Pacific salmon (Oncorhynchus spp.) navigate towards spawning grounds using olfactory cues they imprinted on as juveniles. The timing at which imprinting occurs has been studied extensively, and there is strong evidence that salmon imprint on their natal water during the parr-smolt transformation (PST). Researchers have noted, however, that the life histories of some species of Pacific salmon could necessitate imprinting prior to the PST. Juvenile pink salmon (O. gorbuscha) spend less time in fresh water than any other species of Pacific salmon, and presumably must imprint on their natal water at a very young age. The time at which imprinting occurs in this species, however, has not been experimentally tested. We exposed juvenile pink salmon as alevins to phenethyl alcohol (PEA) or control water, reared these fish to adulthood, and then tested their behavioural responses to PEA to determine whether the fish successfully imprinted. We found that pink salmon exposed to PEA as alevins were attracted to the chemical as adults, suggesting that imprinting can occur during this stage. Our finding provides some of the first evidence to support the long-standing belief that imprinting can occur in pink salmon prior to the PST.
The ability of Pacific salmon (Oncorhynchus spp.) to home to their natal stream is an iconic example of animal navigation during a large scale migration. Wisby and Hasler1 hypothesized that juvenile salmon ‘imprint’ on the unique odour of their natal water, and returning adults use their sense of smell to detect these imprinted odours. Subsequent research confirmed the occurrence of olfactory imprinting2,3, and suggested that the memory of the natal stream is formed during the parr-smolt transformation (PST), as juvenile salmon prepare for their downstream migration to the ocean4,5,6,7,8. Most of the research on the timing of imprinting has focused on coho salmon (O. kisutch) but imprinting during the PST has been confirmed in other species as well, including steelhead (O. mykiss)9, Atlantic salmon (Salmo salar)10 and brown trout (S. trutta)11. Concurrent with the imprinting activity during the PST is a surge in circulating thyroxine12 that may regulate the imprinting process13,14. A recent study15 on chum salmon (O. keta) also found increased expression of the NR1 subunit of the N-methyl-D-aspartate receptor, which influences memory formation in fish and could be critical to successful imprinting, during the downstream migration.
Although imprinting occurs during the PST in species that rear for a period of time in their natal streams, such as coho salmon, species with different life histories must imprint earlier during development6,16,17. Pink salmon (O. gorbuscha) and chum salmon, for example, leave their natal area and swim towards the ocean shortly after emergence from the incubation site, while sockeye salmon (O. nerka) swim directly to a lake. For these species, homing to the natal stream presumably requires learning home stream odours prior to leaving the incubation site, perhaps before emergence or even hatching. Indeed, there is evidence that sockeye salmon fry learn the odour of their incubation site before leaving for a lake18,19, and that some form of learning occurs in sockeye salmon as early as the embryo stage20. The most direct evidence of imprinting during an early life stage was provided by Tilson et al.21, who demonstrated imprinting in sockeye salmon during the alevin stage (when the developing salmon has hatched, but retains nutrients from the egg in a yolk sac and remains in the gravel of the nest site) and the emergence stage (when the yolk sac has been fully absorbed, and the salmon emerges from the gravel). They exposed individuals to a synthetic chemical during several periods of their early development, and found increased whole body thyroxine levels during the alevin and emergence stages, as well an attraction to the imprinting chemical in adults exposed during those periods.
Unlike sockeye salmon, however, which typically reside one or two years in a lake that may share some of the odours from the home stream, pink and chum salmon are the only species of Pacific salmon that do not rear in fresh water before migrating to the ocean. Pink salmon in particular leave their natal sites quickly, developing salinity tolerance around the time of yolk-sac absorption22, and spending less time in fresh water after emerging from the gravel than any other Oncorhynchus species23. Natal site fidelity appears to be lower in pink salmon than the other species as well24, which could result from an imprinting period that is contracted or occurs at an earlier developmental stage, as necessitated by their unique life history. Aside from the research of Tilson et al.21, though, direct evidence of imprinting during larval stages is limited25, and olfactory imprinting prior to emergence from the gravel has not been demonstrated in pink salmon.
