Forensic identification of severely degraded Atlantic salmon (Salmo salar) and rainbow trout (Oncorhynchus mykiss) tissues
© Dalvin et al; licensee BioMed Central Ltd. 2010
Received: 22 April 2010
Accepted: 3 November 2010
Published: 3 November 2010
Aquaculture is a globally important and rapidly growing industry. It contributes positively to the economy and sustainability of coastal communities, but it is not without regulatory challenges. These challenges are diverse, and may include identification of fish discarded in an illegal manner, biological discharge from fish ensilage tanks, and partially destroyed or processed tissues. Robust genetic tools are required by management authorities to address these challenges. In this paper, we describe nine species-specific primer sets amplifying very short DNA fragments within the mitochondrial DNA cytochrome c oxidase (COI) gene, which were designed to permit diagnostic identification of degraded DNA from two of the most commonly farmed salmonids in Europe and North America.
Of the nine designed primer sets, six were found to be species-specific (four Atlantic salmon, two rainbow trout), whereas the remaining three sets (two Atlantic salmon, one rainbow trout) also amplified a product from other, closely related, salmonid DNA templates. Screening of DNA templates from 11 other non-salmonid native fish species did not produce PCR products with any of the primer sets. Specific tests confirmed the ability of these markers to identify Atlantic salmon and rainbow trout tissues in treated food products, chemically treated ensilage waste and fillets left to degrade in saltwater for up to 31 days at 15°C. Importantly, these markers provided diagnostic identification in cases where other genetic methods failed because of degraded DNA quality.
Results from this study demonstrate that amplification of very short DNA fragments using species-specific primers represents a robust and versatile method to create cheap and efficient genetic tests that can be implemented in a range of forensic applications. These markers will provide fishery, aquaculture and food regulatory authorities with a method to investigate and enforce regulations within these industries.
Aquaculture is playing an increasingly important role in meeting global protein requirements. Production of domesticated rainbow trout (Oncorhynchus mykiss, Walbaum) has a long history, and takes place in a large number of countries [1, 2]. Aquaculture production of the Atlantic salmon (Salmo salar L.) was established in the 1960s, and in Europe this species represents the primary farmed fish in terms of both biomass and economic value. Norway has led this development, producing over 700,000 tons of Atlantic salmon and nearly 100,000 tons of rainbow trout in 2008 .
Aquaculture production of rainbow trout is based upon freshwater rearing or a mixture of freshwater and marine rearing, whereas production of Atlantic salmon almost exclusively involves a combination of juvenile rearing in freshwater and growing to market size in marine cages. Marine rainbow trout and Atlantic salmon farms tend to be located in sheltered coastal areas, and they contribute employment and financial opportunities to coastal communities. However, challenges remain concerning the mitigation of the negative effects of aquaculture, including genetic interactions [4, 5], pathogens  and fish-farm effluent discharge . Meeting such challenges involves, among other issues, the requirement to monitor the environmental effects and the ability to detect infringements of legislation. The latter often requires forensic investigation [8, 9].
The application of DNA methods for identifying and authenticating fish and fishery products is increasing. These molecular tests [10, 11] include a wide range of approaches of varying technical sophistication and cost, which exploit diagnostic polymorphisms within both mitochondrial (mt)DNA and nuclear (n)DNA genomes. Sequencing , restriction fragment length polymorphism  and species-specific PCR [14, 15] approaches have been successfully implemented to identify partially degraded and otherwise compromised products. In general, mtDNA targeted methods have predominated in such studies, because of the general robustness and higher cellular copy number of mtDNA compared with nDNA .
One of the major challenges related to all forms of marine aquaculture is containment. In Norway, where fish farm escapees are recorded by the Directorate of Fisheries, the yearly total of farmed escapees were as high as 921,000 in 2006 for Atlantic salmon and 315,000 in 2007 for rainbow trout. [17, 18]. Although DNA methods to identify the farm of origin have recently been developed and successfully implemented for both Atlantic salmon [8, 19] and rainbow trout , there is a need to expand the repertoire of forensic tools to assist aquaculture and fishery agencies in regulation and law enforcement. For example, diagnostic identification of severely degraded tissues resulting from dead fish dumped illegally into the sea or of potential leakage of effluent from fish decomposition tanks located on farms represent two specific cases in which Norwegian enforcement agencies have requested technical assistance for forensic identification of biological matter.
