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Beth Holbrook Graduate Student under Tom Hrabik, Biology
Introduction
Lake trout (Salvelinus namaycush) are the primary native
predatory fish in the Laurentian Great Lakes. In the 1950s, lake trout
populations crashed throughout the Great Lakes due to a combination of
sea lamprey predation, overfishing, and reduction in spawning habitat.
Populations became so low that natural reproduction ceased in all of the
Great Lakes, except Lake Superior. The ecological importance of this
species combined with its value to the commercial and sport fishing
industries resulted in efforts to rehabilitate lake trout populations.
These measures include controlling sea lamprey populations, stocking
lake trout, eliminating commercial fishing, limiting sport fishing, and
establishing refuges where fishing is prohibited. Despite over fifty
years of management intervention, Lake Superior is the only Great Lake
where natural reproduction occurs and lake trout populations have
rebounded.
There is evidence that impediments to natural
reproduction may be occurring the first several months after lake trout
eggs hatch in the spring, yet little is known about this period of lake
trout development. In order to determine whether competition, food
availability, or bioenergetic constraints might be limiting survival, it
is important to better understand the mechanisms by which age-0 lake
trout forage. The purpose of this research was to use VDIL software to
analyze video images of age-0 lake trout feeding trials to accurately
determine parameters used in foraging models.
Overview of research
Foraging potential in fisheries is commonly
approximated using mathematical models. One common model is an
encounter rate model (Z) developed by Gerritsen and Strickler (1978):
where Rij is the reaction distance of the
lake trout, Vj is the swimming speed of the lake trout, Vi is the
swimming speed of the prey, and ui is the prey density. To estimate
daily foraging potential, the encounter rate model is multiplied by the
probability that a fish will locate, pursue, attack, and retain a prey
item.
The purpose of our research was to accurately
estimate these model parameters by conducting a series of age-0 lake
trout foraging trials in the laboratory. We replicated Lake Superior
temperatures by conducting all experiments in a temperature-controlled
chamber at 8ºC. We also simulated natural light conditions by using
cyan LED lights ranging from 450-550 nm, the predominant wavelengths
found at depths greater than 45 m in Lake Superior. The illuminance of
the LED lights was varied from 0 lux to 1960 lux to simulate a range of
depths and nighttime conditions under which age-0 lake trout may forage.
Lab foraging experiments were conduced with two different prey species, amphipods (Hyallela spp.) and mysids (Mysis relicta),
a freshwater shrimp commonly found in Lake Superior. Previous diet
studies have found that mysids are the primary food source for age-0
lake trout; however, they are extremely difficult to culture in the
laboratory. Amphipods were used in the experiments until mysids could
be captured in the field. Experiments were conducted from March until
July, as lake trout grew from approximately 30 mm to 70 mm. Feeding
trials were videotaped overhead using a Sony DCR-TRV250 digital video
camera recorder with built-in infrared light that was used to capture
feeding trials conducted at 2 lux or less.
Application of Viz Lab software
Recorded video of the feeding trials were analyzed
by importing digital clips into Quicktime 7 Pro. The clips were
exported as *.avi files in black and white, and the frame number was
reduced to 15 fps for ease of analysis. The *.avi files were imported
into MATLAB 7.0 and digitalized using a customized MATLAB software
program (Hedrick 2007). Digitalized coordinates were exported for the
length of the lake trout, the length of the prey item, the search speed
of the lake trout, the burst speed of the lake trout, the swimming speed
of the prey item, and the vector of attack. The coordinates were
imported into an Excel spreadseet and scaled to calculate distances
(mm), speeds (mm/sec), and angles of attack. Quicktime 7 Pro was also
used to view the video clips to analyze the probability that an age-0
lake trout would locate, pursue, attack, and retain a prey item during
each feeding trial.
Results
Excluding 0 lux, age-0 lake trout reacted at a
similar distance to prey at low light levels compared with high light
levels. At 0 lux, lake trout fed unsuccessfully—during our trials we
only had one successful capture that occurred at 0 mm (Figure 1). Lake
trout searched for prey at a reduced swimming speed compared to their
burst speed upon location of prey (Figure 2). Amphipods had a much
slower swimming speed than lake trout, and were usually unsuccessful at
avoiding capture (Figures 2, 3). The majority of attacks were located
anterior to the age-0 lake trout (Figure 4), suggesting that age-0 lake
trout relied heavily on visual detection and were not as reliant on
other sensory systems such as their lateral line while foraging.
Figure 1 Reaction distance (mm) plotted against light levels (lux) for amphipods. Error bars are 2*SE.
Figure 2 Swimming speed (mm/sec) for lake trout while searching for prey, after detecting prey (“burst”), and swimming speed of amphipods. Error bars are 2*SE.
Figure 3 The probability of location, pursuit, attack, and retention. The overall probability for these separate events occurring was 0.69. Error bars are 2*SE.
Figure 4 Reaction angles and distances of attack. Each point represents a prey item that was attacked, with the age-0 lake trout oriented vertically (shown by the dark shape in the middle of the polar plot). The majority of attacks occurred between 90º and 280º.
References
Gerritsen, J., Strickler, J., 1978. Encounter probabilities and community structure in zooplankton: a mathematical model. J. Fish. Res. Board Can. 34, 73—82.
Hedrick, Tyson L. "DLT Data Viewer 2", Digitizing and DLT in MATLAB. 2007. http://www.unc.edu/~thedrick/digitzing/
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