ICES Journal of Marine Science, 54: 1009-1014. 1997 Past, present, and future of genetic improvement in salmon aquaculture 0AP H. M. Gjeren and H. B. Bentsen Gjgen, H. M. and Bentsen, ment in salmon aquaculture. H. B. 1997. Past, present, and future of genetic improve- ICES Journal of Marine Science, 54: 1009-1014. The farming of Atlantic salmon has become an important industry in several countries, and breeding programmes have been implemented to improve genetic performance and adaptation to farm environments. Founder stocks used in the Norwegian salmon breeding programme have originated solely from Norwegian rivers and no extrinsic genes have been introduced. The majority (more than 90%) of the additive genetic variation in Norwegian populations of Atlantic salmon has been found within, and not between, river strains. The Norwegian breeding programme comprises four subpopulations. In the event of reduced additive genetic variability due to random drift in the closed breeding populations, crosses between the sub-populations could be made to re-establish the variability. Selection in itself is not expected to reduce the additive genetic variability as long as inbreeding is avoided. To date, seven different traits (body weight at slaughter, age of sexual maturation, survival in challenge tests with furunculosis and ISA, flesh colour, total fat content, and amount of fat tissues) have been included in the breeding goal. The selection response obtained is about 10% per generation for each of these traits. In the future, more traits are likely to be included. The results of and prospects for selective breeding and the use of modern DNA technology to improve genetic performance in aquatic species are discussed. ,c’1997 International Council for the Exploration of the Sea Key words: strains. Atlantic salmon, breeding programmes, H. M. Gjoen and H. B. Bentsen: AKVAFORSK, genetic breeding breeding The Norwegian aquaculture industry started in the early 1970s and by 1995 the output from salmon and trout farming was greater than the sum of the meat production from pig, cattle, and poultry (Anon, 1997a, b). An experiment presently being conducted by AKVAFORSK is comparing a wild stock from the Namsen river with salmon from the fourth generation of the national breeding programme (based mainly on Namsen stock). Preliminary results show that growth of the selected fish until smolting was twice that of the wild fish (T. Refstie, AKVAFORSK, Sunndalsnra, Norway, pers. comm.), suggesting that genetic improvement has contributed substantially to the efficiency of salmon aquaculture. A general understanding of additive genetic improvement through selection and knowledge of the selection L.) is programmes for Atlantic salmon (S&no sub essential when assessing the genetic interactions between the wild stock and escaped farmed Atlantic salmon (Bentsen, 1991). The aim of this paper is to present an outline of some of the general principles of selective $2.5.00/0/jm970299 selection, PO Box 5010. 1432 Aas, Norway. Introduction 105&3139/97/061009+06 variation, and to describe programme. the national Norwegian General principles of a breeding programme The most important prerequisite for genetic improvement through selection is additive genetic variation between individuals for the traits of interest. In practically all traits or characters that can be measured in nature, phenotypic variation can be found. Most studies show that this variation is in part determined by the additive effect of the genes present in the population (e.g. Gjedrem, 1983; Gjedrem et al., 1987; Gjerde et al, 1994). It is this additive genetic variation that makes genetic improvement by selection possible (see, e.g., Gjedrem, 1985; Bentsen, 1990). The initial step in a breeding programme is to select the individuals with the best genetic performance for the trait of interest. Accurate estimates of the breeding values of the breeding candidates is important for the success of a breeding programme (Bentsen and 0 1997 International Council for the Exploration of the Sea 1010 IT. M. Gjeen and H. B. Bentsen Gjerde, 1994). The simplest method is to use the phenotypic value as the breeding value, whereas more advanced breeding programmes utilize more precise methods, methods that estimate the breeding values by using information from all relatives of the breeding candidate. After selecting the superior individuals as parents to produce the next generation, the selection response can be measured in the offspring generation. It should be noted that selection, after an initial two or three generations, is not expected to reduce the additive genetic variation in the offspring generation, either phenotypically or genetically, compared to the parental generation if inbreeding is avoided (Bulmer, 1971; Falconer, 1989; Bentsen, 1994). This improvement of the population mean of a given trait is determined strictly