To meet the needs of authorities enforcing law in aquaculture management, the aim of this study was to establish a rapid and cost-effective DNA-based method for the diagnostic identification of severely degraded Atlantic salmon and rainbow trout tissues. We hypothesised that amplification of very short mtDNA fragments would provide identification where other molecular methods would fail. Consequently, we designed species-specific primers that amplified very short mtDNA fragments within the cytochrome c oxidase (COI) gene [21, 22]. Identifications using these markers were then compared in degradation tests with alternative molecular methods including mtDNA sequencing and fragment analysis of short tandem repeat nuclear loci.
Species specificity of primer sets
Overview of PCR amplification product in salmonids using the short fragment COI primer sets.
When tested against a panel of additional species DNAs (herring, redfish, tusk, cod, coalfish, pollock, plaice, monkfish, haddock, Atlantic halibut, mackerel), no specific PCR products were observed for any of the nine short fragment primer sets designed to salmonid COI genes.
PCR amplification of decayed and processed DNA samples
Summary of PCR amplifications using a range of primers and DNA templates of varying quality.
Short fragment COI
O. mykiss -specific
S. salar -specific
Canned salmon fillet
PCR amplification of the unknown sea sample
PCR using primers specific to Atlantic salmon and rainbow trout revealed no amplification of products in any of the eight DNA isolates taken from the sea sample. Amplicons were generated using the barcoding COI primers in three of the eight DNA extracts but subsequent cloning and sequencing revealed multiple COI sequences having much greater similarity to other organisms, including brown seaweed (Scytosiphon lomentaria) and goldsinny wrasse (Ctenolabrus rupestris). With the latter result indicating that amplifiable template DNA was present within the sea sample, it is unlikely that it originated from either Atlantic salmon or rainbow trout carcases.
Illegal, unreported and unregulated fishing represents a major threat to the sustainable exploitation of the world's marine resources . Consequently, the application of molecular genetic tools in the management of fisheries, aquaculture and wildlife resources in general is gaining global importance. This study reports the successful development of diagnostic markers for Atlantic salmon and rainbow trout, which permitted the amplification of severely degraded DNA obtained from canned fish products, ensilage and heavily decayed fish tissue. These markers will provide management authorities with a tool to increase enforcement in a range of forensic applications.
The primers developed in this study were demonstrated to enable reliable species-specific identification under a range of amplification temperatures and on a range of degraded DNA templates likely to be available for forensic investigation. Although the species comparisons were not exhaustive, the fact that six of the primer sets did not amplify products from other high-quality salmonid template DNA indicates the likely overall robustness of the assays. However, it is not possible to exclude the possibility that false positive amplifications for individual primer sets may occur occasionally from DNA of species not assayed in the current study. It would be prudent, therefore, to assay multiple primer sets for identification purposes and to make a positive assignment only when data from all markers are consistent. The practicality of undertaking multiple PCR assays is aided by the fact that all nine primer sets share identical cycling parameters.
Examples of molecular genetics tools applied to fish and fisheries-related challenges are highly diverse, including competition fraud , identification of farm of origin of escapees, , illegal harvesting  and mixed stock fisheries . Many of these applications relate to population identifications, which often exploit a combination of private and allele frequency differences observed in highly polymorphic markers, which are tested by a variety of statistical approaches . However, although similar approaches have been used for species identification , identification of processed food products containing fish most often relies upon the analysis of diagnostic molecular markers not requiring statistical treatment [10, 11]. With the increase in interest in fish barcoding , the availability of sequence data within the COI gene will provide the opportunity for further development of species-specific markers. Although it is acknowledged that sequencing of the COI gene can produce species identification in many cases, as reported here, species-specific amplification of short DNA fragments will provide an alternative viable and technologically simple approach for severely degraded tissues contaminated with other biological material. Similarly, PCR-based techniques exploiting amplification of short mtDNA has also been applied successfully to human forensics for identification of degraded samples .
There was no obvious qualitative difference in product yield from templates degraded in seawater from 3 to 31 days, or from ensilaged or processed foods. This is testament to the resilience of mtDNA to degradation, and also suggests that the primer sets could still prove to be informative for even more severely degraded material. The inability to detect Atlantic salmon or rainbow trout in the sea sample with the species-specific primers developed here indicates that the sea sample did not include significant amounts of DNA from either of these species. As this sample was taken in the vicinity of both rainbow trout and Atlantic salmon farms and an aquaculture fish processing factory, this result demonstrates that, unlike amplification with the barcoding primers and clone sequencing, these primer sets do not easily pick up false positives from sampling in the proximity of these operations or from other contaminating DNA present in the sample.
