instar Bythotrephes are approximately 3 times more visible than Daphnia, while the total grayness of Daphnia and first instar Bythotrephes were not significantly different. Overall, Bythotrephes increase in visibility with age (i.e., instar), as expected. Furthermore, the increase between first and second instar Bythotrephes (41.1 million) is 2.25 times greater as compared to the increase between second and third instar (18.16 million).
Figure 2 Total grayness (in millions) of Daphnia and first, second, and third instar Bythotrephes. Values were corrected for magnification level (1-5x).
Discussion
These results support the theory that fish preferentially select for Bythotrephes due to their increased visibility as compared to native Daphnia. If not gape-limited, fish should select for the largest, most visible Bythotrephes
available. These results may be used in future studies to predict the
ratio of food present in the planktivore’s stomach (i.e., dietary
proportions). Assuming all else to be equal (e.g., zooplankton densities
equal, no outside selection pressures, fish large enough to easily
consume all sizes of zooplankton, etc.), the planktivore’s expected
stomach content ratio of 3 instar Bythotrephes: 2 instar Bythotrephes: 1 instar Bythotrephes: Daphnia
would be 4:3:1:1. However, more work must be done with larger sample
sizes and more native species to better explain total grayness variation
in Bythotrephes and native zooplankton.
Literature Cited
1) Berg, D.J. and Garton, D.W. (1988) Seasonal abundance of the exotic predatory cladocerans, Bythotrephes cederstroemi, in western Lake Erie. Journal of Great Lakes Restoration, 14, 479-488.
2) Berg, A. and Grimaldi, E. (1966) Ecological relationships between planktophagic fish species in the Lago Maggiore. Verh. Internat. Verein. Limnol., 16, 1065-1073.
3) Branstrator, D.K. (2005) Contrasting life histories of the predatory cladocerans Leptodora kindtii and Bythotrephes longimanus. Journal of Plankton Research, 27, 569-585.
4) Branstrator, D.K., Brown, M.E., Shannon, L.J., Thabes, M. and Heimgartner, K. (2006) Range expansion of Bythotrephes longimanus
in North America: Evaluating habitat characteristics in the spread of
an exotic zooplankter. Biological Invasions, 8, 1367-1379.
5) Bur, M.T. and Klarer, D.M. (1991) Prey selection for the exotic cladoceran Bythotrephes cederstroemi by selected Lake Erie fishes. Journal of Great Lakes Restoration, 17, 85-93.
6) Coulas, R.A., Macisaac, H.J., and Dunlop, W. (1998) Selective predation on an introduced zooplankter (Bythotrephes cederstroemi) by lake herring (Coregonus artedii) in Harp Lake, Ontario. Freshwater Biology, 40, 343-355.
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