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Transgenerational effects of stress in sockeye salmon (Oncorhynchus nerka) on offspring fertilization… Middleton, Collin T. May 2, 2012

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      TRANSGENERATIONAL EFFECTS OF STRESS IN SOCKEYE SALMON (ONCORHYNCHUS NERKA) ON OFFSPRING FERTILIZATION SUCCESS AND EMBRYONIC SURVIVAL    By COLLIN T. MIDDLETON  CONS 498 Thesis Submitted to the Faculty of Forestry  In Partial Fulfilment of the Requirements For the Degree Bachelor of Science in Natural Resources Conservation (Major in Science and Management)  University of British Columbia May 2, 2012         ABSTRACT Fish cope with stress by mounting a primary endocrine response via the sustained release of glucocorticoid steroid hormones – particularly cortisol. Exposure of fish to chronic stress and the sustained release of cortisol is known to have a wide range of effects on physiological processes, although less is known about its effects on reproduction. I utilized wild sockeye salmon from the Fraser River, British Columbia to examine some of the earliest effects of parental exposure to chronic stress and egg exposure to cortisol on viable offspring production. Fraser River sockeye salmon have declined precipitously in numbers and productivity in recent years. Increasingly stressful spawning migrations and the subsequent detrimental effects increased parental stress has on offspring has been put forth as a hypothesis to help explain these recent declines. I simulated chronic stress by periodically chasing female sockeye salmon for 6 weeks prior to ovulation. Egg survival to hatch remained high in both wild (90%) and control (80%) treatments but was significantly reduced as a result of chronic maternal stress (63%; Kruskal-Wallis test, H = 12.64, P = 0.002). To simulate the effect of circulating levels of maternal cortisol, eggs from wild caught females were fertilized in water dosed with control (0 ng/mL), low (300 ng/mL), and high (1000 ng/mL) levels of cortisol. Egg fertilization success remained high in the control group (90%), but was significantly reduced by exposure to both low and high levels of cortisol (78% and 79% respectively; Kruskal-Wallis test, H = 13.27, P = 0.001). Regardless of stress or cortisol exposure, embryos were highly likely to survive to emergence if they hatched.  Results from this study indicate that transgenerational effects of stressful migrations are real and this has ramifications to the productivity of populations and spawner fitness. Transgenerational effects of stress may be one explanatory mechanism contributing to declines in Fraser River sockeye salmon.        ACKNOWLEDGEMENTS I would sincerely like to thank Natalie Sopinka for all her support and guidance while helping me develop and work through this thesis; this would not have been possible without your help. Thank you to Dr. Scott Hinch for the opportunity to work with such fascinating creatures and for allowing me to apply and expand my knowledge of something I truly care about. Thank you to Dr. Kathy Martin for your time spent reading and editing. To Cassandra Storey, and Tracy and Warren Middleton, your love and support have made these past four years as possible and as wonderful as can be. All animal protocols were approved by the UBC Animal Care Committee (AUP – 0215).                   TABLE OF CONTENTS        Page  Title Page          i Thesis Abstract         ii Acknowledgements         iii Table of Contents         iv List of Figures          v List of Tables          vi Introduction          1-8 Methods          8-12  Results          12-15 Discussion          15-24 References          24-37              LIST OF FIGURES         Page Figure 1: Map of the lower Fraser River, British Columbia and Harrison   9      River collection site    Figure 2: Fertilization success of eggs from stressed mothers   13 Figure 3: Fertilization success of eggs exposed to varying levels of cortisol 13 Figure 4: Survival to hatch of eggs from stressed mothers    14 Figure 5: Survival to hatch of eggs exposed to varying levels of cortisol  14 Figure 6: Survival from hatch to emergence of eggs from stressed mothers 15 Figure 7: Survival from hatch to emergence of eggs exposed to varying   15       levels of cortisol                     LIST OF TABLES Table 1: Transgenerational effects of stress on offspring physiology and   2-3      behaviour     Table 2: Summary of crossing design between male and female Harrison    11       Rapids sockeye salmon                 1 Introduction Stress, the stress response and reproduction Stress is omnipresent in the lives of all vertebrates and can stem from stimuli related to changes in an organism’s physical, chemical, or environmental living conditions (Romero 2004). Individuals cope with stress by eliciting a suite of integrated physiological responses when a threat to their homeostasis is perceived (Moberg 2000). This reaction is termed a stress response, and is similar across vertebrates (Romero 2004; Haussman et al. 2011). Indeed, it has been demonstrated that the cumulative effects of a prolonged stress response can ultimately lead to a reduction in survival of individuals (McEwan 1998; Wingfield et al. 1998; Sapolsky et al. 2000; Haussman et al. 2011); however, the primary function of this mechanism is to encourage survival during stressful events.  The primary endocrine response of vertebrates mounting a stress response is the release of glucocorticoid steroid hormones – cortisol and corticosterone (Sapolsky et al. 2000). Fish and mammals primarily release cortisol, whereas reptiles, amphibians, birds, and many rodents release corticosterone (Romero 2004). During a stress response, the release of these hormones brings about different physiological changes to promote survival (Sapolsky 2000). Across vertebrates, glucocorticoids act to mobilize energy stores for immediate utilization in working muscle, stimulate immune function, inhibit reproduction, decrease appetite and feeding, and increase alertness (Wingfield et al. 1998; Moberg 2000; Sapolsky et al. 2000; Haussman et al. 2011). When homeostasis is restored, glucocorticoids quickly return to their baseline levels; however, exposure to repeated or prolonged stressors can give rise to chronic stress and the sustained release of these steroid hormones (Haussman et al. 2011). This prolonged stress response can have a wide range of effects on physiological processes in vertebrates, including reproduction (Sapolsky et al. 2000). It is the sustained release of corticosteroids acting at the level of the hypothalamus- pituitary-adrenal (HPA; or HPI – hypothalamus-pituitary-interrenal in fish) axis and the gonads in vertebrates that are responsible for the effects of stress on reproductive endocrinology (Barton 2002; Wingfield and Sapolsky 2003; Denver 2009). Much is known about the subsequent effects of stress–induced inhibition of reproductive functions, and both acute and chronic stress is shown to adversely affect a range of reproductive indices in vertebrates (Rivier and Rivest 1991; Tilbrook et al. 2000). For example, prolonged stress can result in a suppressive effect on  2 reproductive behaviour, impaired gonadal development, and a reduction in the size, number, and quality of gametes produced across taxa (e.g., in humans, Charmandari et al. 2005; other mammals, Wingfield et al. 1997; birds, O’Reilly and Wingfield 2001; amphibians and reptiles, Moore and Jessop 2003; and fish, Schreck et al. 2001). It is possible that observations like the former and measuring concentrations of glucocorticoids in adults can be used to assess the inhibitory influence of stress on reproduction. However, the most significant metric to assess any animal’s full reproductive capability is the successful production of viable offspring (Campbell et al. 1994). Across vertebrate taxa, it is the effect of stress on this ultimate reproductive parameter that is of greatest importance (Campbell et al. 1994; Painter et al. 2005; Sheriff et al. 2009); the extent to which offspring are affected by parental exposure to stress has received less attention. Transgenerational effects of stress  There is a great deal of variation in the effects of a stressed parent on a number of offspring traits across vertebrate taxa (Table 1). Yet, the quantification of these effects is often based only on the immediate survival of offspring following fertilization, and/or on egg/progeny size, with few studies examining fertilization success or embryonic development, especially in fish (Schreck 2001). Examining how stress affects the fertilization success of eggs and survival through the subsequent stages of embryogenesis in fish can provide a more precise estimate of survival in progeny of by parents that may be predisposed to stressor events prior to or during reproduction. Table 1. Transgenerational effects of stress on offspring physiology and behaviour.  