Use of the primer sets reported here can also be extended beyond forensic purposes. The brown trout is the closest relative to the Atlantic salmon, and these species occur sympatrically in the wild. Several studies have documented hybridisation between these two species, which has been identified by a variety of molecular techniques [31–34]. The fact that four of the Atlantic salmon specific markers developed here were able to distinguish between these two species means that these primers can be used to make a preliminary identification (as a pre-screening technique) of maternal contribution to a suspected hybrid using relatively simple technology before a more technologically demanding approach such as sequencing is undertaken.
The present study was designed to establish a rapid and robust PCR-based assay to perform diagnostic identification of severely degraded Atlantic salmon and rainbow trout tissues. We hypothesised that amplification of very short mtDNA fragments using species-specific primers located in the COI gene would provide amplification where other molecular techniques would be inadequate. Both the species-specificity of these markers and importantly, their superiority in performing identifications on severely degraded DNA compared with alternative methods was demonstrated.
We conclude that these markers can be applied to a range of forensic applications, and will provide management authorities with a useful technique for regulation enforcement.
Study strategy and design of diagnostic PCR assays
The aim of this study was to establish a straightforward diagnostic PCR protocol for unambiguous identification of severely decomposed Atlantic salmon and rainbow trout tissues. This would preferably comprise simple amplification and gel visualisation steps without recourse to additional procedures such as sequencing or post PCR restriction analysis. An mtDNA-based assay was considered to be appropriate, with attention focused on the extensively characterised ~650 bp DNA barcoding fragment of the COI gene . Primers were specifically designed to amplify very small fragments (~ 50-75 bp) within this region, to maximise the probability of amplifying severely fragmented template DNA. Potential species-specific primer sets were then tested for specificity and robustness on a range of common fish and on tissues from the target species, which had been subject to various treatments including degradation in salt water, ensilage and food processing.
Overview of PCR primer sets used in this study
Sequence 5" to 3"
Short fragment COI primers
Barcoding COI primers b
285 to 375e
250 to 350e
Three additional primer sets were used as comparators for successful PCR amplification from rainbow trout and Atlantic salmon DNA samples. These were a standard COI barcoding primer set (Fish 1) that works effectively for salmonids and two microsatellite markers, Atlantic salmon specific Sp2201 and rainbow trout specific OMM1303, which are routinely used in the Institute of Marine Research laboratory. Details of these primers, including expected amplicon sizes, are given in Table 3.
Samples and DNA extraction
Canned Atlantic salmon fillet and pâté (Stabburet, Norway) and frozen Atlantic salmon and rainbow trout fillets, complete with skin, were purchased in a local supermarket. To test the ability of the primers to amplify degraded tissues, the frozen Atlantic salmon and rainbow trout fillets were kept in fish tanks containing running seawater at 15°C. Samples of these fillets were then taken at 3, 5, 7, 10, 13, 17, 21, 24, 28 and 31 days after placing them into the tanks. A sample of ensilage waste of Atlantic salmon was collected from an experimental research farm (Matre Field Station, Matre, Norway). This ensilage tank contained remains of dead Atlantic salmon mixed with sodium hydroxide. Such tanks are commonplace on commercial farms for temporary storage of dead fish before transport to factories for processing.
To test the specificity of the designed primers, a range of native fish species were also examined. Most of these were purchased from a local fish retailer, and comprised herring (Clupea harengus), redfish (Sebastes marinus), tusk (Brosme brosme), cod (Gadus morhua), coalfish (Pollachius virens), pollock (Pollachius pollachius), plaice (Pleuronectes platessa), monkfish (Lophius piscatorius), haddock (Melanogrammus aeglefinus), Atlantic halibut (Hippoglossus hippoglossus) and mackerel (Scomber scombrus). Samples of DNA from three other salmonid species (brown trout (Salmo trutta), Arctic charr (Salvelinus alpinus) and whitefish (Coregonus laveratus)) were available from laboratory archives.
