**ABSTRACT NOT FOR CITATION WITHOUT AUTHOR PERMISSION. The title, authors, and abstract for this completion report are provided below. For a copy of the full completion report, or with questions, please contact the GLFC via email at stp@glfc.org or via telephone at 734-662-3209.**
Effects of Low
Level Aquatic Contaminants on Lake Trout Reproduction: Implication in Lake
Trout Rehabilitation
Weiming Li1 and Christopher B. Rees1
1
Department of Fisheries and Wildlife
Michigan State University
East Lansing, MI
April 2003
ABSTRACT:
We have completed this project and anticipate
submitting in total of three manuscripts. Briefly, we developed several novel
methods to further understand and characterize the induction and function of
this gene in lake trout and other salmonids species. First, we developed the
measurement of gill CYP1A using quantitative PCR with the sampling of non-lethal
gill biopsies in both wild and cultured Atlantic salmon. This study demonstrated
that gill biopsies coupled with quantitative PCR analysis was a potentially valuable
tool in environmental assessment of wild fish populations. Second, advances in the
quantitative PCR method and instruments led us to develop a real-time quantitative
PCR assay useful for measuring CYP1A mRNA in four salmonid species; lake trout,
brook trout, rainbow trout, and Atlantic salmon. In order to obtain necessary
information for the design of a cRNA standard,
full-length CYP1A cDNA sequences were determined for two Salvelinus species,
lake trout (Salvelinus namaycush) and brook trout (Salvelinus fontinalis). Each cDNA was
found to share the same characteristics with known CYP1A sequences of Atlantic
salmon (Salmo salar)
and rainbow trout (Oncorhynchus mykiss), and shared greater than 97%
coding region sequence. The developed a CYP1A-specific real-time quantitative
PCR assay indicated that BNF treated fish showed 1.8 to 3.0 orders of magnitude
higher CYP1A than control fish in all four species studied. Finally, we examined
the effects BNF exposure had on juvenile lake trout brain tissue using a multidisciplinary
approach. Over a 32 day time-course, CYP1A mRNA induction in response to BNF
exposure occurs rapidly and continued to rise in the BNF-treated lake trout
after 4 hours, 8 hours, and 24 hours with a peak in CYP1A mRNA expression after
2 days. At each of these time periods, significantly higher levels of CYP1A
expression were found in each induced group over their respective control
groups (Tukey-Kramer, p < 0.0001). In situ hybridization study supports the
Q-RT-PCR results in that CYP1A mRNA level was universally induced in the brain
of BNF-exposed fish, and that CYP1A mRNA were mainly expressed in the
endothelia and occasionally in the neurons or glial cells. CYP1A
immunoreactivity was induced in the olfactory bulb and valvula
cerebelli of BNF-treated fish. Notably, some BNF-treated fish contained
multifocal hemorrhages in the brain tissue. These fish had overall depressed
CYP1A immunoreactivity in the brain. These results show the relationship
between transcriptional and translational effects of contaminant exposure in
the brain of juvenile lake trout and provide knowledge to the potential
physiological effects sublethal levels of
contaminants have on fish from the population level.