Species Parental stressor Effect on offspring Citation Rat (Rattus norvegicus) Injected with glucocorticoids Reduced birth weights Drake et al. 2004 Snowshoe hares (Lepus americanus) Exposed to the presence of a predator Reduced birth weights Sherrif et al. 2009 Mouse (Mus musculus) Indirectly exposed to disease Increased immune response when exposed to the same disease and less aggression in social groups Curno et al. 2009    3 Great tit (Parus major)  Exposed to ectoparasites Faster growth Buechler et al. 2002 Zebra finch (Taeniopygia guttata) Crowding stress from increased brood sizes Reduction in body size and shorter wing lengths in F1 and F2 generations Naguib et al. 2005 White leghorn chickens (Gallus gallus domesticus) Exposed unpredictable light-dark rhythms Reduced learning, increased competitiveness, and faster growth Lindqvist et al. 2007 Eastern narrow- mouthed toads (Gastrophryne carolinensis) Exposed to a contaminated environment Reduced hatching success, abnormal swimming, and significant craniofacial abnormalities Hopkins et al. 2006 Scincid lizard (Pseudemoia pagenstecher) Exposed to the scent of a predator Increase in chemosensory behaviour and increased body weight Shine and Downes 1999 Striped bass (Morone saxatilis) Eggs developed in polluted estuary Reduction in body length and volume, but an increase in liver size Ostrach et al. 2008 Atlantic salmon (Salmo salar) Females given intraperitoneal cortisol implants Increase offspring mortality and mass, diminished yolk sac volume and utilization, and more aggression in dominant individuals Eriksen et al. 2006; 2011 Rainbow (Oncorhynchus mykiss) and brown trout (Salmo trutta) Chronic chasing and confinement Reduction in survival Campbell et al. 1992; 1994     4 Study species Sockeye salmon are an excellent species in which to examine the parental effects of stress on offspring as a great deal is known about their distribution, migratory life history, and spawning physiology (Groot & Margolis 1991; Quinn 2005; Hinch et al. 2006). The oceanic range of sockeye salmon covers the entire North Pacific Ocean, Bering Sea, and Sea of Okhotsk, with spawning and rearing grounds extending from tributaries of the Columbia River to western Alaska along coastal North America, and throughout the entire Kamchatka Peninsula in Russia (Groot and Margolis 1991). Sockeye salmon are anadromous, that is, they migrate from the ocean to freshwater to spawn and typically exhibit 6 general stages of their migratory life cycle (Hinch et al. 2006). Upon successful spawning during the fall months, fertilized eggs incubate and develop over winter within the gravel or cobble substrates common in most streams and lakes (Quinn 2005; Hinch et al. 2006). In the spring, embryos hatch into alevins where they remain amongst the safety of the substrate and absorb nutrients from their yolk sacs while developing into fry (Quinn 2005; Hinch et al. 2006). Upon absorbing the yolk sac, fry emerge from the substrate and migrate to a nursery lake where they feed and grow for 1-2 years (Quinn 2005; Hinch et al. 2006). In the spring months, after rearing for 1-2 years, juveniles migrate downstream toward the ocean while undergoing smoltification, the process whereby osmoregulatory physiology changes to prepare for entry into saltwater (Quinn 2005; Hinch et al. 2006). While in the ocean, sockeye salmon feed and grow for 1-4 years, covering thousands of kilometers, before sexual maturation is initiated, cuing a directed migration back to the coast and natal rivers (Quinn 2005; Hinch et al. 2006). In the final stages of life from late spring to early fall, sockeye salmon re-enter freshwater and migrate upriver to their natal stream to spawn and eventually die (Quinn 2005; Hinch et al. 2006). It is during this final life stage that sockeye salmon undergo the astonishing physical transformations for which they are best known. Both sexes exhibit drastic changes in colour from their bright silvery marine hues to sexually mature adults characterized by bright green heads and brilliant red bodies, with males developing a distinct large hump on their backs (Groot and Margolis 1991). These unique changes in shape and colour are paralleled by distinct changes in physiology during this final stage of life.  Sockeye salmon undergo constant physiological changes throughout the various stages of their migratory life history (for review see Hinch et. al 2006). However, those that are most  5 challenging and pertinent to successful reproduction are the changes associated with entry into freshwater and upriver spawning migrations (Cooke et al. 2006). During migrations, levels of reproductive and steroid hormones regulating energy use, sexual, and gonadal development change continually up to and following spawning (Hinch et al. 2006). Circulating levels of cortisol increase dramatically as upriver migration progresses (Schmidt and Idler 1962), with increases particularly pronounced in females (Hane and Roberston 1959; Schmidt and Idler 1962; McBride 1986). For example, in sockeye salmon from the Fraser River in British Columbia, levels of cortisol in females can reach 800 ng ml-1during upriver migrations (Hinch et al. 2006), and fall to levels of 350 ng ml-1 upon arrival at spawning grounds, before increasing again to 1200 ng ml-1 post spawning immediately before death (Hruska et al. 2010). Given the correlations of increased maternal and egg cortisol in salmonids (Stratholt et al. 1997), an effect of parental stress on reproduction under these conditions is likely to play a vital role in the subsequent physiological and behavioural development of sockeye salmon offspring.  In salmonids, there is a fine line between too much and too little exposure to cortisol (Hinch et al. 2006; Sloman 2010). The adaptive role of this hormone during adult reproductive migrations and in response to stress is context specific, but the role of cortisol in juvenile development remains unclear (Mommsen et al. 1999). Increased levels of cortisol could serve as a maternally mediated cue that alters offspring phenotypes and behaviour in preparation for a stressful environment (Groothuis et al. 2005; Rubolini et al. 2005 Haussman et al. 2011), or as a mechanism that reduces the overall survival of progeny (Campbell et al. 1992, 1994; McEwan 1998; Wingfield et al. 1998; Sapolsky et al. 2000; Eriksen et al. 2006; 2007; Haussman et al. 2011). These observations in combination with the known effects of increased stress and the role of cortisol on reproductive, survival, and behavioural traits documented in salmonids that are important to aquaculture, present a unique opportunity to experimentally examine the effects of parental exposure to stress on wild sockeye salmon progeny from the Fraser River, British Columbia.   The use of Fraser River sockeye salmon in this study is of particular interest given the significant economic, ecologic, and cultural importance of this species in the province of British Columbia. The Fraser River is the largest salmon producing system in British Columbia, and sockeye salmon are its most commercially valuable and second most abundant species (Hinch and Martins 2011). Sockeye salmon are essential to the prosperity of the people of British  6 Columbia. The commercial fishery for this species has in the past been the most economically valuable salmon fishery in Canada (Williams 2007; Jacob et al. 2007), with the current recreational fishery helping support a multi-billion dollar industry and a number of jobs throughout communities in British Columbia (Kristianson and Strongitharm 2006; British Columbia 2010; Hinch and Martins 2011). Sockeye salmon are essential to marine and freshwater food webs, and decaying adult sockeye salmon carcasses are primary sources of nutrients in coastal watersheds, contributing significantly to ecosystem productivity and the energy available to aquatic and terrestrial organisms (Cederholm et al. 1999; Helfield and Naiman 2001; Hinch and Martins 2011). For thousands of years, many First Nations along the Fraser River have depended on sockeye salmon runs for food, trade, and ceremonial purposes (Jacob et al. 2010). However, since the early 1990s, Fraser River sockeye salmon have declined precipitously in productivity and abundance, ultimately leading to the designation of some populations as ‘endangered’ by the IUCN and the Committee on the Status of Endangered Wildlife in Canada (IUCN-SSG 2009; COSEWIC 2010; Peterman et al. 2010; Hinch and Martins 2011).  Evidence suggests that the recent declines in Fraser River sockeye salmon can be attributed to unfavourable ocean conditions, increasing river temperatures, earlier than usual entry into freshwater, and high en route mortality. However, no single cause of decline can be pointed to (Peterman et al. 2010). Rather, it is suggested that all mechanisms operate simultaneously with additive or multiplicative effects on migrating fish (Peterman et al. 2010; Hinch and Martins 2011). A number of hypotheses have been proposed to further explain these mechanisms and investigate the decline of Fraser River sockeye salmon returns well below historic levels, including those examining the transgenerational effects of stress (Peterman et al. 2010; Hinch and Martins 2011).  