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versión On-line ISSN 0718-1957
Rev. biol. mar. oceanogr. v.43 n.3 Valparaíso dic. 2008
Revista de Biología Marina y Oceanografía 43(3): 669-674, diciembre de 2008
NOTAS CIENTÍFICASNaturalized Chinook salmon in the northern Chilean Patagonia: Do they originate from salmon farming?
Salmones Chinook asilvestrados en el norte de la Patagonia chilena: ¿se originan desde escapes de cultivo?
Marcela P. Astorga1, Cynthia Valenzuela1, Iván Arismendi2,3 and José L. Iriarte1,3
1Instituto de Acuicultura & CIEN Austral. Universidad Austral de Chile. Campus Puerto Montt. Casilla 1327 Puerto Montt, Chile
En los ríos del sur de Chile se han registrado individuos desovantes de salmón Chinook (Oncorhynchus tschawytscha). Esta especie fue introducida a partir del 1900 hasta los 80' y se cultiva actualmente en el mar. Nuestro objetivo fue identificar la procedencia de los salmones Chinook asilvestrados en el río Petrohué, mediante el uso de 3 loci microsatélites. Los resultados fueron comparados con muestras de individuos obtenidos desde cultivo. Los resultados mostraron mayor variabilidad genética en los individuos asilvestrados que la obtenida en los individuos de cultivo y además se observó divergencia genética entre ellos, lo que permite indicar que las poblaciones de salmones desovantes en el río Petrohué actualmente no son explicadas por posibles escapes desde los grupos de salmones de cultivo, sino más bien corresponderían a poblaciones generadas desde los grupos liberados con fines de repoblamiento antes del comienzo de su cultivo.
Palabras clave: Asilvestrados, naturalizados, Chile, Oncorhynchus tschawytscha, cultivo
Salmonids have been introduced into the rivers and lakes of southern South America since the 1900's, principally for recreational fishing purposes (Golusda 1907, Basulto 2003, Pascual & Ciancio 2007). Introduction of Chinook salmon (Oncorhynchus tschawytscha Walbaum) to southern Chile (between 38.7°S and 54.7°S) occurred in five stocking events during the 1970's with the planting of both eggs and alevins from Washington State, U.S.A. (Joyner 1980, Dufflocq 1981, Donaldson & Joyner 1983, Basulto 2003, Pascual & Ciancio 2007), but these initial introductions were described as failures (Basulto 2003). More recently, since the 1980's, there has been a development in intense salmon farming between 40.7°S and 53°S, with Chinook salmon constituting less than 5% of total Chilean farmed fish production (SERNAPESCA 2006). At present, mature salmon have been detected, in Chile, returning to the rivers Pratt (Basulto 2003), Futaleufu (Di Prinzio 2001), and Petrohué (Soto et al. 2006, 2007), and in the Argentinean Patagonia (Di Prinzio 2001, Pascual & Ciancio 2007, Becker et al. 2007). The Petrohué River is of great relevance because it is the only site with documented Chinook salmon spawning sites and juveniles (Soto et al. 2006, 2007). However, it is not clear whether these returning individuals have escaped from farming net pens or are descendents of the first individuals introduced for ranching in the 1970's. Thus, this study genetically compares the spawning Chinook salmon populations in Petrohué River with those from known salmon farming sites to determine whether or not they originated from escaped individuals.
MATERIAL AND METHODS
Obtaining the samples
Naturalized specimens were collected from March to April 2006 in the Laguna de Los Patos sector of the Petrohué River basin (41°S, 79ºW) (Fig. 1). Three campaigns were carried out in which 20 spawning Chinook carcasses were captured using backpack electrofishing. Samples were taken from a total of 22 individuals from a farming site on Río Negro-Hornopirén (41.4°S, 72.5°W) in May 2006. This is the only company which raises Chinook salmon in Chile and they have been cultivating this species since 1985 with the same strain of fish. Samples of scales, fins, and muscles of each individual were taken and stored in 1.5-mL tubes with 95% ethanol.
Figure 1. Map of the sampling sites for naturalized (Petrohué) (41°S, 79ºW) and farmed (Hornopirén) (41.4°S, 72.5°W) individuals of Chinook salmon O. tschawytscha
DNA was extracted from the fin and scale samples using Proteinase K-Chelex at 10% (Estoup et al. 1996). Muscle samples were extracted using the standard method for DNA extraction with phenol-chloroform-isoamylic alcohol followed by precipitation in ethanol. Genotypification was performed on three microsatellites (Ots-9, Ots-10, Oneµ-13) under the conditions described in Greig & Banks (1999). These were then read as a multiplex in an automatic sequencer (ABIPrism 3100).