We attempted to imprint juvenile pink salmon to the odour of phenethyl alcohol (PEA), a chemical that has been used extensively in previous imprinting studies. These studies demonstrated that juvenile salmon can learn specific chemicals such as PEA and later use these chemicals to guide homing adults2,3,6,26. Furthermore, PEA is a natural compound27,28 that elicits olfactory responses7,26,29 and can be learned by salmon6,26 and other fish species30,31. Unlike many odorants such as amino acids, PEA is also ideal for imprinting studies because it does not elicit innate behavioural responses2,31 and is not typically present in municipal waters (used as control water in these studies) allowing for precise control of the concentration. We reared offspring from wild Fraser River pink salmon in a laboratory, and exposed them to either control water or water containing PEA during the alevin, stage. We then tested the behavioural response of these fish to PEA as two-year-old adults during the time of their natural spawning migration. We predicted that fish would imprint to PEA during the alevin stage, the period that directly precedes their emigration from their natal site.
As part of an unrelated study examining swim performance in juvenile pink salmon, a small number of wild pink salmon adults were sampled for sperm and eggs from fish that arrived at artificial spawning grounds in Seton River and Weaver Creek, both tributaries of the lower Fraser River, B.C., Canada, in October 2013. They are situated 215 river km from each other and spawning occurs at the same times of the year in both channels. The population structure of pink salmon in the lower Fraser River is not well defined (as it is with other species such as sockeye salmon) and individuals spawn throughout this entire region at the same time. The gametes were transported to a laboratory at the University of British Columbia where the eggs were fertilized (15 females were each crossed with 3 males for each of the two populations, and a random subset from these were used for this experiment), incubated at 8 °C in Heath trays until emergence (i.e. full yolk sac absorption), and then transferred to 1000 l flow-through troughs, separated by population and treatment. In December 2014, the fry were implanted with Passive Integrated Transponder (PIT) tags (that emit a unique identification code), and in April 2015 they were transferred to a communal 8000 l flow-through tank. They remained in the tank until behavioural trials. Throughout the experiment, lighting was adjusted to match the photoperiod of their natural environment, and water temperatures fluctuated naturally over the course of the two years from 6 °C to 18 °C. The fish were fed commercial salmon feed (EWOS Canada Ltd., BC, Canada) ad libitum until behavioural trials.
Fish were reared and tested in dechlorinated municipal water originating from Metro Vancouver’s Capilano watershed. During the alevin stage (December 15, 2013 to January 28, 2014; 603–859 accumulated temperature units), fish were continuously exposed to control water or water containing 10−7 M PEA (W285803 Sigma-Aldrich). A stock solution of 10−5 M PEA dissolved in municipal water was metered into the Heath trays using a peristaltic pump (Masterflex L/S model 7536–04, Cole-Parmer, QC, Canada) to achieve a final concentration 10−7 M PEA. This concentration of PEA has been used in previous salmon imprinting studies3,6.
We conducted behavioural trials from October 15 to October 27, 2015. We used a two-choice chamber, or Y-maze, to test the behavioural responses of the adult pink salmon to PEA (Fig. 1). The Y-maze was constructed from plywood and sealed with fish-safe liquid rubber (Ames Research Laboratories, Salem, OR), and was covered with a tarp. Water entered each side, or arm, of the Y-maze at a rate of 15 L min−1, and a dye test demonstrated that no water was exchanged between the two arms. Using the peristaltic pump, a stock solution of 10−4 M PEA was added from a 20 L acid-washed Nalgene container to one arm of the Y-maze to achieve a final concentration of 10−7 M. The solution was dripped into the inlet water as it flowed into the maze. Water from a second 20 L acid-washed Nalgene container was added to the other arm at the same rate. The water was drained and refilled between trials, and the arm receiving PEA was alternated daily such that the number of trials with PEA in each arm was equivalent.