During their freshwater spawning migration, Fraser River sockeye salmon face a suite of increasing anthropogenic and environmental stressors related to fisheries, contaminated water, hetero/con-specific competition, increased flows, or less than optimal water temperatures that can lead to high en route mortality before arrival at spawning grounds (Hinch and Martins 2011). Still, many fish are able to successfully spawn, posing the question of what the effects of this increased stress are on the next generation. Hruska et al. (2010) have demonstrated that near fully mature Fraser River sockeye salmon females arriving on spawning grounds have higher  7 baseline stress levels than males at a similar level of maturation. So additional stress experienced during migration may be more detrimental to females and their offspring (Hinch and Martins 2011). Studies of hatchery and farmed raised salmonids suggest there are transgenerational effects of maternal stress related to survival and behaviour in progeny (Campbell et al.1992, 1994; Eriksen et al. 2006, 2011), and both Macdonald et al. (2000) and Patterson (2004) provided evidence that Fraser River sockeye salmon encountering high flows and temperatures, and adverse river conditions can have low embryo survival. However, transgenerational effects in Fraser River sockeye salmon in terms of whether offspring fitness can be affected as a result of stressed maternal condition are not yet supported in the literature (reviewed in Peterman et al. 2010). Therefore, investigating the effects of maternal exposure to increased stress on viable offspring production and progeny development through the later stages in life is imperative as significant transgenerational effects could cause changes in recruit / spawner ratios and contribute to population declines (Peterman et al. 2010). Thesis aims       In an effort to elucidate more of the effects of parental exposure to stress on the progeny of wild Fraser River sockeye salmon, this thesis examined some of the earliest parameters essential to viable offspring production. The aim of my thesis was to determine the effects of maternal exposure to an exogenous stressor and gametic exposure to cortisol, on egg fertilization success and offspring survival through the early stages of embryogenesis. This study utilized gametes from individual females of a wild population of Fraser River sockeye salmon collected during their upriver spawning migration that were chronically exposed to an exogenous stress or whose eggs were exposed to ecologically relevant levels of cortisol during fertilization. I utilized offspring produced by stressed mothers or those from exposed eggs to address two hypotheses.  First, that chronic exposure of female adult sockeye salmon to a repeated exogenous stressor will adversely affect offspring fertilization success and early embryo survival. I predicted that when compared to unstressed or control fish captured on spawning grounds, offspring from stressed mothers would have significantly lower fertilization success and overall lower survival of eggs to the hatched stage. Secondly, that exposure of eggs from females captured during peak spawning to varying elevated levels of cortisol during fertilization would have negative effects on egg fertilization success and reduce offspring survival through early embryogenesis. I predicted that fertilization success and survival to hatch would be significantly  8 lower in eggs exposed to high levels of cortisol when compared to those of low exposure or controls.  Methods  Fish collection and handling  From September 28-30, 2011, male and female sockeye salmon (n = 300) from the Harrison Rapids population were collected by beach seine from the Harrison River (49°17′5 N, 121°54′27 W), a major tributary of the Fraser River in British Columbia (Figure 1). All collection occurred roughly 6 weeks prior to peak spawning while fish were en route to their natal spawning grounds approximately 130 km upstream from the Fraser River mouth below Harrison Lake on Chehalis First Nation’s land. Temperatures of the Harrison River during the time of collection were approximately 14°C. All fish were transported live by vehicle for approximately 1 hour in aerated tanks (at densities no greater than 25 kg fish/m3 of water) continually monitored for dissolved oxygen levels to the Fisheries and Oceans Canada Cultus Lake Salmon Research Laboratory (CLL), British Columbia (Figure 1).  9  Figure 1. Map of the lower Fraser River, British Columbia, Canada, with the locations of the Harrison River collection site and the Fisheries and Oceans Canada Cultus Lake laboratory (CLL). Immediately upon arrival at CLL, fish were distributed among 10 tanks each of 10 000 L holding 30 fish (15 females and 5 males). Each tank was fed with fresh water circulating around the periphery at approximately 25 m/s so fish were able to orient themselves and maintain a constant swimming speed. Air bubblers were constantly in use creating dissolved oxygen levels above 90% at all times, with levels monitored daily. Water for the holding tanks was drawn directly from the Cultus Lake hypolimnion reflecting natural changes in temperature over the course of the study.  Of the ten tanks, 5 served as controls, and 5 as treatment. Treatment began on October 2, 2011 to allow fish time to recover from any stress that may have been caused by transport to the Cultus Lake facility. Over the course of this experiment, treatment fish were subjected to an exogenous stressor and chased around their tanks manually with a net for 3 minutes, twice daily  10 at random times between 0900 and 1700 for approximately 6 weeks. Control fish were left un- chased for the duration of the experiment. After approximately 6 weeks, coinciding with the timing of peak spawning, fish from both treatment groups were dip-netted from their tanks and quickly examined for maturity to minimize air exposure. Fish were considered mature when milt or eggs were easily released from the vent by firmly squeezing along the lateral lines. Immature fish were returned to their tanks and mature fish were immediately sacrificed by cerebral concussion and sampled (see below). Fish were assessed for maturity until November 13th, after which all immature fish were euthanized and the experiment was ended. Before gamete collection, all males had their vents wiped dry with a sterile paper towel to prevent contamination of milt with water or urine. Gametes from each individual were collected into clean, dry, and sterile Tupperware containers and given a dose of O2 in preparation for transport to the Pacific Salmon Ecology and Conservation Lab at the University of British Columbia (UBC) in Vancouver. Between 1 – 4 ml of milt was collected from each male and approximately 100 g of eggs were collected from each female. Measurements of standard length, fork length, postorbital–hypural bone length, and postorbital-fork length were recorded to the nearest 0.1 cm. Fish were weighed for individual total mass and recorded to the nearest 0.01 kg. Gonad mass was measured and recorded to the nearest g. Female gonad mass was the summation of the initial amount of eggs stripped before dissection and that of the mass of any eggs remaining in the body cavity after dissection.   In addition to all the above collection and sampling of experimental fish, 20 male and 20 female sockeye salmon were collected from the same location on November 9, 2011 during peak spawning to serve as ‘wild’ control specimens. All wild fish were subjected to the same terminal sampling and gamete collection as described previously for fish sampled on the Harrison River.  Fertilization, cortisol exposure, and incubation  Gametes from 90 (45 males, 45 females) adult sockeye were used to for this study, allowing for up to 45 full sib crosses (15 unique families across the three treatment groups) to be created. Fertilizations took place from November 8 – 13, 2011 in the UBC lab, with only eggs from a single female crossed with the milt of a single male. Crossing designs included wild × wild, control × control, and control × stress pairings; sample sizes are summarized in Table 2.  11 Table 2. Summary of crossing design between male and female Harrison Rapids sockeye salmon conducted at the Pacific Salmon Ecology and Conservation lab at the University of British Columbia, Vancouver.   Control Male Stress Male Wild Male Control Female n = 14 n = 5  Stress Female n = 14  Wild Female  n = 20  All fertilizations were carried out following a modified method of that presented in Patterson et al. (2004). In a sterile, dry Mason jar, approximately 20 g of eggs were combined with 0.15 mL of milt prior to the addition of 30 mL of water to activate sperm; after 1 minute, an additional 30 mL of water was added. This same dry fertilization technique was applied to all crosses of experimental and ‘wild’ control fish – with the exception of varying doses of cortisol in the water used in ‘wild’ crosses. Fertilizations of ‘wild’ control crosses were each bathed in water containing levels of cortisol equivalent to those found in migrating Fraser River sockeye as described by Hinch et al. (2006) and Hruska et al. (2010). To simulate elevated levels of cortisol in eggs, water for these fertilizations was dosed with 0 ng/mL (control), 300 ng/mL (low), or 1000 ng/mL (high) of cortisol. After remaining undisturbed for approximately 1 hour for water hardening, each group of fertilized eggs was placed into an individual basket and distributed randomly among trays within Heath stacks for incubation. Each stack was supplied with a constant volume of de-chlorinated City of Vancouver water and monitored daily for dissolved oxygen and temperature levels. All Heath stacks were covered in black plastic to