(DRAFT) - Taxonomy
                               Species salmon, chinook
                                 Species Id M010030
                                   Date 26 AUG 96



TAXONOMY

NAME - salmon, chinook OTHER COMMON NAMES - king salmon, tyee, spring, blackmouth, spring salmon, tule and quinnat ELEMENT CODE - CATEGORY - Fish PHYLUM AND SUBPHYLUM - Chordata, CLASS AND SUBCLASS - Osteichthyes, ORDER AND SUBORDER - Salmoniformes, FAMILY AND SUBFAMILY - Salmonidae, GENUS AND SUBGENUS - Oncorhynchus, SPECIES AND SSP - tshawytscha, SCIENTIFIC NAME - Oncorhynchus tshawytscha AUTHORITY - Walbaum TAXONOMY REFERENCES - 89 and 232 COMMENTS ON TAXONOMY - Other common names include king salmon, tyee, spring, and blackmouth *11*. Common names include king salmon, spring salmon, tyee, tule, quinnat, and blackmouth *232*. Caution must be used when extending information from one stock of chinook salmon to another stock. Environmental conditions for one area must not be treated as absolute; the stocks (races) have acclimated or evolved over time and space to habitat conditions that can vary greatly *232*. Taxonomy - 1
                                  (DRAFT) - Status
                               Species salmon, chinook
                                 Species Id M010030
                                   Date 26 AUG 96



STATUS

Coded Status T: Federal Threatened Sport Fish Commercial Commercial/consumption Migrant Existing, FMP exists See Comments REFERENCES FOR STATUS - 89, 232 and 274 COMMENTS ON STATUS - Chinook salmon represent an extremely important component of both the commercial and sport fisheries of the Pacific Northwest. Charter boat fisheries exist along the Pacific coast from San Francisco to Alaska. Chinook and coho salmon support extensive troll fisheries over the same latitudes, but trollers additionally fish well out into the Fishery Conservation Zone (3-200 mi offshore). Catch statistics indicate a decline in the commercial catch of chinook salmon over time. Despite this decline, inflation more than tripled the value of the catch between 1970 and 1980. Although chinook salmon represent only 9% to 13% of the total commercial salmon catch, they are the most important in terms of market value and preference. Troll-caught fresh or fresh-frozen chinook salmon in the 11-18 lb size range are the most highly preferred salmon by market buyers. Among the Pacific states and Provinces, British Columbia contributed the largest percentage (27%) of the chinook commercial and sport catch for the years 1953-1957 *89*. Chinook salmon are migratory *232*. MANAGERIAL AUTHORITY: The Alaska Board of Fisheries develops regulations governing the commercial, sport, and subsistence harvest of salmon in Alaska. The Alaska Department of Fish and Game manages salmon populations in the fresh waters of the state and the marine waters to the 3-mi limit *232*. The North Pacific Fishery Management Council is composed of 15 members, 11 voting and 4 nonvoting members. The 11 are divided as follows: 5 from Alaska, 3 from Washington, 3 from state fishery agencies (Alaska, Washington, Oregon). The four nonvoting members include the director of the Pacific Marine Fisheries Commission; the director of the U.S. Fish and Wildlife Service; the commander, 17th Coast Guard District; and a representative from the U.S. Department of State. The council prepares fishery management plans, which become federal law and apply to marine areas between the 3-mi limit and the 200-mi limit. With regard to salmon, the only plan prepared to date is the Salmon Power Troll Fishery Management Plan *232*. The International North Pacific Fisheries commission (INPFC), a convention Status - 1 (DRAFT) - Status Species salmon, chinook Species Id M010030 Date 26 AUG 96 comprised of Canada, Japan, and the United States, has been established to provide for scientific studies and for coordinating the collection, exchanges, and analysis of scientific data regarding anadromous species. With regard to salmon, the INPFC has also prepared conservation measures that limit the location, time, and number of fishing days that designated high seas (beyond the 200-mi limit) areas may fished by Japanese nationals and fishing vessels *232*. Status - 2
                               (DRAFT) - Distribution
                               Species salmon, chinook
                                 Species Id M010030
                                   Date 26 AUG 96



DISTRIBUTION

Distribution - 1
     

HABITAT ASSOCIATIONS

HABITAT - AQUATIC REFERENCES FOR HABITAT - 89 NATIONAL WETLAND INVENTORY CODES NWI NWICLS NWIMOD NWISPEC Estuarine UB1 L 0 Estuarine UB2 L 0 Estuarine UB3 L 0 Estuarine UB4 L 0 Estuarine UB. L 9 Marine V 1 Marine V 1 Riverine SB1 H 0 Riverine RB2 H 0 Riverine SB3 N 1 Riverine, upper perennial SB1 H 0 REFERENCES FOR NWI - 89 Habitat Associations - 1
                                (DRAFT) - Food Habits
                               Species salmon, chinook
                                 Species Id M010030
                                   Date 26 AUG 96