At the start of each trial, a pink salmon was transferred from the rearing tank to the downstream end of the Y-maze. A plastic gate prevented the fish from entering the two arms. After a 20 minute acclimation period, the gate was removed and the fish’s activity was recorded for 30 minutes using an underwater camera (Cameray Electronic Co., Ltd., China). Behaviours were monitored visually, rather than through the use of a PIT array as in some studies e.g. ref. 32, to capture behaviours that would be missed by an automated PIT system. We recorded the amount of time each fish spent in each of the two arms, as well as the number of times each fish crossed through the stream of water flowing into each arm. The latter behaviour captured the activity of the fish at the upstream end of the arm and could indicate an attempt to swim further ‘upstream’, as salmon are positively rheotactic during the spawning migration33. After the trial, we euthanized each fish with tricaine methanesulfonate (MS-222), measured the fish’s fork length and weight, and dissected each fish to confirm sex. The Y-maze was drained and refilled between trials to limit the possibility of chemical cues released by the fish influencing subsequent trials.
The fork lengths and weights (mean ± standard error) of the salmon at the time of trials were 29.3 ± 0.7 cm and 270 ± 17 g for females (n = 16), and 28.1 ± 0.5 cm and 267 ± 16 g for males (n = 12). We ran the tests when the salmon were clearly nearing maturity and developing secondary sex characteristics. The time of year was also consistent with when these fish would be migrating and spawning in the Fraser River.
The research conformed to protocols approved by the University of British Columbia Committee on Animal Care (A15-0205) and met the Canadian Council for Animal Care guidelines.
Due to mechanical issues with our rearing facility, we were not able to rear large numbers of fish to adulthood. To ensure adequate sample sizes for analyses, we pooled fish whose parents came from the two adult spawning channel sources. This should not bias the core results as the two parent sources are nearly identical in their freshwater imprinting timing and duration. Based on acoustic tagging results, juvenile sockeye salmon migrate down the Fraser River at an average speed of 150 km per day34, which is the approximate speed of the Fraser River in spring. Assuming pink salmon also travel at the speed of the river, juvenile Seton River pink salmon, which are spawned further up the Fraser River than juvenile Weaver Creek pink salmon, would only take ~1.5 days longer to migrate to the ocean than Weaver Creek juveniles. This, combined with the fact that juveniles from both channels immediately migrate downstream following emergence, and do so at the same time of year, suggests that their imprinting patterns are similar. We compared the amount of time spent in each arm using paired t-tests (α = 0.05), and the proportion of time spent in the arm with PEA using a one sample t-test (μ = 0.5, α = 0.05), both of which met assumptions of variance and normality. We compared the number of times the fish crossed through the inflow of the water in each arm, which did not meet assumptions of normality even following transformation, with a Wilcoxon signed-rank test (α = 0.05). Statistical analyses were performed in R Studio (V 0.98.501, RStudio Inc., Boston, MA).
Adult pink salmon exposed to PEA during the alevin stage (n = 10; 6 females and 4 males) spent more time in the arm containing PEA (t9 = 2.27, P = 0.049; Fig. 2a), and they also crossed through the stream of water flowing into this arm more frequently than the stream flowing into the other arm (V = 40, n = 10, P = 0.044; Fig. 2b). The proportion of time spent in the arm with PEA was also greater than 0.5 in this group, although the difference was not significant (t9 = 2.07, P = 0.069; Fig. 3). Adult pink salmon from the control group (n = 18; 10 females and 8 males), which were never exposed to PEA as juveniles, did not spend more time in either arm (t17 = 0.18, P = 0.86; Fig. 2a), did not cross through the inflow more frequently in either arm (V = 83, n = 18, P = 0.78; Fig. 2b), and did not spend a proportion of time in the PEA arm that differed from 0.5 (t17 = −0.22, P = 0.83; Fig. 3).