maintain darkness and monitored daily until fry emergence, when the yolk sac is fully absorbed or fry are determined “button-up”. Dead eggs were routinely picked from incubation baskets and placed into vials containing Stockard’s solution (5% formaldehyde (40%), 4% glacial acetic acid, 6% glycerin, 85% water) for preservation and future embryo analysis. Individual vials were labeled with the date of collection and the basket number from which dead eggs were picked to later aid in identification of families. Fertilization identification All dead eggs from different families preserved in vials of Stockard’s solution were examined for fertilization success. Using a dissecting microscope at 10x magnification, and tweezers, individual eggs were carefully examined for evidence of fertilization. Date picked from Heath  12 tray, basket number, total number of fertilized and unfertilized eggs were all recorded for each individual vial. Fertilization success was evaluated based on the presence of an early morula visible inside an egg and following the methods of Velsen (1980) who previously documented time to varying developmental stages in sockeye salmon eggs. Further identification aid was provided by a colour photographic index of embryonic development in Chinook salmon (Oncorhynchus tshawytscha) eggs presented by Boyd et al. (2010). Careful attention was paid to the stage of development of each egg with records kept of the number of fertilized, eyed, or hatched embryos contained in each vial. Statistical analysis All statistical analyses were performed with JMP, version 10 (SAS Institute Inc.; Data could not be transformed to meet the assumptions of normality and thus, non-parametric tests were used to examine the effects of parental stress and cortisol exposure on fertilization success and offspring survival at different stages of embryogenesis. A Kruskal-Wallis test was used to compare mean fertilization success and offspring survival to hatch and hatch to emergence across treatment groups. Post-hoc differences were identified using the Tukey HSD test. Standard error bars are presented on all figures and different letters on graphs denote significant differences between treatment groups measured at a P<0.05 level. Results Fertilization success Fertilization success of eggs from mothers exposed to exogenous stress was high (> 83%), but did not vary among treatment groups (Kruskal-Wallis test, H = 12.64, P = 0.13; Figure 2).   13  Figure 2. Fertilization success of Harrison Rapids O. nerka eggs from mothers of wild, control, and exogenous stress treatments.  Eggs exposed to varying levels of cortisol exhibited significantly different levels of fertilization success among treatment groups (Kruskal-Wallis test, H = 13.27, P = 0.001; Figure 3). Eggs exposed to low and high doses of cortisol had similar rates of fertilization success (78% and 79% respectively), with highest success in eggs from the control group (90%) (Figure 3).   Figure 3. Fertilization success of Harrison Rapids O. nerka eggs exposed to control (0 ng/ml), low (300 ng/ml), and high (1000 ng/ml) levels of cortisol during artificial spawning. Values not connected by same letter are significantly different.  Survival to hatch In eggs from mothers exposed to exogenous stress, the percentage that survived to hatch differed significantly among treatment groups (Kruskal-Wallis test, H = 12.64, P = 0.002; Figure 4).  Survival to hatch was lowest (63%) in eggs from stressed mothers, and highest for the wild treatment group (90%) with control levels being intermediate (Figure 4).   14  Figure 4. Percentage of Harrison Rapids O. nerka eggs that survived to hatch from mothers of wild, control, and exogenous stress treatments. Values not connected by same letter are significantly different.    In eggs exposed to different levels of cortisol during artificial spawning, overall levels of survival to hatch were high (>84%) and did not differ across treatments (Kruskal-Wallis test, H = 4.35, P = 0.11; Figure 5).  Figure 5. Percentage of Harrison Rapids O. nerka eggs exposed to control (0 ng/ml), low (300 ng/ml) and high (1000 ng/ml) levels of cortisol during artificial spawning that survived to hatch.  Survival from hatch to emergence Overall survival of eggs from hatch to emergence was very high (>95%). Eggs from any treatment group that survived to hatch were likely to survive to emergence regardless of exposure to exogenous stress or cortisol (Kruskal-Wallis test, H = 2.30, P = 0.32; Figure 6; Kruskal-Wallis test, H = 2.32, P = 0.31; Figure 7).    15  Figure 6. Survival from hatch to emergence of Harrison Rapids O. nerka eggs from mothers of wild, control, and exogenous stress treatments.   Figure 7. Survival from hatch to emergence of Harrison Rapids O. nerka eggs exposed to control (0 ng/ml), low (300 ng/ml) and high (1000 ng/ml) levels of cortisol during artificial spawning.  Discussion I examined some of the earliest effects of transgenerational stress in wild sockeye salmon life history. By subjecting wild caught mothers to chronic exogenous stress during the final stages of maturation and ovulation, or exposing eggs to varying levels of cortisol during fertilization, I was able to examine some of the effects of stress on immediate fertilization success and survival through the early stages of embryonic development. Maternal exposure to exogenous stress did not play a role in fertilization success as no differences were detected among treatments. In contrast, I found exposure of eggs to varying levels of cortisol during fertilization resulted in notable differences in fertilization success among treatments. Overall, fertilization success remained high irrespective of stress treatment, suggesting this is not the critical parameter  16 influencing the effects of maternal stress on viable offspring production. A significant reduction in survival to hatch in eggs from stressed mothers indicates survival through the subsequent stages of embryonic development is influenced by maternal stress. However, egg survival to hatch was not affected by direct exposure to cortisol. Furthermore, regardless of maternal stress or cortisol exposure, if eggs survived to hatch they were likely to survive to emergence as survival remained above 94% between experiments and across all treatment groups. These results are similar to those of Burt et al. (2012) who found post hatch alevin mortality was low in Fraser River sockeye salmon juveniles fertilized and incubated in identical but thermally stressful conditions. Preliminary results from the present study suggest the effects of parental stress on viable offspring production are first realized during the early stages of embryonic development following fertilization and prior to emergence. The following discussion will 1) highlight some of the differences and similarities between this and other studies of stressed salmonids, and 2) explore some of the mechanisms and possible causes or explanations for the differences in fertilization success and survival through development observed in sockeye salmon progeny from stressed mothers or gametes exposed to cortisol during fertilization. Fertilization success Few studies have specifically examined the fertilization success of eggs from wild but artificially stressed salmonids. Using the same dry fertilization technique as was used in this study, Patterson et al. (2004) and Galbraith et al. (2006) found fertilization success in wild caught Fraser River sockeye salmon varied between 86-98% in ideal laboratory settings where fertilization could be maximized, thus providing a standard from which to measure the potential effect of stress on fertilization in this study. Furthermore, Campbell et al. (1992) observed rainbow trout eggs from both control and parents subjected to prolonged acute environmental stress maintained fertilization success over 90% regardless of treatment.  Contrary to what was predicted, but within the range of values from the previously mentioned studies, egg fertilization success in the present study was not affected by parental exposure to exogenous stress and overall remained quite high between 83-89% across wild, control, and stressed treatments. These results, supported by those of Campbell et al. (1992), suggest there is little detrimental effect of parental exposure to exogenous stress on offspring fertilization success. Given only control males were used for fertilization in this study, any effect of stress on sperm motility or viability can be ruled out; suggesting female sockeye salmon have the  17 physiological capacity to buffer some aspects of their reproductive systems against the effects of stress, particularly to do with achieving high fertilization success.  