FOOD HABITS

TROPHIC LEVEL - CARNIVORE REFERENCES FOR TROPHIC LEVEL - 89 and 232 LIFESTAGE FOOD FOOD PART Larva Microorganisms See Comments Juvenile Copepods Not Specified Juvenile Insects Not Specified Adult Osteichthyes Not Specified Adult Clupeiformes Not Specified Juvenile Osteichthyes Larva stage Adult Copepods Not Specified Adult Insects Not Specified Juvenile Plankton Not Specified Juvenile Insects: aquatic Larva stage Juvenile Insects:terrestrial Not Specified Juvenile Salmoniformes Egg/Fetus stage Juvenile Arachnids Not Specified Juvenile Invertebrate Cordates Not Specified Juvenile Diptera Larva stage Juvenile Diptera Pupa stage Juvenile Diptera Adult stage Juvenile Crustaceans Larva stage Juvenile Malacostraca Larva stage Juvenile Malacostraca Not Specified Juvenile Copepods Not Specified Juvenile Crustaceans Not Specified Juvenile Branchiopods Not Specified Juvenile Cirripeds Not Specified Juvenile Osteichthyes Not Specified Juvenile Perciformes Not Specified Juvenile Clupeiformes Not Specified Adult Osteichthyes Not Specified Adult Crustaceans Not Specified Adult Malacostraca Not Specified Adult Molluscs Not Specified Adult Squid, Octopus Not Specified Adult Malacostraca Not Specified Adult Malacostraca Larva stage Adult Osteichthyes Not Specified Adult Clupeiformes Not Specified Adult Perciformes Not Specified General Crustaceans Not Specified General Malacostraca Not Specified Juvenile See Comments; Food See Comments Adult See Comments; Food See Comments General See Comments; Food See Comments REFERENCES FOR GENERAL FOOD - 89 and 232 Food Habits - 1 (DRAFT) - Food Habits Species salmon, chinook Species Id M010030 Date 26 AUG 96 REFERENCES FOR IMPORTANT FOOD - 89 REFERENCES FOR ADULT FOOD - 89 and 232 REFERENCES FOR JUVENILE FOOD - 89 and 232 REFERENCES FOR LARVAE FOOD - 89 COMMENTS ON FOOD - Chinook salmon primarily eat fish, except during the spring when invertebrates (especially euphausids) are extremely abundant. In late winter and early spring off San Francisco, chinook feed on herring, rockfish, other fish, crab megalops, and squid. Euphausids and squid, and later, herring, crab megalops, and rockfish comprise the spring diet. In late spring through summer, rockfish dominate the diet, distantly followed by other fishes and some invertebrates. Anchovies are the dominant diet item for the remainder of the year. Chinook salmon frequent the waters of southeast Alaska throughout the year and feed heavily on herring, smelt, and eulachon. During the winter they move deeper and feed on halibut, rockfish, cod, and octopi *89*. Types of Feeding Areas Used: Juveniles feed in low-velocity areas of streams and rivers, such as riverbank pools formed by bank irregularities and in the pools below riffles, where drifting invertebrate material provides a ready food supply. During the first year at sea, the young fish stay near shore. During the second and subsequent years, chinook salmon are far-ranging, undertake extensive migration, and are found over a wide range of depths, from surface waters to depths exceeding 100 m. It is not unusual to encounter them at depths ranging from 20 to 110 m *232*. Factors Limiting Availability of Food: Sedimentation is one of the major factors that affects freshwater food availability. Excessive sedimentation may inhibit production of aquatic plants and invertebrate fauna. Primary food production is lowered above levels of 25 JTU (Jackson Turbidity Unit) and visual references lost above levels of 30 JTU *232*. Feeding Behavior: Chinook salmon are opportunistic feeders. Food consumption is related directly to the types and abundance of items available, although juvenile chinook salmon in fresh water do not seem to utilize fish as food. Upon returning to fresh water, adult salmon no longer feed but live off the fat stored up in the ocean *232*. COMMENTS ON ADULT FOOD - Chinook salmon primarily eat fish, except during the spring when invertebrates (especially euphausids) are extremely abundant. In late winter and early spring off San Francisco, chinook feed on herring, rockfish, other fish, crab megalops, and squid. Euphausids and squid, and later, herring, crab megalops, and rockfish comprise the spring diet. In late spring through summer, rockfish dominate the diet, distantly followed by other fishes and some invertebrates. Anchovies are the dominant diet item for the remainder of the year. Chinook salmon frequent the waters of southeast Alaska throughout the year and feed heavily on herring, smelt, and eulachon. During the winter they move deeper and feed on halibut, rockfish, Food Habits - 2 (DRAFT) - Food Habits Species salmon, chinook Species Id M010030 Date 26 AUG 96 cod, and octopi *89*. Adults eat fish, squid, euphasiids, shrimps, and crab larvae. Fishes make up the bulk (97%) of the food of marine adults, with herring and sand lance being the most frequently eaten. Crustaceans (composed dominantly of euphasiids but including young crabs, crab megalops, and other miscellaneous forms) are eaten in considerable numbers in the spring months (May and June). The diet of adult chinook salmon at sea is related to the types and abundance of food items available *232*. COMMENTS ON JUVENILE FOOD - Juvenile chinook are characterized as opportunistic drift and benthic feeders, primarily eating insects in the stream-rearing phase of life. As the young chinook salmon grow and move farther in to the marine environment, their diet includes crab zoea, Pacific sand lance, eulachon, copepods, euphausids, cephalopods, isopods, and amphipods. Upon entering the estuary, chinook utilize a wide range of invertebrate prey while retaining their insectivorous feeding habits. Gammarid amphipods, insects, mysids, isopods, copepods, and fish larvae comprise the bulk of the estuarine chinook juvenile diet *89*. Following emergence from the redd and while still in fresh water, juveniles feed on plankton, aquatic insect larvae, terrestrial insects, salmon eggs, and spiders. They are characterized as opportunistic drift and benthic feeders. Juvenile chinook salmon food habitat studies during August and September in sloughs and clearwater tributaries of the middle reach of the Susitna RIver suggest that the range and diversity of invertebrates in their diet indicate an ability to adopt to variable conditions. Specimens collected during the study had consumed both terrestrial and aquatic invertebrates. Midges (Diptera: Chironomidae) were the numerically dominant taxa and were consumed as larvae, pupae, and adults. Chironomid adults and terrestrial invertebrates caught on the water surface, as opposed to immature insects drifting in the water column, were often an important food item for juvenile chinook salmon. Upon migration to the sea, young chinook salmon eat crab larvae, amphipods, copepods, euphasiids, cladocerans, barnacles, and a variety of small fish, such as sand lance, eulachon, herring, rockfish, and smooth tongue *232*. Types of Feeding Areas Used: Juveniles feed in low-velocity areas of streams and rivers, such as riverbank pools formed by bank irregularities and in the pools below riffles, where drifting invertebrate material provides a ready food supply. During the first year at sea, the young fish stay near shore *232*. COMMENTS ON LARVAE FOOD - Alevins absorb a yolk sac before emerging as free-swimming fry *89*. Upon hatching, young alevin remain in the gravel for two to three weeks until the yolk sac has been absorbed *232*. Food Habits - 3
                         (DRAFT) - Environment Associations
                               Species salmon, chinook
                                 Species Id M010030
                                   Date 26 AUG 96