Our findings indicated that pink salmon alevins are able to imprint on the chemical composition of rearing water, prior to full absorption of the yolk sac and emergence from the gravel. While these results might be expected based on their life history, these are the first results to provide direct evidence that pink salmon imprint to chemical cues as alevins. Similar results might also be expected in other species of Pacific salmon, particularly chum salmon, which also do not rear in fresh water prior to their downstream migration16,35. Further studies on pink salmon that make use of a larger sample size could also lend evidence to better assess the accuracy of our findings.
There is substantial evidence that imprinting occurs during the PST in Oncorhynchus species3,4,5,6,7,8. The PST is characterized by endocrine, physiological, and behavioural changes that prepare salmon for life in the ocean36, including increases in gill Na+, K+ ATPase (ATPase) activity and circulating thyroxine levels linked to imprinting12,13. For many species with extensive freshwater rearing, the PST occurs months or years after emergence from the natal gravel, during a salmon’s final exposure to odours of its home river prior to seaward migration. For pink and chum salmon the transition to a saltwater environment often occurs as juveniles are leaving their natal site. Previous studies have indicated that just before emergence, pink salmon experience increases in ATPase and thyroxine levels reminiscent of the PST in other species22,37. In pink salmon this developmental period may be analogous to the PST and therefore may represent a similar sensitive period for imprinting.
Other Pacific salmon species with more extensive freshwater rearing can return to natal sites they only experienced as embryos, which suggests that imprinting may also occur prior to emergence in species other than pink and chum salmon. For example, sockeye salmon migrate to a nearby rearing lake immediately after emergence, indicating that imprinting during either the embryo or alevin stage is necessary for returning adults to navigate towards their incubation sites using olfactory directional cues. Indeed, sockeye salmon can demonstrate very fine-scale homing to a natal site only experienced as embryos20. If imprinting does not occur until the PST, returning adults could use olfactory directional cues to locate their rearing lake, but would presumably require some other type of directional cues to find their natal stream. Similarly, coho and Chinook (O. tshawytscha) salmon often make extensive migrations from their natal site prior to the PST, suggesting imprinting may occur before this period38,39.
Hasler and Scholz3 hypothesized that salmon imprint on a ‘bouquet’ of odours in their rearing water, and if true, the individual imprinting chemicals typically used in these studies (e.g. PEA, morpholine) would be just one component added to a more complex bouquet of odours. In many previous artificial imprinting experiments, adults were tested in water that differed from their rearing water such that the imprinted odorant was the only familiar cue available (e.g. refs 2 and 6). It is interesting to note that in our study, salmon were maintained in the same water source throughout their lives including the period of exposure to the imprinting odorant, rearing, and behavioural testing of adults. If the chemical composition of this water remained consistent through the duration of the study, the results of our experiment would indicate that the salmon distinguished the imprinted odour bouquet containing the artificial chemical PEA from the bouquet lacking PEA.
Previous studies in which a single imprinting odorant was added to a complex natural water in an attempt to increase homing fidelity to a hatchery produced mixed results40,41,42. In a series of hatchery experiments, salmon were either exposed to normal hatchery water or hatchery water containing the imprinted odorant morpholine prior to release. In one study, morpholine-exposed coho salmon returned to the hatchery in higher numbers than control fish when morpholine was added to the return ladder, suggesting that salmon had imprinted to and distinguished water with morpholine added41. However, in similar studies with coho and Chinook salmon, prior exposure to morpholine-scented hatchery water did not influence return rates when morpholine was added to the return ladder40,42.
Taking a different approach, Yamamoto and Ueda43 studied imprinting and homing responses of Osaru River chum salmon by identifying the amino acid profile of their natal river and testing the behavioural responses of Osaru River chum salmon to an artificial Osaru River water created by dissolving the same concentration and composition of amino acids to blank fresh water. They also created a second artificial river water that was identical except the most abundant amino acid was not added. Behavioural response tests showed the adult chum salmon preferred both artificial waters to waters from other rivers, and they did not distinguish the two replicates from one another. In other words, the removal of a single amino acid did not affect the response of the salmon to the chemical bouquet.