It is possible that the physiological effects of parental exposure to exogenous stress are less important than effects of stress on parental behaviour. Stressed males and females arriving on spawning grounds could elicit behaviours that compromise their abilities to successfully spawn. For example, physiologically stressed females can prematurely release eggs, leading to water hardening before fertilization, or may choose inferior locations to excavate their redds. These behaviours could in turn give way to egg superimposition, less than adequate dissolved oxygen levels leading to egg suffocation, or higher amounts of suspended sediment impairing the ability of eggs to be fertilized (Galbraith et al. 2006). Stressed males could display courtship behaviours that deter mates or result in premature milt release. Indeed, timing is widely regarded as the critical factor in salmonid fertilization success (Liley et al. 2002) as eggs are fertilized less than 10 s after gamete release, and viability is reduced 20 s after release into the water (Hoysak and Liley 2001). Therefore, any effects of stress that might affect behaviour, particularly to do with spawning timing should be considered. The lack of differences observed in my results might be masked by laboratory procedures that eliminated behavioural variability and maximized fertilization success. Further studies utilizing natural spawning environments to examine the effects of parental stress and behaviour on spawning and fertilization warrant consideration. Regardless, my results suggest strong selective pressure for sockeye salmon eggs to be fertilized irrespective of female exposure to chronic stress; likely a result of the anadromous and semelparous nature of sockeye placing heavy emphasis on reproduction no matter the conditions during spawning. Greater detrimental effects on fertilization success could result from fertilization in stressful abiotic environments.   Consistent with my predictions, exposure of sockeye salmon eggs to varying levels of cortisol resulted in significantly reduced fertilization success rates that fell to below 80% as a result of cortisol exposure. However, a lack of significant difference in fertilization success between dosage levels suggests exposure to cortisol alone is enough to influence fertilization. If cortisol dosed water is representative of increasingly stressful migratory conditions, this suggests stressful abiotic environments play a role in influencing production of viable offspring. My results are contrary to those of Li et al. (2010) who immersed rainbow trout eggs in 100 and 1000 ng/mL doses of cortisol and ovarian fluid prior to fertilization and observed no difference  18 in fertilization success. These differences could be attributed to experimental design. A lack of ovarian fluid and the addition of cortisol-dosed water to initiate fertilization in my experiment likely allowed for the effects of cortisol to act simultaneously on both eggs and sperm and to not be influenced by ovarian fluid. Ovarian fluid is a maternal mechanism suggested to protect against the deleterious effects of hypercortisolism in eggs (Shrek et al. 2001). Contreras-Sanchez (1995) demonstrated that rainbow trout could contain 17 times less cortisol in their ovarian fluid than found in circulation, likely protecting oocytes from this hormone during development. By excluding ovarian fluid from eggs before fertilization and removing the cortisol buffering capacity of this substance in my study, I likely observed the unimpeded effects on fertilization success of elevated levels of this hormone.  Stressful abiotic incubation environments as reflected by cortisol could have the capacity to change structural characteristics of sockeye salmon eggs such that fertilization success is reduced simply by direct exposure to this hormone. Khan and Weis (1993) found that exposure of Mummichog (Fundulus heteroclitus) eggs to environmental pollutants results in artificial activation, blockage and swelling of the egg micropyle and lip, and a reduction in diameter and overall fertilization success. Similar effects could have taken place in this study, though I did not examine these parameters; future studies may look to examine the structural effects of cortisol on sockeye salmon eggs.  In the present study, milt was added to eggs prior to fertilization initiation with cortisol- dosed water. As a result, the effects of cortisol exposure on sperm motility cannot be excluded as a factor affecting interpretation. Sperm motility is a prerequisite for fertilization and correlates strongly with fertilization success (Rurangwa et al. 2004). In rainbow trout, Moccia and Munkittrick (1987) concluded that the number of motile sperm was the critical factor for fertilization. These conclusions, and results from this study, suggest cortisol exposure highly influences a reduction of sperm motility and contributes largely to the significant decline in fertilization success observed in the present study. Although direct exposure of sockeye salmon eggs to cortisol as applied here is unlikely to be replicated in the wild, other stressful environments resulting from increased contamination of Fraser River waters from development and land use activities like forestry and agriculture are likely to be encountered. Pollution and its effects on sperm motility are cause for concern as Kahn and Weis (1987) observed significantly reduced sperm motility in Mummichog after exposure to aquatic pollutants. It is likely that  19 sockeye salmon sperm experience the same fate in similarly contaminated environments, leading to a reduction in fertilization success and early embryo survival.  Stress appears to play a role in some aspects of fertilization, although the maintenance of successful fertilization was above 78% in this study regardless of treatment suggesting a great deal of capacity for sockeye salmon females to buffer against the effects of stress on one of the earliest parameters of viable offspring reproduction. Subsequent observations of the later stages of embryonic development suggest a significantly greater effect of stress post-fertilization and prior to embryo hatch. Embryonic survival to hatch Significant reductions in egg survival post-fertilization imply that transgenerational effects of maternal exposure to chronic exogenous stress exist. Consistent with my predictions, embryonic survival to hatch was significantly reduced in eggs from both control and stressed mothers, falling to as little as 63% in the stress treatment group. No significant differences existed between control and stress treatments, though survival to hatch was slightly higher in the control group, implying a possible effect of capture and captivity on stress. Beach seining is meant to minimize invasiveness; however, it is prone to greater delays in transfer, struggling, and air exposure (Nadeau 2007). The effects of captivity on stress from confinement and increased proximity of fish to pathogens combined with effects of the sampling process should not be ruled out. These effects could have created the slight differences in embryonic survival observed between stress and control treatments relative to wild fish. However, Crossin et al. (2008) found no physiological differences in stress measures between captive control and wild Fraser River sockeye salmon at the end of a study applying similar thermal stress, implying that treatment in this study was indeed stressful.  A significant reduction in survival to hatch after parental and embryonic exposure to stress was observed in previous studies conducted on salmonids. Using Fraser River sockeye salmon and thermal stress, Burt et al. (2012) observed egg survival to hatch was high in eggs incubated at optimal water temperatures of 12° C, but decreased significantly to less than 60% using thermally stressful water temperatures during incubation. The present study did not account for the effects of thermal stress; however, my results and those of Burt et al. (2012) could have additive effects and severely reduce sockeye salmon embryonic survival if stressors in the Fraser River continue to escalate (Patterson et al. 2007). Similar to my stress treatment,  20 Campbell et al. (1994) observed offspring from both brown and rainbow trout exposed to chronic exogenous stress before spawning exhibited significantly reduced survival in embryos to hatch. Our results, and those of the two previously mentioned studies, suggest salmonid eggs are particularly susceptible to the effects of parental stress post-fertilization.  A number of mechanisms may be responsible for the observed reductions in survival following stress. Eggs from stressed parents were smaller in size than controls (unpublished data). Though this was not likely a contributing factor to the observed reduction in survival as egg size is not a good indicator of egg quality in many teleosts (Bromage et al. 1992; Brooks et al. 1997). Rather, decreases in egg survival from stressed mothers could be a result of a reduction in egg quality that is related more to function and content. Reductions in egg enzymes and lipid reserves are a result of the stress response in female fish (Schreck et al. 2001; Leatherland et al. 2010). The reduction in embryonic survival I observed could be attributed to a lack of sustenance required for embryonic development. Enzymes are present in all teleost eggs and act to catalyze a number of metabolic processes vital for production of viable offspring (Brooks et al. 1997). Of particular importance are cathespin enzymes that mediate the degradation of stored yolk proteins in free amino acids used by developing embryos (Sire et al. 1994; Brooks et al. 1997). Chronic parental stress may influence the production of these enzymes in eggs and could contribute to the reduction in survival observed in eggs from stressed mothers, particularly if enzymes are important to nutrient absorption in developing embryos. Maternal transfer of lipids during egg development is essential to quality egg and viable offspring production (Brooks et al. 1997). However, this process can be interrupted by the stress response in fish (Schreck et al. 2001) and plays a role in subsequent offspring development. A reduction in the transfer of lipids to eggs could contribute to the reduction of embryonic survival observed in this study. When confounded with a reduction in egg enzymes, the cumulative effects of parental stress on egg nutrient composition is likely enough to elicit the reduction in survival observed in this experiment.  