ENVIRONMENTAL ASSOCIATIONS

G = General A = Adult LIM = Limiting RA = Resting Adult J = Juvenile FA = Feeding Adult RJ = Resting Juvenile BA = Breeding Adult FJ = Feeding Juvenile P = Pupae L = Larvae E = Egg RL = Resting Larvae FL = Feeding Larvae
LIFESTAGE ENVIRONMENTAL ASSOCIATIONS G Water Temperature: Below 15 degrees C E Water Temperature: Below 15 degrees C A Water Temperature: Specified in Comments G Dissolved Oxygen: Moderate [5-7 mg/l] oxygen concentrations G Turbidity: Clear water G Relation to Substrate: Unattached - normally free living J Substrate: Rocks A Substrate: Mud or silt A Substrate: Rocks G Bottom Type [Aquatic]: Mud or silt A Bottom Type [Aquatic]: Sand A Bottom Type [Aquatic]: Gravel J Bottom Type [Aquatic]: Boulders G Water Velocity [Instream Flow Group Increments]: Specified in Comments G Water Depth Preference: Specified in Comments REFERENCES FOR ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR LIMITING ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR FEEDING ADULT ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR RESTING ADULT ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR BREEDING ADULT ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR FEEDING JUVENILE ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR RESTING JUVENILE ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR FEEDING LARVAE ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR RESTING LARVAE ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR PUPAE ENVIRONMENTAL ASSOC_ - 89 REFERENCES FOR EGG ENVIRONMENTAL ASSOC_ - 89 Environment Associations - 1 (DRAFT) - Environment Associations Species salmon, chinook Species Id M010030 Date 26 AUG 96 COMMENTS ON ENVIRONMENTAL ASSOCIATIONS - Temperature: Adult spring chinook can survive in deep pools in the summer with the surface temperature 23.0 deg C, but cannot spawn above 22.0 deg C. Upper lethal temperature for chinook salmon is 25.1 deg C. Salinity: Chinook salmon have been associated with salinities from 6.75 to 25.73 ppt in the Straits of Georgia off the Fraser River plume. Dissolved oxygen: Chinook salmon can survive when resting with dissolved oxygen levels as low as 2.0 mg/l and could swim against 0.8 ft/s current for a day when dissolved oxygen concentrations were 3.0 mg/l. Depth: The preferred depth for spawning is >0.24 m to 10 m for spring and fall chinook and >0.30 m for summer chinook. Upstream migrations are generally triggered by rains, which raise the river levels and change the water temperature. Water movement: A 70 mm chinook can maintain a home station facing velocities of 0.23 m/s but lie under a layer of 0.45 m/s water and be surrounded by velocities of 0.6 m/s. Turbidity: Salmonid fishes will cease movement or migration in streams with high silt loads (>4000 mg/l). Study has shown that exposure to low levels of volcanic ash in a Y-test chamber caused chinook salmon to exhibit significant avoidance reactions. Because turbid water absorbs more radiation than clear water, a thermal barrier to movement and migration may also develop. Substrate: No substrate preference has been documented for adults in the marine environment *89*. COMMENTS ON RESTING ADULT ENVIRONMENTAL ASSOC_ - Temperature: Adult spring chinook can survive in deep pools in the summer with the surface temperature 23.0 deg C, but cannot spawn above 22.0 deg C. Upper lethal temperature for chinook salmon is 25.1 deg C. Salinity: Chinook salmon have been associated with salinities from 6.75 to 25.73 ppt in the Straits of Georgia off the Fraser River plume. Dissolved oxygen: Chinook salmon can survive when resting with dissolved oxygen levels as low as 2.0 mg/l and could swim against 0.8 ft/s current for a day when dissolved oxygen concentrations were 3.0 mg/l. Depth: The preferred depth for spawning is >0.24 m to 10 m for spring and fall chinook and >0.30 m for summer chinook. Upstream migrations are generally triggered by rains, which raise the river levels and change the water temperature. Water movement: A 70 mm chinook can maintain a home station facing velocities of 0.23 m/s but lie under a layer of 0.45 m/s water and be surrounded by velocities of 0.6 m/s. Turbidity: Salmonid fishes will cease movement or migration in streams with high silt loads (>4000 mg/l). Study has shown that exposure to low levels of volcanic ash in a Y-test chamber caused chinook salmon to exhibit significant avoidance reactions. Because turbid water absorbs more radiation than clear water, a thermal barrier to movement and migration may also develop. Substrate: No substrate preference has been documented for adults in the marine environment *89*. COMMENTS ON BREEDING ADULT ENVIRONMENTAL ASSOC_ - Temperature: The recommended temperatures for spawning range between 5.6 and 13.9 deg C. Adult spring chinook can survive in deep pools in the Environment Associations - 2 (DRAFT) - Environment Associations Species salmon, chinook Species Id M010030 Date 26 AUG 96 summer with the surface temperature 23.0 deg C, but cannot spawn above 22.0 deg C. Dissolved oxygen: Although migrating adult chinook salmon encounter dissolved oxygen levels of 3.0 to 4.0 ppm in the Duwamish River Estuary, it could not be demonstrated that this impeded the spawning migration of chinook salmon. Substrate: Adult chinook salmon spawn in gravel ranging from 6 cm to 14 cm in diameter. Gravel substrates from 1.3 cm to 10.2 cm in diameter have been listed in the literature as acceptable for spawning. Depth: Chinook salmon will spawn in rivers with depths of 0.10 m to 10 m. The preferred depth for spawning is >0.24 m for spring and fall chinook salmon and >0.30 m for summer chinook. Water movement: Chinook salmon require enough current on spawning beds to ventilate the eggs during incubation *89*. COMMENTS ON RESTING JUVENILE ENVIRONMENTAL ASSOC_ - Temperature: Optimum temperature for fingerlings is 17.0 deg C. Salinity: Juvenile chinook salmon encounter a wide range in salinity when moving from freshwater through an estuary and into the marine environment. Estuaries normally maintain a freshwater lens above the area of saltwater intrusion that smolts tend to occupy during the initial stages of their estuary and marine residence. Dissolved oxygen: A marked avoidance of oxygen concentrations at or below 4.5 mg/l by juvenile chinook in the summer at 20.0 deg C has occurred. Decreased avoidance occurred in the fall as temperatures declined or as dissolved oxygen concentrations rose above 4.5 mg/l, with no avoidance noted at 6.0 mg/l. Substrate: Spring chinook juveniles that overwinter in freshwater require large boulder habitat for winter refuge areas. However, they prefer different habitats than do steelhead. In the estuaries, juvenile chinook salmon show a wide range of substrate associations including mud, sand, gravel, and eelgrass. Depth: Juvenile chinook salmon prefer deeper water (>0.5 m) than steelhead in the same streams. Juvenile chinook occupy the water near the surface during their initial marine stages and then utilize water down to 60 m. Water movement: Juvenile chinook can detect and orient in water velocities of 0.005 m/s. Turbidity: Excessive amounts of sand and silt may limit production of benthic invertebrates necessary for optimum rearing of juvenile fish. Chinook salmon smolts may be quite tolerant of high concentrations of volcanic ash and mudflow sediments. 96-hr LC50 values for these fish have been determined to be 11,000 mg/l. Sublethal sediment concentrations did not produce consistant effects on swimming performance or fatigue velocity. Chinook smolts were much less tolerant of seawater after exposure to high concentrations of volcanic ash and mudflow sediments, but low level exposure did not affect them. Gill tissues revealed only minor effects even at the highest exposure concentrations, but death at high concentrations of these materials was caused by hypoxia. Behavioral reactions to high suspended solid concentrations were identical to responses to low dissolved oxygen: the fish stayed near the surface *89*. COMMENTS ON RESTING LARVAE ENVIRONMENTAL ASSOC_ - Temperature: Optimum temperature for chinook fry is 11.0 deg C. Environment Associations - 3 (DRAFT) - Environment Associations Species salmon, chinook Species Id M010030 Date 26 AUG 96 Turbidity: Fry emergence from the gravel may be hindered by excessive amounts of sand and silt *89*. COMMENTS ON EGG ENVIRONMENTAL ASSOC_ - Temperature: Optimum temperature for chinook eggs is 11.0 deg C. Dissolved oxygen: Chinook eggs require dissolved oxygen concentrations of 5.0 mg/l. Water movement: Chinook salmon require enough current on the spawning beds to ventilate the eggs during incubation *89*. Environment Associations - 4
                               (DRAFT) - Life History
                               Species salmon, chinook
                                 Species Id M010030
                                   Date 26 AUG 96