It is possible that the chemical composition of the water used for our experiment changed between the rearing period and the behavioural trials two years later, aside from PEA, which remained stable. Yamamoto et al.44 found that the concentrations of many amino acids in a salmon-bearing river in Hokkaido, Japan changes seasonally and annually. Of course, returning salmon are presumably able to recognize the overall odour of their natal water even if the specific chemical composition changes, and the intricacies of the specific chemicals involved in olfactory imprinting are simply not yet understood. Taken together, the previous research and our study suggest Pacific salmon may be able to detect and distinguish changes to even a single component of the olfactory bouquet, but their sensitivity to such changes, and how changes in chemical composition might occur in the natural environment, remain unknown.
Our finding with pink salmon provides evidence for the long-standing assumption that some Pacific salmon imprint on their natal water prior to the PST. It is possible that imprinting might occur prior to emergence in other species as well. It is also possible that the necessity for pink salmon to imprint earlier than their congenerics might contribute to reduced home stream fidelity, as the olfactory and central nervous systems may be relatively less developed at the time of imprinting. The timing of imprinting in different salmon species is not only important biologically but may have important implications for salmon hatchery rearing and release practices as well17. Further studies on the imprinting process in species such as chum salmon, which also must imprint at an early life stage before migrating to the ocean, and sockeye salmon, which may need to imprint prior to moving from their natal stream to their rearing lake, could determine whether species-level similarities or differences exist.
How to cite this article: Bett, N. N. et al. Evidence of Olfactory Imprinting at an Early Life Stage in Pink Salmon (Oncorhynchus gorbuscha). Sci. Rep. 6, 36393; doi: 10.1038/srep36393 (2016).
Publisher’s note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Wisby, W. J. & Hasler, A. D. Effect of olfactory occlusion on migrating silver salmon (O. kisutch). J. Fish. Res. Bo. Can . 11, 472–478 (1954).
Scholz, A. T., Horrall, R. M., Cooper, J. C. & Hasler, A. D. Imprinting to chemical cues: the basis for home stream selection in salmon. Science 192, 1247–1249 (1976).
Hasler, A. D. & Scholz, A. T. Olfactory Imprinting and Homing in Salmon . (Springer-Verlag, 1983).
Cooper, J. C. & Hasler, A. D. Electroencephalographic evidence for retention of olfactory cues in homing coho salmon. Science 183, 336–338 (1974).
Cooper, J. C., Scholz, A. T., Horrall, R. M., Hasler, A. D. & Madison, D. M. Experimental confirmation of the olfactory hypothesis with homing, artificially imprinted coho salmon (Oncorhynchus kisutch). J. Fish. Res. Bo. Can . 33, 703–710 (1976).
Dittman, A. H., Quinn, T. P. & Nevitt, G. A. Timing of imprinting to natural and artificial odors by coho salmon (Oncorhynchus kisutch). Can. J. Fish. Aquat. Sci. 53, 434–442 (1996).
Dittman, A. H., Quinn, T. P., Nevitt, G. A., Hacker, B. & Storm, D. R. Sensitization of olfactory guanylyl cyclase to a specific imprinted odorant in coho salmon. Neuron 19, 381–389 (1997).
Yamamoto, Y., Hino, H. & Ueda, H. Olfactory imprinting of amino acids in lacustrine sockeye salmon. PLoS One 5, e8633 (2010).
Cooper, J. C. & Scholz, A. T. Homing of artificially imprinted steelhead (rainbow) trout, Salmo gairdneri. J. Fish. Res. Bo. Can . 33, 826–829 (1976).
Sutterlin, A. M., Saunders, R. L., Henderson, E. B. & Harmon, P. R. The homing of Atlantic salmon (Salmo salar) to a marine site. Can. Tech. Rep. Fish. Aquat. Sci. 1058, 111 + 6 p (1982).
Scholz, A. T., Cooper, J. C., Horrall, R. M. & Hasler, A. D. Homing of morpholine-imprinted brown trout, Salmo trutta. Fish. B-NOAA 76, 293–295 (1978).