by parameters that can be measured in the population. The improvement, AG, is given by: AG=i . op. h2 where i is the selection intensity; or, is phenotypic standard deviation, which is the sum of the genetic and environmental variation; and h2 is the heritability, which is determined by the proportion of the phenotypic variation that is caused by additive gene effects (Falconer, 1989). The validity of this equation has been proved through hundreds of experiments in a variety of species. The principles of the equation will also apply to more complex selection procedures, such as combined selection and multi-trait selection (e.g. Cunningham, 1969). This means that if selection programmes are to generate continuous genetic progress, they will have to be managed so that the additive genetic variation is maintained in every generation (Gjerde et al., 1996; Villanueva et al., 1996). This can be achieved by controlling inbreeding (Meuwissen and Woolliams, 1994; Meuwissen et al., 1995). In the Norwegian national breeding programme records are kept of the pedigree of all the breeding candidates, and the mating scheme is designed in a way that minimizes any increase in inbreeding. Simulation studies and experiments have shown that maintaining additive genetic variation through generations of selection is possible, both in fish and other animals (e.g. Falconer, 1989; Toro and Perez-Enciso, 1990; Gjerde et al., 1996). This is in contrast to a common assumption that selective breeding will necessarily make a population genetically homogeneous. The great advantage of selecting for additive genetic improvement is that new genetic gain can be accumulated in each generation and may then be maintained in the population. This will result in stepwise and long-term genetic progress. Current breeding programmes The Norwegian breeding programme for Atlantic salmon Origin and gene flow The base populations of the Norwegian breeding programme were formed in the years 1971 to 1974 (Gjedrem et al., 1991a). In order to obtain a broad genetic base, AKVAFORSK collected fertilized eggs from 40 out of about 400 rivers that had stocks of Atlantic salmon. The breeding programme is designed with full-sib groups as the basic unit. The goal was to collect about 12 full-sib groups from each river, but the number of such groups from each river varied. Owing to a four-year generation interval in Atlantic salmon in Norway, four populations of different genetic origin were formed in order to provide stock for the farming industry each year (Gjedrem, 1979; Gjedrem et al., 1987). In each new generation, broodstock is selected according to a ranking of all breeding candidates. This ranking is based on the individual’s breeding values for the traits described in the breeding goal, which will be outlined later. At present the programme is in the 6th generation. In 1989, the strain or stock composition of the Norwegian breeding populations was estimated (Gjedrem et al., 1991a). Figure 1 shows the results from population 1 as an example. In the base population, generation 0, when the eggs were collected from the different rivers, there was a fairly even distribution among a number of river stocks. After only a few generations, however, one of the strains dominated the population. This may be explained by the findings from comparative studies of strains (Gjerde and Refstie, 1984). Most of the genetic variation for a given trait was found within river-strains, between and within families. Only a small fraction, less than 5-10% of the total variation, was explained by the river of origin. This agrees well with studies based on the allelic variation of enzymes (Stahl and Hindar, 1988). Thus, because of the rather small sample sizes from each river stock in the base populations, samples from some rivers could by chance include a larger proportion of superior individuals. Consequently, this strain would also contribute more to the next generation. If a larger proportion of the genetic variability had been associated with the riverstrains, measures could have been taken to secure a more equal genetic representation of the strains in the future gene pool. This would, however, require at least two generations (i.e. 8 years) of strain crossing with severe restrictions on the selection, and consequently limited genetic progress. Figure 2 shows the pattern of gene-flow from the river-strains to the eight populations currently in the Norwegian breeding programme for Atlantic salmon. Past, present, and future of genetic improvement in salmon aquaculture Figure 1. Frequency of river strains in population 1 in the Norwegian breeding programmes. gen. 0 0; gen. 3 (El). 