Finally, a 2 litre sample of unidentified floating biological material mixed with sea water was collected from an undisclosed coastal location in Norway. This sample, herein referred to as the 'sea sample', was taken in the summer of 2008 in the vicinity (<1 km) of a commercial Atlantic salmon farm and a factory that processes fish waste from aquaculture installations. The legal authorities were interested as to whether the sample could be related to biological discharge from either nearby operation.
DNA was extracted from fish fins or from a mixture of skin and muscle from the rainbow trout and Atlantic salmon samples that had been exposed to a variety of treatments (described above). For the sea sample, DNA was extracted from a homogenised mixture of the seawater and floating biological matter sample. For all samples, DNA was extracted using a commercially available column purification protocol (DNAeasy Kit, Qiagen, Valencia, CA, USA). DNA was quantified spectrophotometrically (Nanodrop ND-1000; Thermo Scientific, Wilmington, DE, USA). Except for tissues exposed to degradation, DNA was extracted from a minimum of two individuals in separate isolations. For the canned food samples (potentially containing tissue from multiple individuals) two separate DNA extractions from each can were performed. Eight separate DNA extractions were performed on the homogenised sea sample mixture.
Each short fragment COI gene PCR reaction (25 μL total volume) contained ~25 ng DNA, 5 μL GoTaq® buffer, 2.5 mM MgCl2, 200 μM each dNTP, 0.25 μM each primer and 0.15 U Taq polymerase (GoTaq®, Promega Corp., Fitchburg, WI, USA). DNA was amplified in a thermal cycler (Mastercycler epgradient S; Eppendorf, Hamburg, Germany) using the following cycling conditions: initial denaturation at 94°C for 2 min, followed by 30 cycles of denaturation at 94°C for 30 seconds, 62°C for 30 seconds and extension at 72° for 30 seconds, then a final extension at 72°C for 10 minutes. To examine the robustness of this temperature profile for each assay, PCR reactions were then repeated with annealing temperatures 2°C above and 5°C below the selected optimum. Positive and negative controls (no template) were used throughout. The Fish1, the Ssp2201 and the Omm1303 primer sets used the same conditions, but with an annealing temperature of 55°C.
Where amplicon verification was required, fragments were either cloned (TOPO TA Cloning Kit; Invitrogen Corp., Carlsbad, CA, USA) before sequencing, or purified (ExoSAP-IT; Affymetrix-USB, Cleveland, OH, USA) and sequenced directly on an automated sequencer (ABI 3700 with BigDye 3.1 sequencing reagents; Applied Biosystems, Foster City, CA, USA).
This study was funded by the Norwegian Department of Fisheries and Institute of Marine research
- Gall GAE, Crandell PA: The rainbow trout. Aquaculture. 1992, 100: 1-10. 10.1016/0044-8486(92)90333-G.View ArticleGoogle Scholar
- Maccrimmon HR: World distribution of rainbow trout (Salmo gairdneri). J Fish Resh Board Can. 1971, 28: 663-704.View ArticleGoogle Scholar
- Directorate of Fisheries: Key Figures from Aquaculture Industry. 2008, Bergen: Directorate of Fisheries, NorwayGoogle Scholar
- Clifford SL, McGinnity P, Ferguson A: Genetic changes in an Atlantic salmon population resulting from escaped juvenile farm salmon. J Fish Biol. 1998, 52: 118-127. 10.1111/j.1095-8649.1998.tb01557.x.View ArticleGoogle Scholar
- Crozier WW: Evidence of genetic interaction between escaped farmed salmon and wild Atlantic salmon (Salmo salar L) in a Northern Irish river. Aquaculture. 1993, 113: 19-29. 10.1016/0044-8486(93)90337-X.View ArticleGoogle Scholar