Morin, P.-P., Anderson, Ø., Haug, E. & Døving, K. B. Changes in serum free thyroxine, prolactin, and olfactory activity during induced smoltification in Atlantic salmon (Salmo salar). Can. J. Fish. Aquat. Sci. 51, 1985–1992 (1994).
Dittman, A. H. & Quinn, T. P. Homing in Pacific salmon: mechanisms and ecological basis. J. Exp. Biol. 199, 83–91 (1996).
Lema, S. C. & Nevitt, G. A. Evidence that thyroid hormone induces olfactory cellular proliferation in salmon during a sensitive period for imprinting. J. Exp. Biol. 207, 3317–3327 (2004).
Ueda, H. et al. Involvement of hormones in olfactory imprinting and homing in chum salmon. Sci. Rep . 6, 21102 (2016).
Brannon, E. L. Orientation mechanisms of homing salmonids In Salmon and Trout Migratory Behavior Symposium (ed. Brannon, E. L. & Salo, E. O. ) 219–227 (University of Washington, 1982).
Dittman, A. H., Pearsons, T. N., Couture, R. B. & Noakes, D. L. G. Imprinting of hatchery-reared salmon to targeted locations: a new embryonic imprinting paradigm for hatchery programs. Fisheries 40, 114–123 (2015).
Bodznick, D. Characterization of olfactory bulb units of sockeye salmon with behaviorally relevant stimuli. J. Comp. Physiol. A 127, 147–155 (1978).
Courtenay, S. C. Learning and memory of chemosensory stimuli by underyearling coho salmon Oncorhynchus kisutch (Walbaum). PhD Dissertation, University of British Columbia (1989).
Quinn, T. P., Steward, I. J. & Boatright, C. P. Experimental evidence of homing to site of incubation by mature sockeye salmon, Oncorhynchus nerka. Anim. Behav. 76, 941–949 (2006).
Tilson, M. B., Scholz, A. T., White, R. J. & Galloway, H. Thyroid-induced chemical imprinting in early life stages and assessment of smoltification in kokanee salmon: implications for operating Lake Roosevelt kokanee salmon hatcheries. Bonneville Power Administration, US Department of Energy (1994).
Gallagher, Z. S., Bystriansky, J. S., Farrell, A. P. & Brauner, C. J. A novel pattern of smoltification in the most anadromous salmonid: pink salmon (Oncorhynchus gorbuscha). Can. J. Fish. Aquat. Sci. 70, 349–357 (2013).
Heard, W. R. Life history of pink salmon In Pacific Salmon Life Histories (eds Groot, C. & Margolis, L. ) 119–230 (University of British Columbia Press, 1991).
Quinn, T. P. The Behavior and Ecology of Pacific Salmon & Trout . (University of Washington Press, 2005).
Bett, N. N. & Hinch, S. G. Olfactory navigation during spawning migrations: a review and introduction of the hierarchical navigation hypothesis. Biol. Rev. 91, 728–759 (2015).
Nevitt, G. A., Dittman, A. H., Quinn, T. P. & Moody, W. J. Evidence for a peripheral olfactory memory in imprinted salmon. P. Natl. Acad. Sci. USA 91, 4288–4292 (1994).
Erbas, S. & Baydar, H. Variation in Scent Compounds of Oil-Bearing Rose (Rosa damascena Mill.) Produced by Headspace Solid Phase Microextraction, Hydrodistillation and Solvent Extraction. Records Of Natural Products 10, 555–565 (2016).
Medjahed, F., Merouane, A., Saadi, A., Bader, A., Cioni, P. L. & Flamini, G. Chemical profile and antifungal potential of essential oils from leaves and flowers of Salvia algeriensis (Desf.): A comparative study. Chilean J. Agri. Res. 76, 195–200 (2016).
Harden, M. V., Newton, L. A., Lloyd, R. C. & Whitlock, K. E. Olfactory imprinting is correlated with changes in gene expression in the olfactory epithelia of the zebrafish. J. Neurobiol. 66, 1452–1466 (2006).