LIFE HISTORY

MORPHOLOGY: Dorsal fin (10-14 rays), adipose stout and fleshy, anal (13-19), pelvic (10), abdominal with a free-tipped fleshy appendage above its insertion. Cycloid scales. Gill rakers (18-30) rough and widely spaced on first gill arch. Body elongate, moderate, lateral compression. IDENTIFICATION AIDS: Tail moderately forked with stiff outer rays. Moderately large irregular black spots on back, upper sides, dorsal, adipose, and both lobes of the caudal fin. Black lower gum line. Juveniles: Parr marks appear as long vertical dark bars extending equally above and below the lateral line. Parr marks are wider than or equal to the width of spaces between marks. SPAWNING: Chinook salmon exhibit at least three distinct life history patterns. Spring chinook salmon populations occur in large river systems where enough flow is available over the summer to hold these fish. Spring-run fish may enter freshwater as early as February or March, but they usually spawn between August and November. These fish travel upstream slowly and remain for protracted periods in pools near the spawning grounds and typically spawn in the upper reaches of rivers. Summer chinook salmon enter the rivers from late spring through midsummer and hold in the river until they spawn in the fall. Fall-run chinook salmon enter both large rivers and small coastal streams in autumn. They generally move rapidly during high water periods to the spawning areas and commence spawning activities. Complete spawning normally occurs within 7 days after the initial breeding activity. Males are attracted by females digging and testing the gravel. When the female is satisfied with her excavation site, spawning proceeds. The female deposits a portion of her ova in the gravel depression while one primary male and possibly several subdominant males move alongside simultaneously to fertilize the eggs. Following each of these spawning acts, the female moves directly upstream to dig a new depression, which also covers the eggs fertilized in the preceeding act. The average depth of productive redds was reported to be 203 mm to 356 mm beneath the surface of the stream bed. Columbia River chinook constructed redds from 1.2 m to 10.7 m in diameter. Nest building commences earliest in the uppermost reaches of the river and progresses sequentially downstream as river temperatures drop to the levels encountered by the upstream spawners. When females have expended their ova, the males desert them and apparently search for additional matings until they are spawned out or die. Chinook salmon live 2 to 4 weeks after spawning. During this time, females will defend their redds and an area as wide as 6.1 m beyond the margin of the redd against other females, but they will normally ignore male chinook salmon. FECUNDITY, EGGS, AND ALEVINS: Female chinook salmon produce 3,000 to 6,000 eggs. Fecundity is size related, and higher in southern populations. Chinook salmon eggs are the largest of the Salmonidae. The eggs require an average of 882 to 991 temperature units for hatching (1 temperature unit = 1 degree Fahrenheit above freezing for a period of 24 hours), with fewer temperature units required for eggs incubated at lower temperatures. During the incubation period, substantial mortality may be incurred by redd disturbances from overspawning, fluctuating flows, dewatering, freezing, Life History - 1 (DRAFT) - Life History Species salmon, chinook Species Id M010030 Date 26 AUG 96 isolation, suffocation, and microbial infestation. Depending upon the temperature regime of the natal stream, eggs hatch in the late fall or early winter. The alevins remain in the gravel for 4 to 6 weeks until the yolk sac is absorbed. The alevins are initially negatively phototactic and migrate downward into the gravel. High CO2 levels may elicit a dispersal response within the gravel. When the yolk sac is nearly absorbed, the alevins begin to express positive rheotaxis. After yolk absorption, young chinook salmon generally emerge after dark as free-swimming fry. FRY AND SMOLTS: Fry spend 1 to 18 months in freshwater. Some fry migrate seaward immediately after emergence while others live in the stream for about a year before migrating downstream. Ninety percent of the juvenile chinook from the Sacramento River migrate downstream from the middle of January to the middle of March, and most enter saltwater by June of their first year (6 to 10 months following spawning) at an average length of 41 mm. Downstream fall migrants, including both fall- and spring-run juveniles, reach saltwater at an average length of 100 mm. In British Columbia, 78% of the chinook salmon migrate to sea as fry while the remaining 22% enter saltwater as yearlings. Some chinook populations, particularly from coastal streams, leisurely feed and migrate downstream rather than living in distinct reaches of the river for extended periods of time. Spring chinook salmon from the upper reaches of large rivers, such as the Columbia, exhibit the more familiar year-long freshwater rearing stage. In warmer months, young chinook are associated with velocities and depths in proportion to body size, shifting to faster, deeper waters as they grow. Chinook are primarily drift and benthic feeders. During the day the fish remain in a small home area. At night they settle to the bottom, usually after moving inshore. In early autumn, juvenile chinook salmon emigrate downstream from the tributaries to overwinter in larger streams, often living in the substrate. Winter cover, especially large rocks, is important in holding overwintering fish. Juvenile chinook salmon prefer deeper water with smaller substrate particles than do steelhead. Chinook salmon