- Krkosek M, Gottesfeld A, Proctor B, Rolston D, Carr-Harris C, Lewis MA: Effects of host migration, diversity and aquaculture on sea lice threats to Pacific salmon populations. Proc Biol Sci. 2007, 274: 3141-3149. 10.1098/rspb.2007.1122.PubMed CentralView ArticlePubMedGoogle Scholar
- Brigolin D, Pastres R, Nickell TD, Cromey CJ, Aguilera DR, Regnier P: Modelling the impact of aquaculture on early diagenetic processes in sea loch sediments. Mar Ecol Prog Ser. 2009, 388: 63-80. 10.3354/meps08072.View ArticleGoogle Scholar
- Glover KA, Skilbrei OT, Skaala O: Genetic assignment identifies farm of origin for Atlantic salmon Salmo salar escapees in a Norwegian fjord. ICES J Mar Sci. 2008, 65: 912-920. 10.1093/icesjms/fsn056.View ArticleGoogle Scholar
- Waldman JR, Doukakis P, Wirgin I: Molecular analysis as a conservation tool for monitoring the trade of North American sturgeons and paddlefish. J Appl Ichthyol. 2008, 24: 20-28. 10.1111/j.1439-0426.2008.01086.x.View ArticleGoogle Scholar
- Gil LA: PCR-based methods for fish and fishery products authentication. Trends Food Sci Technol. 2007, 18: 558-566. 10.1016/j.tifs.2007.04.016.View ArticleGoogle Scholar
- Rasmussen RS, Morrissey MT: DNA-based methods for the identification of commercial fish and seafood species. Compr Rev Food Sci Food Saf. 2008, 7: 280-295. 10.1111/j.1541-4337.2008.00046.x.View ArticleGoogle Scholar
- Hsieh HS, Chai T, Cheng CA, Hsieh YW, Hwang DF: Application of DNA technique for identifying the species of different processed products of swordfish meat. J Food Sci. 2004, 69: C1-C6. 10.1111/j.1365-2621.2004.tb17847.x.View ArticleGoogle Scholar
- Carrera E, Garcia T, Cespedes A, Gonzalez I, Fernandez A, Asensio LM, Hernandez PE, Martin R: Identification of smoked Atlantic salmon (Salmo salar) and rainbow trout (Onchorhynchus mykiss) using PCR-restriction fragment length polymorphism of the p53 gene. J AOAC Intl. 2000, 83: 341-346.Google Scholar
- Abercrombie DL, Clarke SC, Shivji MS: Global-scale genetic identification of hammerhead sharks: Application to assessment of the international fin trade and law enforcement. Cons Gens. 2005, 6: 775-788. 10.1007/s10592-005-9036-2.View ArticleGoogle Scholar
- Lee JCI, Tsai LC, Liao SP, Linacre A, Hsieh HM: Species identification using the cytochrome b gene of commercial turtle shells. Forensic Sci Int Genet. 2009, 3: 67-73. 10.1016/j.fsigen.2008.10.005.View ArticlePubMedGoogle Scholar
- Mackie IM, Pryde SE, Gonzales-Sotelo C, Medina I, Perez-Martin R, Quinteiro J, Rey-Mendez M, Rehbein H: Challenges in the identification of species of canned fish. TrendsFood Sci Technol. 1999, 10: 9-14. 10.1016/S0924-2244(99)00013-8.View ArticleGoogle Scholar
- Directorate of Fisheries: Key Figures from Aquaculture Industry. 2006, Bergen: Directorate of Fisheries, NorwayGoogle Scholar
- Directorate of Fisheries: Key Figures from Aquaculture Industry. 2007, Bergen: Directorate of Fisheries, NorwayGoogle Scholar
- Glover KA, Hansen MM, Skaala O: Identifying the source of farmed escaped Atlantic salmon (Salmo salar): Bayesian clustering analysis increases accuracy of assignment. Aquaculture. 2009, 290: 37-46. 10.1016/j.aquaculture.2009.01.034.View ArticleGoogle Scholar
- Glover KA: Genetic characterisation of farmed rainbow trout in Norway: intra- and inter-strain variation reveals potential for identification of escapees. BMC Genet. 2008, 9: 87-10.1186/1471-2156-9-87.PubMed CentralView ArticlePubMedGoogle Scholar
- Hebert PD, Cywinska A, Ball SL, deWaard JR: Biological identifications through DNA barcodes. Proc Biol Sci. 2003, 270: 313-321. 10.1098/rspb.2002.2218.PubMed CentralView ArticlePubMedGoogle Scholar
- Hebert PD, Gregory TR: The promise of DNA barcoding for taxonomy. Syst Biol. 2005, 54: 852-859. 10.1080/10635150500354886.View ArticlePubMedGoogle Scholar