It is well understood that chronic stress results in increased maternal cortisol and is directly correlated with increases in egg cortisol in salmonids (Stratholt et al. 1997). Still, the significance of this hormone in eggs and whether it affects egg quality is less understood (Brooks et al. 1997). Mingist et al. (2007) demonstrated a significant negative relationship between egg survival to the eyed stage and egg cortisol content in masu salmon (O. masou), and Eriksen et al.  21 (2006) have shown that developing embryos from cortisol-stressed Atlantic salmon mothers exhibit increased mortality. This leads to the inference that maternal cortisol has a negative effect on salmonid eggs, and greatly enhances chances of progeny mortality post-fertilization. The effects of stress and presumed increases in maternal and egg cortisol is probably a significant contributing factor to the reduction in embryo survival prior to hatch observed in this study. Future analyses of egg and whole body cortisol content of juveniles used in this study are needed to examine this hypothesis.   Contrary to my predictions, artificially exposing eggs to elevated levels of cortisol did not influence egg survival to hatch, suggesting other maternal and egg aspects affected by stress aside from cortisol levels were equally as important to embryo survival post-fertilization. My findings contradict those of Li et al. (2010) who suggest the function of cortisol on egg survival is dose dependent. However, their results are likely influenced by the cortisol buffering capacity of ovarian fluid maintained in their experiment. Nevertheless, their results support the idea that there is a threshold level of cortisol (Hinch et al. 2006; Sloman 2010) that could affect salmonid offspring survival. A lack of difference in survival to hatch among treatments in my study could be a result of the applied dosage levels being too similar to naturally circulating levels of cortisol found in migrating female sockeye salmon. Perhaps if the applied dosage was higher and better reflected significantly high stress, differences in survival could have been observed. Given these dosages failed to produce results, wild female sockeye and their eggs may possess a capacity to buffer against relatively high levels of cortisol. Female sockeye salmon and their eggs have likely evolved a mechanism to ensure offspring survival during routine spawning. However, increased stressors beyond those encountered naturally during spawning migrations could compromise the natural capacity of females to buffer eggs from cortisol. Still, protection against increased maternal cortisol may be inherent in sockeye salmon eggs.    Another possible explanation for the differences in egg survival to hatch among treatments observed in this study is the ability of eggs to rapidly metabolize or excrete cortisol. Studies of egg cortisol content in salmonid eggs suggest this hormone clears rapidly from developing embryos by the late-eyed stage and may not be a factor in later development (Stratholt et al. 2007; Li et al. 2010). Li et al. (2010) noted a rapid decline in total embryo cortisol content immediately following fertilization of rainbow trout eggs bathed in elevated levels of cortisol. Stratholt et al. (1997) observed significantly elevated levels of cortisol in eggs  22 from stressed female coho salmon was followed by a rapid reduction in cortisol to levels no different from control egg levels only 8 days post-fertilization. Sockeye salmon eggs used in this study likely exhibited the same processes; no differences in survival to hatch across cortisol treatments could be explained by this phenomenon. These patterns suggest sockeye salmon eggs are likely adapted to increases in circulating maternal cortisol and are able to withstand certain threshold levels of this hormone before it becomes deleterious and impedes the very early stages of viable offspring production. This suggests stress and the resulting cortisol in females and eggs is not the ultimate factor determining embryonic survival, rather, offspring survival may be more influenced by the effects of stress on gene expression in eggs and how this relates to embryonic growth after fertilization (Barton 1991; Li et al. 2010). Or perhaps the real effects of stress and cortisol on viable offspring production are realized as post-emergence fry (Eriksen et al. 2006; 2007; 2011).  Subsequent juvenile development in the later stages of life may be compromised by the female stress response. Offspring may be more prone to behaviours that reduce survival (Eriksen et al. 2006), or transgenerational maternal stress may compromise juvenile stress responses (Wendelaar Bonga 1997) that ultimately affect progeny survival in the later stages of life. For example, a compromise in offspring stress response has been observed in the progeny of domestic chickens exposed to elevated levels of maternal cortisol (Haussman et al. 2011). The stress response of chicks shifted to that of more oxidative stress and a reduction in telomere length, which in many species of vertebrates ultimately leads to reduced offspring survival (Haussman et al. 2011). This has not been examined in sockeye salmon; however, a reduction in offspring stress response following maternal stress with similar consequences could compromise future viable offspring production. Future studies examining parental, egg, and offspring gene expression related to growth, behaviour, oxidative stress and telomere length in Fraser River sockeye salmon may be necessary to gain a more precise understanding of the stress response and role of cortisol in offspring development and how this hormone may ultimately affect survival. Conclusions and Future Directions My study suggests increasingly-stressed maturing Fraser River sockeye salmon females have a great capacity to buffer against the effects of elevated physiological stress during migrations on fertilization success. However, observations that subsequent offspring survival can be  23 significantly decreased when female spawners encounter stressful migration conditions (Macdonald et al. 2000; Patterson 2004; Burt et al. 2011; 2012), and the significant reductions in embryonic survival observed in this study suggest transgenerational effects of maternal stress in Fraser River sockeye salmon exist. This has large ramifications for the productivity of populations and spawner fitness.  A number of different hypotheses have been put forth to explain the recent declines in Fraser River sockeye salmon abundance and productivity (Peterman et al. 2010; Hinch and Martins 2011), including transgenerational effects that reduce the overall fitness of subsequent generations. However, due to a lack of directed research and support from empirical analysis of the population data, transgenerational effects are considered very unlikely to have contributed to the long-term downward trend in productivity of Fraser sockeye salmon (Peterman et al. 2010). This study shows that detrimental transgenerational effects on production of viable future generations are real and should be considered as a potential contributing factor in the precipitous decline of Fraser River sockeye salmon.  Climate change, increased flows, and warming water temperatures are widely regarded as significant contributing factors to recent declines in Fraser River sockeye salmon (Peterman et al. 2010; Hinch and Martins 2011). Predictions of further river warming and increasingly difficult migrations will only increase en-route mortality and exacerbate the effects of stress on adults that survive to spawn (Patterson et al. 2007; Hinch and Martins 2011). It is therefore expected that transgenerational effects of stress will become increasingly prevalent and could lead to additional declines in sockeye salmon abundance and productivity in the Fraser River. Accordingly, further research is needed to examine subsequent aspects of transgenerational stress that could affect the overall fitness of future generations of Fraser River sockeye salmon. A number of additional experiments should be conducted to build on the results from this study and enhance the current understanding of the effects of transgenerational stress in Fraser River sockeye salmon. Juvenile survival through the later stages of life must be monitored completely. Evaluating the swimming capability of juveniles from stressed mothers will aid in assessing how well offspring can successfully reach their nursery lakes. Behavioural studies of feeding and aggression in juveniles that ultimately affect survival in the wild should be conducted. Examination of the compromising capability of parental stress on the juvenile stress response is essential to determine how offspring will cope with increasingly stressful  24 environmental conditions. Effects on osmoregulation and smoltification should be examined to monitor how offspring from stressed parents cope with the transition to seawater. Additionally, sampling for contaminants and disease should include both parents and offspring (Peterman et al. 2010). To more fully comprehend transgenerational effects of stress in Fraser River sockeye salmon, all studies should be paired with gene expression to investigate the parameter of interest (Peterman et al. 2010).            