migrations into estuaries are correlated with periods of high discharge and turbidity, and migration is normally heaviest at night. These migrations occur primarily during spring and early summer, but continue at lower levels through fall. Fish entering the estuary range from 35 mm to 160 mm according to several authors. The larger juveniles tend to migrate earlier and growth increases in brackish estuarine waters. Spacial distribution of juvenile chinook within an estuary may be size dependent, while schooling in an estuary may be influenced by fright elicited in the fish due to tidal cycles and wave action. Estuarine residence times may be influenced by the occurrence of fall freshets, population abundance, and various estuarine characteristics; duration and timing of estuarine residence vary geographically with seasonal differences. Chinook salmon in the Skagit River Estuary occupied the inner estuarine salt marshes for 2 to 3 days before emigrating farther out in the estuary. The larger smolts, greater than 46 mm, spent approximately a day less in the salt marsh than did the smaller fish. Smolts congregated in tidal streams at low tide, with the majority of fish observed in deep, slow water over soft substrates. The highest chinook salmon densities occurred in tidal streams without any freshwater influence. It has been suggested that the abundance of the epibenthic prey fauna in soft, packed substrate habitat attract juvenile chinook. In the Nanaimo Life History - 2 (DRAFT) - Life History Species salmon, chinook Species Id M010030 Date 26 AUG 96 River Estuary, chinook salmon were found in water a few centimeters to over a meter deep over gravel, sand, and mud substrates. Where an extensive estuarine environment exists, juvenile chinook will reside there for up to 2 months. Within estuaries and bays, juvenile chinook salmon utilize shoreline areas extensively. Smaller fish may utilize the inshore areas while larger ones occupy deeper waters. Juvenile chinook salmon in Similk Bay primarily occupy the surface waters (93.8%) while a few (1.8%) extend down to 18.3 m. In river systems with high flushing rates relative to the amount of existing estuarine habitat, juveniles may move quickly through the mouth of the river and into the receiving marine waters. From work on the Snohomish River, it was hypothesized that fish carried in midstream have little chance to contact the shoreline and are carried offshore by strong river and tidal currents during ebb tide. Juvenile chinook salmon have been observed in several nearshore habitats, inshore from the 20-m depth level, between mid-May and September in Puget Sound. During estuarine rearing, chinook salmon exhibit significant growth. A minimum growth estimate of 2.6 mm per week for juveniles in the Duwamish River Estuary has been calculated. Minimum growth estimates of 1.5% of fork length per day have been indicated for juvenile chinook in the Skagit River Estuary. This spurt of growth before entering the marine environment may be vital to the subsequent early marine survival of juvenile chinook salmon. MARINE STAGES: Upon leaving the rivers of Oregon, Washington, and British Columbia, juvenile chinook salmon move up the coast in a northwesterly direction. This migration is a relatively slow feeding and dispersal movement with distance from the natal stream increasing with age. Sacramento River chinook are caught off the Washington and Oregon coast while Columbia River chinook are collected as far north as Alaska and as far south as San Francisco, California. Columbia River fish dominate the catch along the west coast of the Queen Charlotte Islands, and the Fraser River fish replace the Columbia River stocks north of the Queen Charlotte Islands. They remain in the marine environment between 1 and 6 years with the average being 3 or 4 years. Certain races of chinook salmon, such as the Puget Sound blackmouth, tend to remain in local marine areas. Two- to 5-year-old chinook salmon comprised the bulk of the troll catch in the nearshore areas, while the offshore catches were dominated by 5- and 6-year-old fish. Chinook salmon captured in the outer waters of British Columbia were on long spawning migrations, traveling southeast along the Continental Shelf. The return migration was fairly rapid in comparison to the feeding or dispersal migration. One- and 2-year-old chinook salmon in the Straits of Georgia were caught from the surface down to 30 m with the majority occupying the deeper water. In southeast Alaska, chinook salmon reside in marine waters throughout the year, feeding at relatively shallow depths in the spring and summer and occupying deeper waters (60-80 m) in the winter. Salmon spawning migrations are elicited by environmental cues, such as temperature or salinity, olfaction, celestial navigation, and magnetic orientation. The timing of this migration is innate, while the location or destination of the migration is learned through imprinting. GROWTH CHARACTERISTICS: Chinook fry emerge from the gravel during the winter, and some will migrate to sea after the first month when about 30 mm long. Some spring chinook populations enter saltwater as yearlings at Life History - 3 (DRAFT) - Life History Species salmon, chinook Species Id M010030 Date 26 AUG 96 lengths exceeding 100 mm *89*. Breeding Habitat: The general nature of the spawning ground, which may be located from just above tidal limits to great distances upstream (over 3,200 km in the Yukon River), varies considerably. Main channels and tributaries of larger rivers serve as the major chinook spawning areas. Normally, the spawning grounds are characterized by stream underflow (downwelling currents or intragravel