- Ogden R: Fisheries forensics: the use of DNA tools for improving compliance, traceability and enforcement in the fishing industry. Fish Fish. 2008, 9: 462-472.View ArticleGoogle Scholar
- Primmer CR, Koskinen MT, Piironen J: The one that did not get away: individual assignment using microsatellite data detects a case of fishing competition fraud. Proc R Soc Ser B Biol Sci. 2000, 267: 1699-1704. 10.1098/rspb.2000.1197.View ArticleGoogle Scholar
- Withler RE, Candy JR, Beacham TD, Miller KM: Forensic DNA analysis of Pacific salmonid samples for species and stock identification. Environ Biol Fish. 2004, 69: 275-285. 10.1023/B:EBFI.0000022901.26754.0b.View ArticleGoogle Scholar
- Beacham TD, Lapointe M, Candy JR, Miller KM, Withler RE: DNA in action: Rapid application of DNA variation to sockeye salmon fisheries management. Cons Genet. 2004, 5: 411-416. 10.1023/B:COGE.0000031140.41379.73.View ArticleGoogle Scholar
- Hansen MM, Kenchington E, Nielsen EE: Assigning individual fish to populations using microsatellite DNA markers. Fish Fish. 2001, 2: 93-112.View ArticleGoogle Scholar
- Mccusker MR, Paterson IG, Bentzen P: Microsatellite markers discriminate three species of North Atlantic wolffishes (Anarhichas spp.). J Fish Biol. 2008, 72: 375-385. 10.1111/j.1095-8649.2007.01701.x.View ArticleGoogle Scholar
- Fish Barcode of Life Initiative. [http://www.fishbol.org/]
- Eichmann C, Parson W: 'Mitominis': multiplex PCR analysis of reduced size amplicons for compound sequence analysis of the entire mtDNA control region in highly degraded samples. Int J Legal Med. 2008, 122: 385-388. 10.1007/s00414-008-0227-5.View ArticlePubMedGoogle Scholar
- Beland KF, Roberts RL, Saunders RL: Evidence of Salmo-Salar X Salmo-Trutta Hybridization in a North-American River. Can J Fish Aquat Sci. 1981, 38: 552-554. 10.1139/f81-078.View ArticleGoogle Scholar
- Jansson H, Ost T: Hybridization between Atlantic salmon (Salmo salar) and brown trout (S-trutta) in a restored section of the River Dalalven, Sweden. Canadian J Fish Aquat Sci. 1997, 54: 2033-2039. 10.1139/cjfas-54-9-2033.View ArticleGoogle Scholar
- Jordan WC, Verspoor E: Incidence of natural hybrids between Atlantic salmon, Salmo salar L., and brown trout, Salmo trutta L., in Britain. Aquacult Fish Manage. 1993, 24: 373-377.Google Scholar
- Matthews MA, Poole WR, Thompson CE, McKillen J, Ferguson A, Hindar K, Wheelan KF: Incidence of hybridization between Atlantic salmon, Salmo salar L., and brown trout, Salmo trutta L., in Ireland. Fish Manage Ecoly. 2000, 7: 337-347. 10.1046/j.1365-2400.2000.00208.x.View ArticleGoogle Scholar
- Ward RD, Hanner R, Hebert PDN: The campaign to DNA barcode all fishes, FISH-BOL. J Fish Biol. 2009, 74: 329-356. 10.1111/j.1095-8649.2008.02080.x.View ArticlePubMedGoogle Scholar
- Hall TA: BioEdit: A user-friendly biological sequence alignment editor and analysis program for Windows 95/98/NT. Nucl Acids Symp Ser. 1999, 41: 95-98.Google Scholar
- Ward RD, Zemlak TS, Innes BH, Last PR, Hebert PDN: DNA barcoding Australia's fish species. Philosl Trans R Soc Ser B Biol Sci. 2005, 360: 1847-1857. 10.1098/rstb.2005.1716.View ArticleGoogle Scholar
- Paterson S, Piertney SB, Knox D, Gilbey J, Verspoor E: Characterization and PCR multiplexing of novel highly variable tetranucleotide Atlantic salmon (Salmo salar L.) microsatellites. Mol Ecol Notes. 2004, 4: 160-162. 10.1111/j.1471-8286.2004.00598.x.View ArticleGoogle Scholar
- Palti Y, Fincham MR, Rexroad CE: Characterization of 38 polymorphic microsatellite markers for rainbow trout (Oncorhynchus mykiss). Mol Ecol Notes. 2002, 2: 449-452. 10.1046/j.1471-8286.2002.00274.x.View ArticleGoogle Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.