Genetic variability indicators were estimated for each group of individuals, namely observed and expected heterozygosity, average number of alleles per locus, and allelic frequency. The fit to the Hardy-Weinberg equilibrium model was evaluated with the Fisher's exact test using the program GENEPOP v3.1 (Raymond & Rousset 1995). Genotypic disequilibrium values were estimated for comparison of mixed origins between samples. In order to establish the probability that each individual would be assigned to a population, an assignment test was performed using the program GeneClass (Cournet et al. 1999). The presence of some population bottleneck process was estimated with the Wilcoxon sign rank test using the program Bottleneck v1.2.02 (Piry et al. 1999). The genetic differentiation of the population was evaluated using allelic distribution at different loci through a Fisher's exact test and with Fst values for each locus.
On average, the 3 loci analyzed in Chinook salmon had 5.3 alleles per locus (Table 1). This value was higher for the naturalized spawning specimens (N = 4.6, Median = 5) than for the farmed juveniles (N = 3.6, Median = 3). However, these differences were not significant (Mann-Whitney U test Z = -1.178; P = 0.238). Oneµ-13 had the greatest number of alleles (6 alleles) in both groups (naturalized, farmed), followed by Ots-9 and Ots-10 (5 alleles each). The number of alleles per locus differed with the naturalized salmon having 5 alleles and the farmed specimens 3 alleles at Ots-9 and Ots-10 and the naturalized samples showing 4 alleles and the farmed fish 5 alleles at Oneµ-13. Moreover, the three loci contained alleles that were not shared; these unique alleles are observed in Table 1. The observed heterozygosity value (Ho) for the combined groups of Chinook salmon was 0.611 ± 0.109, with the naturalized fish presenting a significantly larger value (Ho = 0.699 ± 0.052, Median = 0.70) than the farmed fish (Ho = 0.524 ± 0.061, Median = 0.55) (Mann-Whitney U test Z = -1.963; P = 0.049). The observed and expected heterozygosity values within each group were similar. Most loci fit Hardy-Weinberg equilibrium (Table 2), with the exception of the farmed fish Oneµ-13 sample. When both groups were included, a global fit to the Hardy-Weinberg equilibrium was observed (Fisher = 14.0; P = 0.300). The allelic frequencies showed the same common allele for both groups at the three loci (Table 2). However a high presence of unique alleles was observed for both groups. The naturalized salmon had more unique alleles (4 alleles, 25%) than did the farmed fish (2 alleles, 12.5%). The endogamy index (Fis) was slightly greater in the farmed individuals (Fis = 0.0457) than in the naturalized samples (Fis = -0.0491), which had negative values. Nonetheless, the differences were not significant (Mann-Whitney U test Z = 1.091; P = 0.275). The genotypic disequilibrium values did not show significant differences for each locus and each kind of sample (0.324 < P < 0.818), therefore the mixing of origins between samples was rejected.
Table 1. Number of alleles per locus for naturalized and farmed Chinook salmon with total values, loci mean and sample
Table 2. Allelic frequency of the three microsatellite loci used. The number of individuals analyzed (N), Hardy-Weinberg equilibrium fit (PHW), and coefficient of endogamy (Fis) are indicated for the farmed and naturalized Chinook salmon samples
The assignment analysis (Fig. 2) indicated that 76.2% of the individuals were correctly classified in their group of origin, with 75% assigned correctly to the naturalized salmon and 77% to the farmed fish. Only between 5% and 3% could be assigned to either of the two origins. The assignment of the individuals based on their multi-locus genotypes showed few individuals distributed close to and around the diagonal and low likelihood values. This allowed the specimens, for the most part, to be assigned to their groups of origin. The bottleneck analysis performed on the naturalized group did not reveal significant values (P = 0.125). Some population reductions were observed, but these were not significant.
Figure 2. Assignment test based on the individual multi-locus genotype of naturalized and farmed Chinook salmon
Finally, the global analysis of genetic heterogeneity revealed a medium Fst value (0.057), thereby establishing a genetic differentiation between the naturalized and farmed individuals. A significant genetic divergence was also found (Fisher, P = 0.001) based on the allelic distribution between both analyzed salmon groups (Table 3), explained mainly by the Ots-9 locus.