flow) created by the depth and velocity of the water, rather than being associated with the emergence of groundwater. Ninety-five percent of the redds in the Kamchatka River, USSR, were situated precisely at the transition between a pool and a riffle. Many chinook salmon redds were located near the upstream tips of vegetated islands in the Kenai River where loose, clean gravels aggraded and where predominant substrates ranged from 1.6 to 6.4 cm diameter materials. Areas just below log jams, where flow through the gravel is increased as a consequence of reduced surface flow, are also favorite spawning sites. Exceptions to what may be considered normal breeding habitat and behavior have been documented. During late October and early Noverber 1965, approximately 50 chinook salmon from University of Washington hatchery stocks spawned in groundwater seepage areas of gravel and sand beaches in Lake Washington. This behavior is believed to have resulted from crowding and high water temperatures, both unfavorable conditions, at the hatchery homing pond *232*. Breeding Seasonality: In Alaska, mature chinook salmon ascend the rivers from May through July. Generally, fish that appear at the river mouth earliest migrate farthest. Peak spawning occurs from July through September *232*. Breeding Behavior: As with other salmon, adult chinook salmon return from the sea and normally move into their natal freshwater streams to spawn. The female selects the spawning site and digs the redd (nest) by turning on her side and thrashing her tail up and down. The current washes loosened substrate material downstream, and a depression 35 to 60 cm deep is formed in the river bottom. Eggs and sperm (milt) are released simultaneously and deposited in the redd. After egg deposition, the female moves to the upstream margin of the redd and repeats the digging process. Dislodged substrate is washed over the eggs. In this manner, the eggs are covered and prevented from washing away. The process is repeated many times, and the redd appears to move upstream. As a result of the continued digging, the redd may grow to become 1.3 to 5.6 m in length and 1.5 to 3.3 m wide. A female may dig several redds and spawn with more than one male. Males may also spawn with several females *232*. Age at Sexual Maturity: The age at which chinook salmon reach sexual maturity ranges from two to eight years (generally zero to two years in fresh water and one to seven years at sea), although the vast majority of the fish mature in their third to sixth year. Age at maturity, like freshwater age and ocean age, tends to be greater in the north than in the south because more northern populations spend a longer time at sea. From California northward to Cook Inlet, Alaska, for example, three, four, and five-year-old fish prevail (there are significant numbers of six-year-olds in some areas, but few if any seven- or eight-year-olds). Five- and six-year-olds dominate runs from Bristol Bay northward, but seven- and Life History - 4 (DRAFT) - Life History Species salmon, chinook Species Id M010030 Date 26 AUG 96 eight-year-olds are not uncommon *232*. Fecundity: Chinook salmon fecundity varies by stock and the size of the female; however, northern stocks generally produce more eggs. In Alaska, the number of eggs ranges from 4,242 to 17,255 per female *232*. Frequency of Breeding: As with all Pacific salmon, the spawning cycle is terminal. Both male and female die after spawning *232*. Incubation Period/Emergence: The amount of time required for eggs to hatch is dependent upon many interrelated factors, including 1) dissolved oxygen, 2) water temperature, 3) apparent velocity in gravel, 4) biological oxygen demand, 5) substrate size (limited by percentage of small fine material), 6) channel gradient and 7) configuration, 8) water depth, 9) surface water discharge and velocity, 10) permeability, 11) porosity, and 12) light. Generally speaking, factors 4 through 12 influence/regulate the key factors 1, 2, and 3. Eggs require about 900 temperature units (TU) to hatch and become alevins and an additional 200 to 800 TUs to absorb their yolk sac. The TUs for one day = mean 24-hour water temperature in degrees Farenheit - 32 oF + 1 oF if the mean temperature is 32 oF. Incubation of the eggs takes place with both ascending and descending water temperatures. Depending on the time of spawning and the water temperature, the eggs usually hatch in late winter or early spring. The newly hatched fish, or alevins, remain in the gravel until the attached yolk sac has been absorbed, normally two to three weeks after hatching. The juveniles then work their way up through the gravel to become free-swimming, feeding fry *232*. Size of Use Areas: A conservative figure for the number of pairs of salmon that satisfactorily utilize a given area of spawning gravel may be obtained by dividing the area by four times the average size of the redds. The redd area can be computed by measuring the total length of the redd (upper edge of pit to lower edge of tailspill) and the average of several equidistant widths. Chinook salmon redds in a Kenai River tributary stream are about 4.37 m2 in size. Mean values for mainstream Kenai River chinook salmon redds are 6.38 m2. Because of the effects of dewatering and freezing, the amount of available habitat at the time when adult salmon are spawning is a poor indicator of the amount of actual habitat that is available as potential incubation habitat. Estimates of available incubation habitat must take into account the differential effects of dewatering and freezing in various habitat types *232*. Timing of Movements and Use of Areas: Young-of-the-year juveniles move downstream