1011 gen. 1 (B)); gen. 2 (0; River strains Pop. 2 Pop. 3 Pop. 4 1986 NFA Figure 2. Gene-flow in the Norwegian breeding programme. After three to four generations of selection at AKVAFORSK’s research station at Sunndalserra, a second breeding station, the Norwegian Fish Farmers’ Breeding Station, was established at KyrksEtersra (Norske Fiskeoppdretteres Avlsstasjon, NFA). Between 1986 and 1989, parallels of full-sib groups from AKVAFORSK were transferred to NFA. Transfer of eyed eggs between the two breeding stations has continued on a regular basis with 10 to 15 full-sib groups exchanged annually between the two stations. In addition to the national breeding programme, private hatcheries have produced their own stocks for farming since 1971, based on fry originating from the national breeding programme or from Norwegian rivers. Two of these private hatcheries, Jakta and Bolaks, also supplied full-sib groups from their own populations to 1012 H. A4. Gjgen and H. B. Bentsen NFA between 1986 and 1989. These groups are no longer represented in the NFA breeding populations, since they did not compete with the National breeding programme’s original broodstock for the traits included in the breeding goal (Fig. 2). The total number of breeding populations in Norway, both national and private breeding programmes, is between 8 and 15, depending on how many of the private programmes are classed as breeding populations. Division of a population into several sub-populations is a recommended strategy to counteract loss of genetic variability due to genetic drift (e.g. Falconer, 1989). The random allelic loss is expected to be divergent in different sub-populations, and full variability may thus be restored by crossing of sub-populations. This possibility has not yet been exploited in Norwegian farmed salmon, but could be used if loss of genetic variability is detected in the future. Furthermore, genetic variability may be restored or introduced by using broodstock from outside the breeding programme. Since it is likely that such introductions will perform less well than the selected broodstock, a separate operation will be needed to preserve and upgrade the introduced germplasm by relaxed selection and controlled crossing with top breeders from the breeding programme. This may require several generations. Organization of the breeding programme The breeding programme comprises two breeding centres located on the north-west coast of Norway. Each breeding centre has four test stations located along the coast to ensure testing under different farming conditions. The mating system used is hierarchical, such that each male is mated to two or three females (Refstie, 1990). When the fish are large enough to be tagged (about 20 g in weight), the 120 best ranked full-sib groups are mixed together in the same tank to avoid systematic errors in the test due to common environmental effects influencing each full-sib group. At smolting the fish are transferred to sea cages. One hundred fish from each full-sib group are evenly distributed among the test stations and an additional 150 fish from each full-sib group are reared at the breeding centre’s sea unit as breeding candidates. In 1992, AKVAFORSK transferred the breeding activity to a separate unit, AkvaGen. Both NFA and AkvaGen were then organized under a new mother company, Norwegian Salmon Breeding (Norsk Lakseavl, NLA), which now operates both breeding centres. Breeding goal Over the 20 years of the programme, the breeding goal has been expanded to cover an increasing number of traits (Table 1). The first trait selected for was growth performance, which is measured as body weight at Table 1. Breeding goal in the Norwegian breeding programme. Year 1975 1981 1993 1994 1995 Trait Growth (G) G+Age sexual maturation (SM) G+SM + Disease resistance (DR) G+SM+DR+Flesh colour (C) G+SM+DR+C+Body composition slaughter. In 1981, age at sexual maturation was included as the second trait, since maturation of fish after 1 year in the sea was a problem for the industry. At that time, the fish reached market size only after 2 years in sea cages. Breeding values for growth and age at sexual maturation are computed based on records collected at the breeding centres as well as from the relatives at the test stations. In 1990, the first experiments with challenge tests to determine resistance against the bacterial disease furunculosis were carried out (Gjedrem et al., 1991b), and this information was utilized in the breeding programme in 1993. The following year, resistance in challenge tests with the viral disease Infectious Salmon Anaemia, ISA, was included in the breeding goal. The challenge tests are carried out with parallel groups from the full-sib groups at the breeding centres in a carefully designed closed test station. The test fish are destroyed after testing and the records are used to select among their relatives at the breeding centres. Flesh quality is considered important when marketing Atlantic salmon, but there has been a lack of good methods to measure it, and of exact definitions of the trait(s). Flesh colour, measured optically by a Minolta spectrophotometer, was