Braubach, O. R., Wood, H. D., Gadbois, S., Fine, A. & Croll, R. P. Olfactory conditioning in the zebrafish (Danio rerio). Behav. Brain Res. 198, 190–198 (2009).
Morin, C., Silva, M. A. D., Muller, C. P., Hardigan, P. & Spieler, R. E. Active avoidance learning in zebrafish (Danio rerio)—The role of sensory modality and inter-stimulus interval. Behav. Brain Res. 248, 141–143 (2013).
Yun, S.-S. et al. Identification of putative migratory pheromones from Pacific lamprey (Lampetra tridentata). Can. J. Fish. Aquat. Sci. 68, 2194–2203 (2011).
Johnsen, P. B. & Hasler, A. D. The use of chemical cues in the upstream migration of coho salmon, Oncorhynchus kisutch Walbaum. J. Fish Biol. 17, 67–73 (1980).
Clark, T. D. et al. Tracking wild salmon smolts to the ocean reveals distinct regions of nocturnal movement and high mortality. Ecol. Appl., doi: 10.1890/15-0632 (2016).
Salo, E. O. Life history of chum salmon In Pacific Salmon Life Histories (eds Groot, C. & Margolis, L. ) 231–310 (University of British Columbia Press, 1991).
Hoar, W. S. Smolt transformation: evolution, behavior, and physiology. J. Fish. Res. Bo. Can. 33, 1233–1252 (1976).
Sullivan, C. V., Brewer, S. D., Johnston, G. P. & Dickhoff, W. W. Plasma thyroid-hormone concentrations and gill (Na+K)-ATPase activities in postemergent pink salmon. T. Am. Fish. Soc. 112, 825–829 (1983).
Beckman, B. R., Larsen, D. A., Sharpe, C., Lee-Pawlack, B., Schreck, C. B. & Dickhoff, W. W. Physiological status of naturally reared juvenile spring chinook salmon in the Yakima River: seasonal dynamics and changes associated with smolting. T. Am. Fish. Soc . 129, 727–753 (2000).
Shrimpton, J. M. et al. Freshwater movement patterns by juvenile Pacific salmon Oncorhynchus spp. before they migrate to the ocean: Oh the places you’ll go! J. Fish. Biol. 85, 987–1004 (2014).
Rehnberg, B. G., Curtis, L. & Schreck, C. B. Homing of coho salmon (Oncorhynchus kisutch) exposed to morpholine. Aquaculture 44, 253–255 (1985).
Hassler, T. J. & Kucas, S. T. Returns of morpholine-imprinted coho salmon to the Mad River, California. N. Am. J. Fish. Manage . 8, 356–358 (1988).
Hassler, T. J. & Kutchins, K. Homing by Chinook salmon exposed to morpholine. Calif. Fish Game 76, 31–35 (1990).
Yamamoto, Y. & Ueda, H. Behavioral responses by migratory chum salmon to amino acids in natal stream water. Zool. Sci. 26, 778–782 (2009).
Yamamoto, Y., Shibata, H. & Ueda, H. Olfactory homing of chum salmon to stable compositions of amino acids in natal stream water. Zool. Sci. 30, 607–612 (2013).
We would like to thank M. Banet, S. Healey, A. Lotto, J. Lotto, and K. Zinn for assistance in rearing the fish. S.G.H. was funded by a Natural Sciences and Engineering Research Council of Canada (NSERC) Discovery grant (no. 170064-10). N.N.B. was funded by a NSERC Postgraduate Scholarship-Doctoral.
The authors declare no competing financial interests.
About this article
Cite this article
Bett, N., Hinch, S., Dittman, A. et al. Evidence of Olfactory Imprinting at an Early Life Stage in Pink Salmon (Oncorhynchus gorbuscha). Sci Rep 6, 36393 (2016). https://doi.org/10.1038/srep36393
This article is cited by
Scientific Reports (2018)