in the fall to overwinter in areas of the stream with larger substrate (possibly because it provides better cover). Out-migrating smolt bound for the sea depart fresh water in the springtime. Smolt out-migrations tend to be nocturnal. Adults return to fresh water during the period of May through July. Studies on the Kenai River indicated that of all radio-tagged adults returning to the spawning grounds, most moved between 1400 and 2200 hours. Adult chinook salmon moved upstream mainly in the daytime *232*. Migration Routes: Large rivers serve as corridors for smolt out-migration. Barriers to adult upstream movement include excess turbidity, high Life History - 5 (DRAFT) - Life History Species salmon, chinook Species Id M010030 Date 26 AUG 96 temperatures (20.0 oC or more), sustained high-water velocities, and blockage of streams (log jams, waterfalls). While in the marine environment, first-year ocean fish are confined primarily to coastal areas and are much less abundant in the open ocean. During the second and subsequent years of ocean life, they are found widely distributed in the North Pacific Ocean and Bering Sea. Chinook salmon from Alaskan streams enter the Gulf of Alaska gyre and move extensively across the northern Pacific and in the Bering Sea, and during the summer their numbers increase in the area of the Aleutian Islands and in the western Gulf of Alaska. Many of the inshore fish of Southeast Alaska, however, appear to be of local origin. Except for areas immediately adjacent to the coast it is possible that chinook salmon do not occur in the high seas south of 40 oN. The central Bering Sea is a feeding ground and migration path for immature chinook salmon in Western Alaska (defined as the area from and including Bristol Bay northward to Point Hope). Tag recoveries are known to occur in the Bering Sea as far west at 172 deg 12' E (at 59 deg 03'N), whereas scale-pattern and maturity studies, combined with seasonal distribution and Japanese mothership and research vessels information, push the range further west, to probably at least 160 deg to 165 deg E. These same stocks have been found as matures in the North Pacific Ocean just south of Adak at 176 deg 18' W (at 51 deg 36' N). Scale-pattern analysis shows tentatively that they may extend from 160-170 deg E to at least 175 deg W; but their distribution to the south over this range, at least beyond 50 deg N, is even more uncertain. Other North American chinook salmon (including stocks from central Alaska [Cook Inlet] southward) are known to occur as immatures in the North Pacific Ocean as far west as 176 deg 34' W (at 51 deg 29' W). Recent coded-wire tag recoveries of chinook salmon marked in Oregon, Southeast Alaska (Stikine River and Little Port Walter), and Southcentral Alaska (Crooked Creek, a tributary of the Kasilof River on the Kenai Peninsula) indicate that these stocks occur in the southeastern Bering Sea north of the Alaska Peninsula. Tag recoveries occurred during the months of November, February, April, and May in an area from 54 deg 21' to 55 deg 26' N and 165 deg 21' to 167 deg 58' W. The tag recovery of the Crooked Creek fish at 55 deg 26' N, 167 deg 58' W was a definite range extension of Southcentral Alaska chinook salmon stocks into the Bering Sea *232*. Natural Factors Influencing Populations: Juvenile chinook salmon are preyed on by other fish (e.g., rainbow, cutthroat, Dolly Varden, coho salmon smolts, and sculpins) and birds (e.g., mergansers, king fishers, terns, osprey, other diving birds). Estuarine and marine predators include fish-eating birds, pelagic fishes, killer whales, seals, sea lions, and possibly the Pacific lamprey. The greatest natural mortality occurs in fresh water during the early life stages and is greatly influenced by the environment; therefore, deleterious changes in freshwater quality, quantity, or substrate are most detrimental. Flooding can either wash away or bury eggs. Natural sedimentation can smother eggs *232*. Human-related Factors Influencing Populations: A summary of possible impacts from human-related activities includes: alteration of preferred water temperatures, pH, dissolved oxygen, and chemical composition; alteration of preferred water velocity and depth; alteration of preferred stream morphology; increase in suspended organic or mineral material; increase in sedimentation and reduction in permeability of substrate; Life History - 6 (DRAFT) - Life History Species salmon, chinook Species Id M010030 Date 26 AUG 96 reduction in food supply; reduction in protective cover (e.g., overhanging stream banks, vegetation, or large rocks); obstruction of migration routes; shock waves in aquatic environment; and human harvest *232*. LIFE HISTORY CODES - Breeding/Spawning Season: July Breeding/Spawning Season: August Breeding/Spawning Season: September Mating System (Single breeding season): Promiscuity ( Nest Materials: Mud Nest Materials: Sand Average Number of Offspring/Reproductive Effort: 1,00 Average Number of Offspring/Reproductive Effort: Grea Periodicity: Active at night Periodicity: Active in day COMMENTS ON LIFE HISTORY - The juveniles apparently subordinate minimal space requirements to exploit periods of short-term food abundance. Juvenile chinook salmon prefer deeper water with smaller substrate particles than do steelhead. Interaction for space between species is minimized by differing spawning and emergence times *89*. REFERENCES FOR LIFE HISTORY- 89 and 232 Life History - 7
                           (DRAFT) - Management Practices
                               Species salmon, chinook
                                 Species Id M010030
                                   Date 26 AUG 96