Table 3. Genetic differentiation and Fst values for naturalized and farmed Chinook salmon individuals, O. tschawytscha indicating the value of probability (P) and Standard Error (SE)
Our results for naturalized and farmed Chinook salmon are genetically divergent and the naturalized population has a higher percentage of unique alleles than the farmed population does. Thus, the farmed population cannot be genetically linked to the naturalized population and so the fish sampled in the river could not have originated from the farmed sampled population. The genotypic disequilibrium analysis, which is used to determine mixed origins, is not mixed and, therefore, the absence suggests that probably the naturalized populations are not individuals which escaped from current salmon farming sites. Future studies should look into the genetic composition of salmon in other rivers of the Chilean Patagonia where releases have been described as being successful (Di Prinzio 2001, Soto et al. 2006, 2007) to construct a history of the colonization process of this species in the rivers of southern Chile.
This work provides the first record of genetic diversity levels for introduced Chinook salmon in Chile's rivers. Genetic variability (more alleles, higher heterozygosity) was greater in the group of naturalized individuals than farmed individuals, which coincides with results obtained for natural Chinook populations of in the northern Hemisphere (Banks et al. 2000, Heath et al. 2002, Williamson & May 2005) in which high genetic variability was detected through either follow-up of genetic variation over time (Williamson & May 2005), an association with reproductive characters (Heath et al. 2002), or the genetic characterization of natural populations (Banks et al. 2000). The number of alleles observed per locus was similar to that yielded in the same loci for Chinook in California, where Ots-10 had between 2 and 5 alleles and Oneµ-13 had 5 alleles (Banks et al. 1999, 2000). However, Ots-9 has been reported to have 3 alleles per locus (Banks et al. 1999, 2000), which is similar to our results for farmed individuals, but different from the naturalized population, which presents 5 alleles. Local biological processes of differentiation (differential selection), which have been taking place in the naturalized populations since their settlement in Chilean waters, may explain this slight differentiation. The Chinook individuals found in the fish farming sites may have been artificially selected for certain characteristics which yielded in a lower number of alleles from bottlenecking.
In addition, the observation of a greater number of alleles in this `founded' Chilean population in relation to the populations of the northern Hemisphere may be due to: a) multiple population events with individuals from various populations (Holland 2001, Kolbe et al. 2004, Therriault et al. 2005); b) differential selection processes between the habitats of both hemispheres (Lemaire et al. 2000, Lee 2002, Therriault et al. 2005); and c) mixing of individuals between those originating in the naturalized population and recent escapees from platform-cages. The assignation values at each site of origin, which indicate a tendency to segregation and, therefore, a genetic divergence between the two samples, revealed that only 3 to 5% of the individuals can be assigned to either of the two origins, suggesting the low possibility that the naturalized population originated from escaped individuals. Given the high variability values, these populations are highly adapted to the new colonized environment. Future studies are planned that will help us understand the colonization of this or other introduced species in the rivers of the Chilean Patagonia by evaluating more loci and their variation over time.
This is a contribution of the Forest Ecosystem Services to aquatic systems under climatic variability scenarios (FORECOS, a Millennium Scientific Initiative Nucleus). We thank the students of the Limnology and Oceanography undergraduate course at Universidad Austral de Chile for their valuable help in the field. To Brooke Penaluna for revising the English in the final version. Finally, we thank the anonymous reviewers for their many suggestions for improving this paper.
Banks MA, MS Blouin, BA Badwin, VK Rashbrook, HA Fitzgerald, SM Blankenship & D Hedgecock. 1999. Isolation and inheritance of novel microsatellites in Chinook salmon (Oncorhynchus tschawytscha). The Journal of Heredity 90: 281-288. [ Links ]
Banks MA, VK Rashbrook, MJ Calavetta, CA Dean & D Hedgecock. 2000. Analysis of microsatellite DNA resolves genetic structure and diversity of Chinook salmon (Oncorhynchus tschawytscha) in California's Central Valley. Canadian Journal of Fisheries and Aquatic Science 57: 915-927. [ Links ]
