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Genetic Analysis of Salmonids and Other Fishes
in the Western US

The Problem

Bridgecreek a tributary of the Stehekin river.
Bridgecreek a tributary of the Stehekin river.

As salmonid populations continue to decline in the western US, it is imperative to develop a better understanding of ecological, genetic, and biological aspects of these species. Over the last 10 years, molecular tools have been used to nonlethally characterize salmonid populations. While this has provided invaluable information to resource managers, there is still a need to develop nonlethal genetic diagnostic systems to discriminate life histories, hybridization, and gender in salmonids. This will allow for the design of management strategies involving water allocation, supplementation, harvesting, and habitat usage that will ensure their continued survival.

Objectives

Within the broad context of the Fisheries and Aquatic Resources Program the 5-year research goals address: development of non-lethal genetic procedures for identification of gender, populations, phylogeographic, and taxonomic relationships for western fish; and conservation genetics of rare and endangered species. The genetic systems generated from this research address broad goals to characterize salmonid genetic diversity and more specific objectives to: (1) help ensure that hatchery practices do not contribute to the decline of salmonids due to the generation of inferior genetic products; (2) allow for the monitoring of the movement of juveniles from endangered runs for better management of water allocations and to obtain more complete life history information; (3) ensure equal sex ratios are collected when take limits are imposed for listed species; and (4) determine if temporal and/or spatial aspects of salmonid genetics within and between river systems require modifications in management strategies.

Methodology

To aid in the understanding of both returning adults and outmigrating juveniles, four aspects of salmonid genetics are being pursed: (1) assessment of temporal and spatial aspects of genetic diversity in wild and hatchery populations; (2) development of genetic markers to discriminate runs
Coastal cutthroat trout from an Olympic peninsula stream.
Coastal cutthroat trout from an Olympic peninsula stream.
and populations; (3) development of genetic markers to discriminate sex; (4) development of genetic markers to assess cross-species hybridization. This subtask was initiated with the non-lethal collection of tissue samples from distinct populations of wild and hatchery chinook salmon (Oncorhynchus tshawytscha) throughout the western US. A DNA extraction protocol was developed to efficiently extract high quality DNA from small tissue samples. The DNA obtained from a fin clip was determined to be sufficient for hundreds of genetic analyses and is of sufficient quality for molecular studies. The DNA is analyzed by genetic fingerprint analysis using single oligonucleotide primers and the Polymerase Chain Reaction (PCR). This technique is designated arbitrarily primed-PCR (apPCR) and the fingerprints generated from each primer are very similar (80-100%) within a species and very different (0-30%) between species. This allows for rapid species discrimination and the identification of genetic polymorphisms to define specific genotypes and the level of genetic diversity within species. All of
Rainbow trout smolt from an Olympic peninsula stream.
Rainbow trout smolt from an Olympic peninsula stream.
the populations will be assessed for the levels of genetic diversity and screened for population, sex, and run specific markers. The second phase of this study involves the isolation and cloning of apPCR amplified polymorphic markers and subsequent sequence analysis of the cloned products. Primers will then be constructed from the sequence at each end of the products so dual-primer PCR (dpPCR) can be performed--which is 100 times more sensitive than apPCR. In addition, dpPCR is faster and easier to perform so results can be obtained in a time frame to assist with the real time management of this species. This same strategy will also be used to address several management concerns about steelhead (Oncorhynchus mykiss), cutthroat trout (Oncorhynchus clarki), char (Salvelinus spp.), and white sturgeon (Acipenser transmontanus) populations. As markers are identified and PCR primers designed, the systems will be made available to management agencies so they can monitor genetic aspects of local populations.

Highlights and Key Findings

Three non-lethal genetic diagnostic systems have been developed that discriminate spring and fall chinook in the Columbia/Snake river system, gender of chinook salmon, and hybridization between cutthroat and rainbow trout. In addition, we have identified genetic markers that discriminate populations of steelhead trout and char from several rivers of the Kamchatka peninsula in Russia. All of these systems are currently being used in field studies and have resulted in manuscripts that are currently being reviewed for publication in scientific journals. These diagnostic systems are based on the Polymerase Chain Reaction (PCR) so non-lethal samples can be collected and
Westslope cutthroat from the Stehekin river.
Westslope cutthroat from the Stehekin river.
analyzed. The markers were first identified by single primer PCR and discriminating products cloned and sequenced. Primers were then constructed to the terminal sequences of the products so more rapid and dependable dual primer PCR could be performed. This approach has allowed us to identify novel genetic markers that discriminate life histories, gender, and closely related species. We have also used these markers to characterize genotype patterns between hatchery and wild fish from the same river system. Currently, we are using 24 species-specific markers to determine the occurrence of hybridization between introduced rainbow trout and native subspecies of cutthroat trout in several drainages in the western US. This genetic system allows us to visualize hybrids to the 4th generation backcross. Hybrid distribution patterns will be correlated with water chemistry and temperatures to determine if abiotic factors effect hybrid distribution and if management strategies can be designed to recover pure populations.

Where Are We Headed In 2003

We will pursue three aspects of this system over the next year: complete the development of species-specific molecular markers; complete the third year of hybridization analysis on populations of introduced non-native rainbow and native cutthroat trout that have overlapping habitat; and identify streams that have native rainbow and native cutthroat trout to determine levels of hybridization in populations that have not experienced any introductions. To complete the molecular genetic system, mitochondrial markers will be developed that are species-specific. This will involve generating consensus DNA sequence from regions of the mitochondria and developing species-specific PCR primers to amplify those regions.

All of the species-specific markers will be applied to trout populations in select streams on the Olympic peninsula and North Cascades National Park, both locations have rainbow and cutthroat trout occupying overlapping habitat (all of these streams have had hatchery raised non-native rainbow trout planted on top of native cutthroat trout). This will be the third year of a study to determine how hybridization frequencies change over time and space. This year we will analyze juveniles as well as adults to determine where hybrids are reproducing and how genomic content is reflected in animal behavior. These data will be compiled for publication in a peer-reviewed scientific manuscript and used to determine if management strategies can be generated to recover the pure cutthroat populations.

In order to determine the full impacts of hybridization on cutthroat populations it is necessary to determine if hybridization occurs between native populations of these species that have overlapping habitat. There are a limited number of river/stream systems in the contiguous western U.S. that may have these populations. Each year of this project we will analyze populations in one or two new systems. The proposed systems for 2003 are the John Day river in Oregon and the Chilliwack river in North Cascades National Park.

Project Contact

Rusty Rodriguez
U.S. Geological Survey
Western Fisheries Research Center
6505 NE 65th St.
Seattle, WA 98115

Email: rusty_rodriguez@usgs.gov
Phone: 206-526-6282
Fax: 206-526-6654

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