References Auperin, B., and M. Geslin. 2008.  Plasma cortisol response to stress in juvenile rainbow trout is influenced by their life history during early development and by egg cortisol.  Barton, B.A. 2002. Stress in fishes: a diversity of responses with particular reference to changes in circulating corticosteroids. Integrative and Comparative Biology 42: 517-525. Boyd, J.W., E.W. Oldenburg, and G.A. McMichael. 2010. Color photographic index of fall Chinook salmon embryonic development and accumulated thermal units.  PLoS ONE 7: 1-10.  British Columbia. 2010. Sport Fishing. Website. Available from (Accessed 1/04/12) Bromage, N.R., J. Jones, C. Randall, M. Thrush, B. Davies, J. Springate, J. Duston, and G. Barker. 1992. Broodstock management, fecundity, egg quality and the timing of egg production in the rainbow trout (Oncorhynchus mykiss). Aquaculture 100: 141-166. Brooks, S., C.R. Tyler, J.P Sumpter. 1997. Egg quality in fish: what makes a good egg? Reviews in Fish Biology and Fisheries 7: 387-416. Buechler K, Fitze P.S., B. Gottstein, A. Jacot, and H. Richner. 2002. Parasite-induced maternal response in a natural bird population. Journal of Animal Ecology 71: 247-252. Burt, J.M., S.G. Hinch, and D.A. Patterson. 2012. Developmental temperature stress and parental identity shape offspring burst swimming performance in sockeye salmon (Oncorhynchus nerka). Ecology of Freshwater Fish 21: 176-188. Campbell P.M., T.G. Pottinger, and J.P Sumpter. 1994. Preliminary evidence that chronic confinement stress reduces the quality of gametes produced by brown and rainbow trout. Aquaculture 120: 151-169. Campbell P.M., T.G. Pottinger, and J.P. Sumpter. 1992. Stress reduces the quality of gametes produced by rainbow trout. Biology of Reproduction 47: 1140-1150.   25 Carruth L.L., R.E. Jones, and D.O. Norris. 2002. Cortisol and Pacific salmon: a new look at the role of stress hormones in olfaction and home-stream migration. Integrative and Comparative Biology 42: 574-581. Cederholm C.J., M.D. Kunze, T.Murota, and A. Sibatani. 1999. Pacific salmon carcasses: essential contributions of nutrients and energy for aquatic and terrestrial ecosystems. Fisheries 24: 6-15.  Charmandari, E., C. Tsigos, and G. Chrousos. 2005. Endocrinology of the stress response. Annual Review of Physiology 67: 259-284. Contreras-Sanchez, W.M. 1995. Effects of stress on the reproductive performance and physiology of rainbow trout Oncorhynchus mykiss. MSc thesis. Oregon State University. 60 pp. Cooke, S.J., S.G. Hinch, G.T. Crossin, D.A. Patterson, K.K. English, J.M. Shrimpton, G. Van Der Kraak, and A.P. Farrell. 2006. Physiology of individual late-run Fraser River sockeye salmon (Oncorhynchus nerka) sampled in the ocean correlates with fate during spawning migration. Canadian Journal of Fisheries and Aquatic Sciences 63: 1469-1480. COSEWIC (Committee on the Status of Endangered Wildlife in Canada). 2010. Canadian Wildlife Species at Risk.  Crossin, G.T., S.G. Hinch, S.J. Cooke, D.W. Welch, D.A. Patterson, S.R.M. Jones, A.G. Lotto, R.A. Leggatt, M.T. Mathes, J.M. Shrimpton, G. Van Der Kraak, and A.P. Farrell. Exposure of high temperature influences the behaviour, physiology, and survival of sockeye salmon during spawning migration. Canadian Journal of Zoology 86: 127-140.  Curno O, J.M. Behnke, A.G. McElligott, T. Reader, and C.J. Barnard. 2009. Mothers produce less aggressive sons with altered immunity when there is a threat of disease during pregnancy. Proceedings of the Royal Society 276: 1047-1054. Davis, A.M., S.C. Ward, M. Selmanoff, A.E. Herbison, and M.M. McCarthy. 1999. Developmental sex differences in amino acid neurotransmitter levels in hypothalamic and limbic areas of the rat brain. Neuroscience 90: 1471-1482. de Jesus, E.G., T. Hirano, and Y. Inui. 1991. Changes in cortisol and thyroid hormone concentrations during early development and metamorphosis in the Japanese flounder Paralichthys olivaceus. General and Comparative Endocrinology 82: 369-376. Denver, R.J. 2009. Structural and functional evolution of vertebrate neuroendocrine stress systems. Trends in Comparative Endocrinology and Neurobiology: Annals of the New York Academy of Science 1163: 1-16.   26 Drake, A.J., B.R. Walker, and J.R. Seckl. 2004. Intergenerational consequences of fetal programming by in utero exposure to glucocorticoids in rats. American Journal of Physiology: Regulatory, Integrative and Comparative Physiology 288: 34-38. Eriksen, M.S., A.M. Espmark, B.O. Braastad, R. Salte, and M. Bakken. 2007. Long-term effects of maternal cortisol exposure and mild hyperthermia during embryogeny on survival, growth and morphological anomalies in farmed Atlantic salmon Salmo salar offspring. Journal of Fish Biology 70: 462-473. Eriksen, M.S., G. Færevik, S. Kittilsen, M. I. McCormick, B. Damsgard, V. A. Braithwaite, B. O. Braastad, and M. Bakken. 2011. Stressed mothers – troubled offspring: a study of behavioural maternal effects in farmed Salmo salar. Journal of Fish Biology 575-586.  Eriksen, M.S., M. Bakken, A.M. Espmark, B.O. Braastad, and R. Salte. 2006. Prespawning stress in framed Atlantic salmon Salmo salar: materncal cortisol exposure and hyperthermia during embryonic development affect offspring survival, growth and incidence of malformations. Journal of Fish Biology 69: 114-129. Galbraith, R.V., E.A. MacIsaac, J.S. Macdonald, and A.P. Farrell. 2006. The effect of suspended sediment on fertilization success in sockeye (Oncorhynchus nerka) and coho (Oncorhynchus kisutch) salmon. Canadian Journal of Fisheries and Aquatic Sciences 63: 2487-2494.     Giesing E.R., C.D. Suski, R.E. Warner, and A.M. Bell. In press. Female sticklebacks transfer information via eggs: effects of maternal experience with predators on offspring. Proceedings of the Royal Society doi:10.1098/rspb.2010.1819. Groot C, and L. Margolis (Eds). 1991. Pacific Salmon Life Histories. University of British Columbia Press, Vancouver. Groothuis, T.G., W. Muller, N. von Engelhardt, C. Carere, and C. Eising. 2005. Maternal hormones as a tool to adjust offspring phenotype in avian species. Neuroscience. Biobehavioral Review29: 329-352.  Hane S, and O.H. Roberson.1959. Changes in plasma 17-hydroxycorticosteroids accompanying sexual maturation and spawning of the Pacific salmon (Oncorhynchus tschawytscha) and rainbow trout (Salmo gairdnerii). Proceedings of the National Academy of Sciences 45: 886-893. Haussman, M.F., A.S. Longnecker, N.M. Marchetto, S.A. Juliano, R.M. Bowden. 2011. Embryonic exposure to corticosterone modifies the juvenile stress response, oxidative stress and telomere length. Proceedings of the Royal Society. Biological Sciences.  27 Helfield, J. M., and R.J. Naiman. 2001. Effects of salmon-derived nutrients on riparian forest growth and implications for stream productivity. Ecology, 82, 2403-2409. Hinch, S.G., and E.G. Martins. 2011. A review of potential climate change effects on survival of Fraser River sockeye salmon and an analysis of interannual trends in en route loss and pre-spawn mortality. Cohen Commission Technical Report 9: 134p. Vancouver, B.C. Hinch, S.G., S.J. Cooke, M.C. Healey, and A.P. Farrell. 2006. Behavioural physiology of fish migrations: salmon as a model approach. In: Sloman K, S. Balshine, and R. Wilson (Eds) Fish Physiology 24: Behaviour and Physiology of Fish. Elsevier Press, San Diego, pp. 239-295. Hopkins W.A., S.E. DuRant, B.P. Staub, C.L. Rowe, and B.P. Jackson. 2006. Reproduction, embryonic development, and maternal transfer of contaminants in the amphibian Gastrophryne carolinesis. Environmental Health Perspectives 114: 661-666. Hoysak, D.J., and N.R. Liley. 2001. Fertilization dynamics in sockeye salmon and a comparison of alternative male phenotypes. Journal of Fisheries Biology 58: 1286-1300. Hruska K.A., S.G. Hinch, M.C. Healey, D.A. Patterson, S. Larsson, and A.P. Farrell. 2010. Influences of sex and activity level on physiological changes in individual adult sockeye salmon during rapid senescence. Physiological and Biochemical Zoology 83: 663-676.  Hwang P, S. Wu, and J. Lin. 1992. Cortisol content of eggs and larvae in teleosts. General and Comparative Endocrinology 86: 189-196.  Idler, D.R., A.P. Ronald, and P.J. Schmidt. 1962. Biochemical studies on sockeye salmon during migration: VII. Steroid hormones in plasma. Canadian Journal of Biochemistry and Physiology 37: 1227-1238. Jabob, C., T. McDaniels, and S. Hinch. 2010. Indigenous culture and adaptation to climate change: sockeye salmon and the St’át’imc people. Mitigation and Adaptation Strategies for Global Change 15: 859-876. Khan, A.T., and J. Weis. 1987. Toxic effects of mercuric chloride on sperm and egg viability of two population of Mummichog, Fundulus heteroclitus. Environmental Pollution 48: 263- 273. Khan, A.T., and J. Weis. 1993. Differential effects of organic and inorganic mercury on the micropyle of the eggs of Fundulus heteroclitus. Environmental Biology of Fishes 37: 323-327. Kristianson, G., and D. Strongitharm. 