Basulto S. 2003. El largo viaje de los salmones: una crónica olvidada, propagación y cultivo de especies acuáticas en Chile, 299 pp. Editorial Maval, Santiago de Chile. [ Links ]
Becker LA, MA Pascual & NG Basso. 2007. Colonization of the Southern Patagonia Ocean by exotic Chinook salmon. Conservation Biology 21: 1347-1352. [ Links ]
Cournet JM, S Piry, G Luikart, A Estoup & M Solinac. 1999. New methods employing multilocus genotypes to select or exclude populations as origins of individuals. Genetics 153: 1989-2000. [ Links ]
Di Prinzio CY. 2001. Estudio preliminar de la remonta del salmón Chinook (Oncorhynchus tschawytscha) en las cuencas de los ríos Corcovado, Futaleufú y Pico, Chubut, Argentina. Undergraduate thesis. Universidad Nacional de la Patagonia, San Juan Bosco, Esquel, 52 pp. [ Links ]
Donaldson LR & T Joyner. 1983. The salmonid fishes as a natural livestock. Scientific American 249: 50-58. [ Links ]
Dufflocq A. 1981. Introducción del salmón del Pacífico en Chile, 176 pp. Ministerio de Economía, Fomento, y Reconstrucción, Subsecretaria de Pesca, Santiago de Chile. [ Links ]
Estoup A, CR Largiadèr, E Perrot & D Chourrout. 1996. Rapid one-tube DNA extraction for reliable PCR detection of fish polymorphic markers and transgenes. Molecular Marine Biology and Biotechnology 5: 295-298. [ Links ]
Golusda P. 1907. La introducción del salmón en Chile. Anales Agronómicos, 31 pp. Sección de Aguas y Bosques del Ministerio de Industria. Santiago de Chile. [ Links ]
Greig C & MA Banks. 1999. Five multiplexed microsatellite loci for rapid response run identification of California's endangered winter Chinook salmon. Animal Genetics 30: 318-320. [ Links ]
Hall TA. 1999. BioEdit: a user-friendly biological sequence alignment editor and analysis program for Windows 95/98/NT. Nucleic Acids Symposium Series 41: 95-98. [ Links ]
Heath DD, CA Bryden, JM Shrimpton, GK Iwama, J Nelly & JW Heath. 2002. Relationships between heterozygosity, allelic distance (d2), and reproductive traits in Chinook salmon, Onchoryhnchus tshawystscha. Canadian Journal of Fisheries and Aquatic Science 59: 77-84. [ Links ]
Holland BS. 2001. Invasion without a bottleneck: microsatellite variation in natural and invasive populations of the brown mussel Perna perna (L). Marine Biotechnology 3: 407-415. [ Links ]
Joyner T. 1980. Salmon ranching in South America. In: Thorpe JE (ed). Salmon ranching, pp. 261-276. Academic Press, London. [ Links ]
Kolbe JJ, RE Glor, L Rodríguez, A Chamizo, A Larson & JB Losos. 2004. Genetic variation increases during biological invasion by Cuban lizard. Nature 431: 177-181. [ Links ]
Lee CE. 2002. Evolutionary genetics of invasive species. Trends of Ecology and Evolution 17: 386-391. [ Links ]
Lemaire C, G Allegrucci, M Naciri, L Bahri-Sfar, H Kara & F Bonhomme. 2000. Do discrepancies between microsatellite and allozyme variation reveal differential selection between sea and lagoon in the sea bass (Dicentrarchus labrax)? Molecular Ecology 9(4): 457-467. [ Links ]
Pascual M & J Ciancio. 2007. Introduced anadromous salmonids in Patagonia: Risks, uses, and conservation paradox. In: Bert T (ed). Ecological and Genetic Implications of Aquaculture Activities, pp. 333-354. Springer-Verlag, New York. [ Links ]
Raymond M & F Rousset. 1995. GENEPOP (version 1.2): A population genetics software for exact test and ecumenicism. Journal of Heredity 86: 248-249. [ Links ]
Piry SG, G Luikart & JM Cornuet. 1999. BOTTLENECK: a computer program for detecting recent reductions in the effective population size using allele frequency data. Journal of Heredity 90: 502-503. [ Links ]
SERNAPESCA. 2006. Anuario estadístico de Pesca 2006, 181 pp. Servicio Nacional de Pesca, Valparaíso. [ Links ]
Soto D, I Arismendi, J González, J Sanzana, F Jara, C Jara, E Guzmán & A Lara. 2006. Southern Chile, trout and salmon country: invasion patterns and threats for native species. Revista Chilena de Historia Natural 79: 97-117. [ Links ]
Soto D, I Arismendi, C di Prinzio & F Jara. 2007. Establishment of Chinook salmon (Oncorhynchus tshawytscha) in Pacific basins of Southern South America and its potential ecosystem implications. Revista Chilena de Historia Natural 80(1): 81-98. [ Links ]
Therriault TW, MI Orlova, MF Docker, HJ Macisaac & DD Heath. 2005. Invasion genetics of a freshwater mussel (Dreissena rostriformis bugensis) in a eastern Europe: high gene flow and multiple introductions. Heredity 95: 16-23. [ Links ]
Williamson KS & B May. 2005. Homogenization of fall-run Chinook salmon gene pools in the Central Valley of California, USA. North American Journal of Fisheries Management 25: 993-1009. [ Links ]
Recibido el 18 de abril de 2008 y aceptado el 12 de agosto de 2008