included in the breeding goal in 1994. In 1995, the second quality trait, body composition or fat content in the meat, was included. This trait consists of two different measurements, total fat content and amount of fat tissue, recorded in a computer tomograph. Carcass traits are recorded on fish slaughtered at the test stations, and the records are used to select among their relatives at the breeding centres. Genetic gain Estimates from 1994 indicate approximately 8-10% genetic gain per generation for growth rate, age at maturation and flesh pigmentation (B. Gjerde AKVAFORSK, As, Norway, pers. comm.). The highest gain has been achieved for growth rate. Since this is the only trait that can be measured on the breeding candidate itself, a higher selection intensity is achieved than for the other traits which are selected based on information from relatives only. Past, present, and future of genetic improvement in salmon aquaculture Future additions to the breeding goal Methods by which to measure the texture of the flesh are under evaluation. A mechanical procedure which has been shown to give similar scores to those given by a trained sensorial test panel has been investigated. The preliminary results are promising, and a heritability of 0.2 has been estimated. NLA is likely to include this trait in the breeding goal in 1997. The next quality trait which is likely to be included in the breeding goal is body shape. Rapid growth in Atlantic salmon is associated with deeper body shape, which is undesirable for marketing reasons since it is different from most wild fish. This can be counteracted by selecting for slimmer fish. The trait may be measured by the traditional condition factor or by developing other related measurements. Some traits may be discontinued if they cease to be of economic importance. For example, as growth rate has been improved, an increasing proportion of the farmed salmon in Norway will reach market size within 1 year of transfer to sea-cages. Delaying sexual maturation through the breeding programme may then become less important than it was some years ago. Breeding programmes other countries for Atlantic salmon 1013 from Scotland and Newfoundland, via Australia. Since, 1996 a breeding programme with selection based on full and half-sib information has been established. The future Genetic engineering During recent years, much attention and many resources have been allocated to research efforts on genetic engineering (e.g. gene transfer). To date, such techniques have not been considered as acceptable tools in the national breeding programme in Norway, or to the fish farmers, to the general public, or to the consumers. The results so far have been of limited value to the industry. One of the main problems when applying these techniques to enhance performance is the incorporation of the introduced gene in a way that results in a wellbalanced organism, able to benefit from the superior gene effect without major disturbances of other biological processes. If transgenic farmed fish become more acceptable or offer benefits in the future, the testing of such individuals and the incorporation of the new gene into the population, are best achieved in an ongoing breeding programme utilizing additive genetic effects. in In Iceland, the main focus of Atlantic salmon production since 1960 has been sea ranching. Initially, the programme utilized (natural) selection for return rate by using recaptured fish as broodstock. In the years 1988 to 1993, a large-scale breeding programme funded by the Nordic Council was conducted at Kollafiordur breeding station near Reykjavik (Jonasson, 1993, 1996). An increased return rate was observed as a result of selective breeding based on family information (Jonasson, 1994). Owing to a general decrease in return rates, the programme was terminated in 1993. In 1995, however, a breeding programme in support of salmon farming was initiated based on broodstock imported from private breeding programmes in Norway. In Canada, the Atlantic salmon Federation in St Andrews, New Brunswick, has conducted a breeding programme since 1984 based on Atlantic salmon captured in the St John River (Friars et al., 1995). The design of the programme is similar to the Norwegian national breeding programme, and the improved stocks are used by the salmon farming industry. Fish from the national breeding programme in Norway were used as base populations in a breeding programme in the Faeroe Islands. The breeding programme was established in 1992 and is based on records from full and half-sib groups. From its beginning in the early 198Os, the Chilean Atlantic salmon farming industry has been based on imported broodstock, mainly from Norway, but also Microsatellite loci Currently available tagging systems represent a major economic and practical limitation for further development of selection programmes based on pedigree