MANAGEMENT PRACTICES

RESULT MANAGEMENT PRACTICE Existing Regulating harvest of species being described Existing Stocking captive-reared wild-strain animals Existing Regulating commercial harvest gear types Existing Regulating harvest - setting bag/creel limits Beneficial Developing/maintaining suitable pH Beneficial Controlling water levels Beneficial Controlling sedimentation Beneficial Establishing/maintaining nesting and escape cover Beneficial Developing/maintaining stream bank vegetation Beneficial Developing/maintaining stream structures Adverse Migration barriers Beneficial Regulating harvest of species being described REFERENCES FOR BENEFICIAL MANAGEMENT PRACTICES - 232 REFERENCES FOR ADVERSE MANAGEMENT PRACTICES - 232 REFERENCES FOR EXISTING MANAGEMENT PRACTICES - 89 COMMENTS ON MANAGEMENT PRACTICES - Nearshore and terminal area fisheries are conducted with purse seines and gill nets, and inriver set net fisheries are allowed by treaty-Indian fishermen in most river drainages. Salmon fisheries management is an extremely complex problem due to user-group allocations and mixed-stock and mixed-age fisheries. Optimum yield is the desired management goal for this fishery. Ocean fisheries are managed by a catch quota, while terminal area fisheries are managed by subtracting escapement goals from pre-season run forecasts, which are updated throughout the season. This yields the total allowable harvest, which must be allocated among the user groups involved. Individual chinook salmon stocks can be identified by studying the fine structure of the scales. Stocks are artificially identified by extensive coded wire tagging programs. Chinook salmon of Canadian and United States origin often are intercepted on the high seas by Japanese motherships. These fish are primarily taken as immature fish in the western Pacific Ocean and Bering Sea. Estimated incidental catch of chinook salmon by foreign trawl vessels was about 113,000 fish in 1981 *89*. The greatest natural mortality occurs in fresh water during the early life stages and is greatly influenced by the environment; therefore, deleterious changes in freshwater quality, quantity, or substrate are most detrimental. Flooding can either wash away or bury eggs. Natural sedimentation can smother eggs *232*. A summary of possible impacts from human-related activities includes: alteration of preferred water temperatures, pH, dissolved oxygen, and chemical composition; alteration of preferred water velocity and depth; alteration of preferred stream morphology; increase in suspended organic or Management Practices - 1 (DRAFT) - Management Practices Species salmon, chinook Species Id M010030 Date 26 AUG 96 mineral material; increase in sedimentation and reduction in permeability of substrate; reduction in food supply; reduction in protective cover (e.g., overhanging stream banks, vegetation, or large rocks); obstruction of migration routes; shock waves in aquatic environment; and human harvest *232*. Management Practices - 2
                                   (DRAFT) - References
                                 Species salmon, chinook
                                    Species Id M010030
                                      Date 26 AUG 96



     

References

232 * State of Alaska Department of Fish, and Game. 1986. Alaska Habitat Management Guide: Life Histories and Habitat Requirements of Fish and Wildlife. (ed.). Alaska Department of Fish and Game Juneau, Alaska:763. 89* Beauchamp, D. A., M.F. Shepard, G. B. Pauley. 1983. Species Profiles: Life Histories and Environmental Requirements of Coastal Fishes and Invertebrates (Pacific Northwest) -- Chinook Salmon. U.S. Fish and Wildlife Service Biol. Rep. 82(11.6) pp 15. References - 1