2006. The evolution of recreational salmon fisheries in British Columbia. Pacific Fisheries Resource Conservation Council, Vancouver, BC.  28 Li M, Bureau DP, King WA, Leatherland JF. 2010. The actions of in ovo cortisol on egg fertility, embryo development and the expression of growth-related genes in rainbow trout embryos, and the growth pefromance of juveniles. Molecular Reproduction & Development 77, 922-931. Liley, N.R., P. Tamkee, R. Tsai, and D.J. Hoysak. 2002. Fertilization dynamics in rainbow trout (Oncorhynchus mykiss): effect of male age, social experience, and sperm concentration and motility on in vitro fertilization. Canadian Journal of Fisheries and Aquatic Sciences 59: 144-152. Lindqvist, C, A.M. Janczak, D. Nätt, I. Baranowska, N. Lindqvist, A. Wichman, J. Lundeberg, J. Lindberg, P.A. Torjsen, and P. Jensen. 2007. Transmission of stress-induced learning impairment and associated brain gene expression from parents to offspring in chickens. PLoS One 4, e364-  Macdonald, J.S., M.G.G. Foreman, T. Farrell, I.V. Williams, J. Grout, A. Cass, J.C. Woodey, H. Enzenhofer, W.C. Clarke. R. Houtman, E.M. Donaldson, and D. Barnes. 2000. The influence of extreme water temperatures on migrating Fraser River sockeye salmon (Oncorhynchus nerka) during the 1998 spawning season. Canadian Technical Report of Fisheries and Aquatic Sciences 2326: 117p.  McCormick MI, Nechaev IV. 2002. Influence of cortisol on developmental rhythms during embryogenesis in a tropical damselfish. Journal of Experimental Zoology 293, 456-466. McCormick MI. 1999. Experimental test of the effect of maternal hormones on larval quality of a coral reef fish. Oecologia 118, 412-422. McEwen, B. S. 1998. Stress, adaptation, and disease: allostasis and allostatic load. Annals of the New York Academy of Sciences 840: 33–44. Milla, S, B. Jalabert, H. Rime, P. Prunet, and J. Bobe. 2006. Hydration of rainbow trout oocyte during meiotic maturation and in vitro regulation by 17,20β-dihydroxy-4 pregnen-3-one and cortisol. Journal of Experimental Biology 209: 1147-1156. Mingist, M., T. Kitani, N. Koide, and H. Ueda. 2007. Relationship between eyed-egg percentage and levels of cortisol and thyroid hormone in masu salmon Oncorhynchus masou. Journal of Fish Biology 70: 1045-1056. Moberg, G.P., J.A. Mench (Eds). 2000. The Biology of Animal Stress: Assessment and Implications for Welfare. CAB International, Wallingford, pp. 1-2.   Moccia, R.D., and K.R. Munkittrick. 1987. Relationship between the fertilization of rainbow trout (Salmo gairdneri) eggs and the motility of spermatozoa. Theriogenology 27: 679- 689.  29 Mommsen T.P., M.M. Vijayan, and T.W. Moon. 1999. Cortisol in teleosts: dynamics, mechanisms of action and metabolic regulation. Reviews in Fish Biology and Fisheries 9: 211-268.   Moore, I.T., and T.S. Jessop. 2003. Stress, reproduction, and adrenocortical modulation in amphibians and reptiles. Hormones and Behavior 43: 39-47. Nadeau, P.S. 2007. Parental contribution to the early life history traits of juvenile sockeye salmon (Oncorhynchus nerka): the roles of spawner identity and migratory experience. MSc thesis. University of British Columbia, Canada. Naguib M, and D. Gil. 2005. Transgenerational effects on body size caused by early developmental stress in zebra finches. Biology Letters 1, 95-97. O’Reilly, K.M., and J.C. Wingfield. 2001. Ecological factors underlying the adrenocortical response to capture stress in Arctic breeding shorebirds. General and Comparative Endocrinology 124: 1-11. Painter R.C., T.J. Roseboom, and O.P. Bleker. 2005. Prenatal exposure to the Dutch famine and disease in later life: an overview. Reproductive Toxicology 20, 345-352. Patterson, D.A. 2004. Relating the sockeye salmon (Oncorhynchus nerka) spawning migration experience with offspring fitness: A study of intergenerational effects. M.Sc. Thesis, Simon Fraser University, Canada.  Patterson, D.A., H. Guderley, P. Bouchard, J.S. Macdonald, and A.P. Farrell. 2004. Maternal influence and population differences in activities of mitochondrial and glycolytic enzymes in emergent sockeye salmon (Oncorhynchus nerka) fry. Canadian Journal of Fisheries and Aquatic Sciences 61: 1225-1234.  Patterson, D.A., J.S. Macdonald, K.M. Skibo, D.P. Barnes, I. Guthrie, and J. Hills. 2007. Reconstructing the summer thermal history for the lower Fraser River, 1941 to 2006, and implications for adult sockeye salmon (Oncorhynchus nerka) spawning migration. Canadian Technical Report of Fisheries and Aquatic Sciences.   Patterson, D.A., J.S. Macdonald, S.G. Hinch, M.C. Healey, and A.P. Farrell. 2004. The effect of exercise and captivity on energy partitioning, reproductive maturation, and fertilization success in adult sockeye salmon. Journal of Fish Biology 64: 1-21.  Peterman R.M., D. Marmorek, B. Beckman, M. Bradford, N. Mantua, B.E. Riddell, M. Scheuerell, M. Staley, K. Wieckowski, J.R. Winton, and C.C. Wood. 2010. Synthesis of evidence from a workshop on the decline of Fraser River sockeye. June 15-17, 2010. A Report to the Pacific Salmon Commission, Vancouver, B.C., 123 pp.    30 Quinn, T.P. 2005. The behaviour and ecology of Pacific salmon and trout. University of Washington Press, Seattle. Rivier, C. and S. Rivest. 1991. Effects of stress on the activity of the hypothalamic-pituitary- gonadal axis: peripheral and central mechanisms. Biology of Reproduction 45: 523-532. Romero, L.M. 2002. Seasonal changes in plasma glucocorticoid concentrations in free-living vertebrates. General and Comparative Endocrinology 128: 1-24 Romero, L.M. 2004. Physiological stress in ecology: lessons from biomedical research.  TRENDS in Ecology and Evolution 19: 249-255. Rubolini, D., M. Romano, G. Boncoraglio, R.P. Ferrari, R. Martinelli, P. Galeotti, M. Fasola, and N. Saino. 2005. Effects of elevated egg corticosterone levels on behavior growth immunity of yellow-legged gull (Larus michahellis) chicks. Hormones and. Behavior 47: 592-605.   Rurangwa, E., D.E. Kime, F. Ollevier, and J.P. Nash. 2004. The measurement of sperm motility and factors affecting sperm quality in cultured fish. Aquaculture 234: 1-28. Sampath-Kumar, R., R.E. Byers, A.D. Munro, and T.J. Lam. 1995. Profile of cortisol during the ontogeny of the Asian seabass, Lates calcarifer. Aquaculture 132: 349-359. Sampath-Kumar, R., S.T.L. Lee, C.H. Tan, A.D. Munro, T.J. Lam. 1997. Biosynthesis in vivo and excretion of cortisol by fish larvae. Journal of Experimental Zoology 277A: 337-344. Sapolsky, R.M., L.M. Romero, A.U. Munck. 2000. How do glucocorticoids influence stress responses? Integrating permissive, suppressive, stimulatory and preparative actions. Endocrine Reviews 21: 55-89.  Schluter, D. 1994. Experimental evidence that competition promotes divergence in adaptive radiation. Science 266, 798-801. Schreck, C.B., W. Contreras-Sanchez, and M.S. Fitzpatrick. 2001. Effects of stress on fish reproduction, gamete quality, and progeny. Aquaculture 197: 3-24. Sheriff M.J., C.J. Krebs, R. Boonstra. 2009. The sensitive hare: sublethal effects of predator stress on reproduction in snowshoe hares. Journal of Animal Ecology 78: 1249-1258. Shine R, and S.J. Downes. 1999. Can pregnant lizards adjust their offspring phenotypes to environmental conditions? Oecologia 119: 1-8.  Sire, M.F., P.J. Babin, and J.M. Vernier. 1994. Involvement of the lysosomal system in yolk protein deposit and degradation during vitellogenesis and embryonic development in trout. Journal of Experimental Zoology 269: 69-83.  31 Sloman KA. 2010. Exposure of ova to cortisol pre-fertilisation affects subsequent behaviour and physiology of brown trout. Hormones and Behavior 58: 433-439. Stratholt M.L., E.M. Donaldson, N.R. Liley. 1997. Stress induced elevation of plasma cortisol in adult female coho salmon (Oncorhynchus kisutch), is reflected in egg cortisol content, but does not appear to affect early development. Aquaculture 158: 141-153.  Tilbrook, A.J., A.I. Turner, and I.J. Clarke. 2000. Effects of stress on reproduction in non-rodent mammals: the role of glucocorticoids and sex differences. Reviews of Reproduction 5: 105-113.  Velsen, F.J. 1980. Embryonic development in eggs of sockeye salmon, Oncorhynchus nerka. Canadian Journal of Fisheries and Aquatic Science Special Publication 49: 1-19. Williams, A .2007. The pacific salmon treaty: a historical analysis and prescription for the future. Journal of Environmental Law and Litigation 22:153–195. Wingfield, J. C., D.L. Maney, C.W. Breuner, J.D. Jacobs, S. Lynn, M. Ramenofsky, and R.D. Richardson. 1998. Ecological bases of hormone – behavior interactions: the ‘emergency life history stage’. American Zoology 38: 191-206.  Wingfield, J.C., and R.M. Sapolsky. 2003. Reproduction and resistance to stress: when and how. Journal of Neuroendocrinology 15: 711- 724. Wingfield, J.C., K. Hunt, C. Breuner, K. Dunlap, G.S. Fowler, L. Freed, and J. Lepson. 1997. Environmental stress, field endocrinology, and conservation biology. In: Behavioral Approaches to Conservation in the Wild. Clemmons, J.R., and R. Buchholz (eds). London: Cambridge University Press; pp. 95-131. 


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