information. In such programmes, family groups have to be reared separately until individuals are large enough for tagging. This requires costly multi-tank facilities and also introduces systematic environmental effects common to sibs that may lead to bias in the estimated breeding values. The detection and use of microsatellite loci for family identification purposes may, therefore, represent a milestone in selective breeding of aquatic species. These techniques enable family groups to be reared in a common environment post-fertilization, and the number of families included in the test may be increased considerably. References Anon. 1997a. Jordbruksstatistikk 1995 (Agricultural Statistics 1995). Statistisk Sentralbyra (Statistics Norway). OsloKongsvinger. Anon. 1997b. Tallenes tale. Norsk Fiskeoppdrett (Norwegian Fish Farming), 3: 20-21. Bentsen, H. B. 1990. Application of breeding and selection on farmed fish. 4th World Congress on Genetics Applied to Livestock Production. Edinburgh. 16: 149-158. Bentsen, H. B. 1991. Quantitative genetics and management of wild populations. Aquaculture, 98: 263-266. Bentsen, H. B. 1994. Genetic effects of selection on polygenic traits with examples from Atlantic salmon, Salrvzo salar L. Aquaculture and Fisheries Management, 25: 89-102. 1014 H. M. Gjeen and H. B. Bentsen Bentsen, H. B. and Gjerde, B. 1994. Design of fish breeding programs. Proceedings. 5th World Congress on Genetics Applied to Livestock Production. Guelph, Canada. 19: 353359. Bulmer, M. G. 1971. The effect of selection on genetic variability. The American Naturalist, 105: 201-211. Cunningham, E. P. 1969. Animal breeding theory. Universitetsforlaget, Oslo, Norway. 272 pp. Falconer, D. S. 1989. Introduction to quantitative genetics. Longman Group Limited, Essex, UK. 400 pp. Friars, G. W., Bailey, J. K., and O’Flynn, F. M. 1995. Applications of selection for multiple traits in cage-reared Atlantic salmon (Salvo salar). Aquaculture, 137: 213-217. Gjedrem, T. 1979. Selection for growth and domestication in Atlantic salmon. Zeitschrift fur Tierziichtung und Ztichtungsbiologie, 96: 5659. Gjedrem, T. 1983. Genetic variation in quantitative traits and selective breeding in fish and shellfish. Aquaculture, 33: 51-72. Giedrem, T. 1985. Improvement of productivity through breed-ing schemes. GeoJournal, 10: 233241. Giedrem. T.. Gierde. B.. and Refstie. T. 1987. A review of quantitative genetic research in salmonids at AKVAFORSK. Second International Conference on Quantitative Genetics. Raleigh, North Carolina. 9 pp. Gjedrem, T., Gjoen, H. M., and Gjerde, B. 1991a. Genetic origin of Norwegian farmed Atlantic salmon. Aquaculture, 98: 41-50. Gjedrem, T., Salte, R., and Gjoen, H. M. 1991b. Genetic variation in susceptibility of Atlantic salmon to furunculosis. Aquaculture, 97: l-6. Gjerde, B., Gjoen, H. M., and Villanueva, B. 1996. Optimum designs for fish breeding programmes with constrained inbreeding: mass selection for a normally distributed trait. Livestock Production Science, 47: 59972. Gjerde, B. and Refstie, T. 1984. Complete diallele cross between five strains of Atlantic salmon. Livestock Production Science, 11: 207-226. Gjerde, B., Simianer, H., and Refstie, T. 1994. Estimates of genetic and phenotypic parameters for body weight, growth rate and sexual maturity in Atlantic salmon. Livestock Production Sciences, 38: 133-143. Jonasson, J. 1993. Selection experiments in salmon ranching. I. Genetic and environmental sources of variation in survival and growth in fresh water. Aquaculture, 109: 225-236. Jonasson, J. 1994. Selection experiments in Atlantic salmon ranching. Ph.D. Thesis. Agricultural University of Norway, Aas, Norway. Jonasson, J. 1996. Selection experiments on Atlantic salmon ranching. 2. Variation among release sites and strains for return rate, body weight and ratio of grilse to total return. Aquaculture, 144: 217-294. Meuwissen, T. H. E. and Woolliams, J. A. 1994. Effective size of livestock populations to prevent a decline in fitness. Theoretical and Applied Genetics, 89: 1019-1026. Meuwissen, T. H. E., Gibson, J. P., and Quinton, M. 1995. Genetic improvement of production while maintaining fitness. Theoretical and Applied Genetics, 90: 627-635. Refstie, T. 1990. Application of breeding schemes. Aquaculture, 85: 1633169. Stahl, G. and Hindar, K. 1988. Genetisk struktur hos norsk laks: status og perspektiver (Genetic structure in Norwegian Atlantic salmon: status and perspectives). Direktoratet for naturforvaltning. Trondheim Rapport fra Fiskeriforskningen, No. 1, 57 pp. Toro, M. and Perez-Enciso, M. 1990. Optimization of selection response under restricted inbreeding. Genetics Selection Evolution, 22: 93-107. Villanueva, B., Woolliams, J. A., and Gjerde, B. 1996. Optimum design for breeding programmes under mass selection with an application in fish breeding. Animal Science, 63: 563-576.
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