It is commonly assumed that the Kobuk River issues from Walker Lake. However, the headwaters of the river are to the east of Walker Lake in the Endicott Mountains within the Gates of the Arctic National Park and Preserve, just north of the Arctic Circle near 67°05′N, 154°15′W. It flows briefly south, descending from the mountains through two spectacular canyons (Upper and Lower Kobuk Canyon), then flows generally west along the southern flank of the western Brooks Range in a broad wetlands valley. In the valley it passes a connected community of inland native villages, including Kobuk, Shungnak, and Ambler, where it receives the Ambler River. In the river’s lower reaches, where it passes between the Baird and Warring mountains, it traverses Kobuk Valley National Park, the location of the 25 square-mile (65 km²) Kobuk Sand Dunes. It then passes Kiana. The river enters its broad delta approximately 10 miles (16 km) southwest of Kiana. The delta is located in The Hotham Inlet of the Kotzebue Sound approximately 30 miles (48 km) southeast of Kotzebue.
The Kobuk's Inuit name means "big river". It was first transcribed by John Simpson in 1850 as "Kowuk." Explored by Lt. G. M. Stoney, USN, in 1883-1886, who wrote the name "Ku-buck," but proposed that it be called "Putnam" in honor of Master Charles Flint Putnam, USN, officer of the Rodgers, who was carried to sea on the ice and lost in 1880. Lt. J. C. Cantwell, USRCS, also explored the river in 1884 and 1885 and spelled the name "Koowak" on his map and "Kowak" in his text. Ivan Petroff spelled the river name "Kooak" in 1880, and W. H. Dall spelled it "Kowk" in 1870. Lt. H. T. Allen, USA, obtained the Koyukan Indian name in 1885 which he spelled "Holooatna" and "Holoatna."
Native peoples have hunted, fished, and lived along the Kobuk for at least 12,500 years and it has long been an important transportation route for inland peoples. In 1898 the river was the scene of a brief gold rush called the Kobuk River Stampede. In 1980 the United States Congress designated of the river downstream from Walker Lake as Kobuk Wild and Scenic River as part of the National Wild and Scenic River program. The river is considered an outstanding destination for recreational floating.
The river contains an exceptional population of sheefish (Stenodus leucicthys), a large predatory whitefish within the salmon family, found throughout the Arctic that spawns in the river's upper reaches during the autumn. A portion of the vast Western Arctic Caribou Herd utilize the Kobuk river valley as winter range.
The Kobuk River Basin is located just north of the Arctic Circle and has a continental climate. The summers are short and warm, while winters are long and cold. The mean annual temperature in the middle and upper portions of the Kobuk Valley is -6°C, and the mean temperature in July is 15°C . An average of 21 inches (53 cm) of precipitation falls in the basin. However, actual precipitation can range from 15-40 inches (40-100 cm) with greater amounts falling in the upper reaches of the river basin .
The Kobuk River Basin is very sensitive to changes in climate. Arctic climates have warmed at approximately twice the global rate in the last several decades . Records of air-temperature from 1961-90 logged at the latitudes of the Kobuk River, show a warming trend of about 1.4°F (0.78°C) per decade . The warming has been the strongest in the winter and spring months . Observations of precipitation in the Arctic indicate an increase in precipitation by about 8% over the last 100 years . Much of the increased precipitation has fallen as rain, mostly in winter months . In the North America Arctic, there has been an increase in the duration of snow-free days at the rate of 5-6 days per decade . Climate change is presently considered the most severe environmental stress in the Kobuk River Basin and throughout Alaska .
As a specific example, climate change will cause widespread thawing of permafrost in the discontinuous zone and significant changes in the continuous zone. Thawing permafrost can lead to a landscape of irregular depressions (thermokarst) due to subsiding soils. This can alter drainage patterns and even change the course of streams; whereas other areas could become swamplike. In addition, slope stability will decrease and permafrost degradation could lead to erosion of river banks resulting in an increase in sediment transport by the rivers . These physical changes will impact nutrient cycling and biological processes within the basin as well.
As the glacier first retreated and melted, large amounts of highly erodible, fine-grained sediment dropped out in relatively high mountain valleys. The availability of fine-grained, loose sediment combined with a high gradient to turn a newly forming Kobuk River into a fast-working sediment transport system. The river picked up glacial till from its upper reaches and transported it downstream until the gradient diminished. When the river hit flatter ground, it deposited its sediment load resulting in the creation of large floodplains, alluvial fans, and meander bends through aggradation.
After the first stage of aggradation and sediment transport, the Kobuk began a new phase of erosion and landform development. The river exhausted its supply of easily erodible sediment upstream, thus decreasing its sediment load and increasing its downstream load carrying capacity. With more carrying capacity downstream, the river began to incise into the alluvial fan it previously created, moving sediment stored for a long time on its original floodplains to newer floodplains further downstream.
Further down in the Kobuk watershed, the river worked in concert with the wind to create one of the more famous landforms in Alaska: the Kobuk Dunes. These large sand dunes are the modern ancestor of alluvial deposits that became shaped and dominated by an exchange of aeolian and fluvial processes. In moister climates, the river has more water, and thus more power, and cuts down through a sandy bed. In times of drier climate, wind dominates and blows a lot of sediment into a weaker fluvial system, leading to aggradation and floodplain re-distribution.
Currently, the Kobuk River in its middle and lower reaches is an anastomizing stream, with several braided channels in places, wide migrating meander bends, and oxbow lakes. It is controlled by yearly cycles of freeze and thaw, much like its surrounding landscape. For six months of the year, the river is largely still, frozen on top by a thick layer of ice. In the spring, warmer temperatures cause this ice to begin to melt. But the resulting process is not gradual. Rather, the pressure of melting ice from upstream builds up upon ice “dams” in the river’s channel, eventually causing an “ice break-up” event, in which a flood of ice and water moves powerfully downstream.
These annual spring break-up events have several important consequences. First, the river has deeply undercut and eroded banks, caused by large, fast-moving chunks of ice carving out the river’s channel before it begins spilling out onto its floodplain, which is 1 to 6 miles (1.6-9.7 km) wide except at the confluence of major tributaries . Second, the river moves laterally very quickly and dramatically, re-inventing side channels every year as its secondary streams become drowned in each yearly flood by an overwhelming amount of sediment. Lastly, since the river is surrounded mostly by permafrost and because during the spring break-up event there are still large parts of frozen ground close to its banks, floods often transports large amounts of fine sediment across broad expanses of floodplain in thin sheets of water that slide easily across the frozen ground. These characteristics also translate into a relatively variable habitat for the Kobuk’s native species.
Farthest west, the Kobuk empties into Hotham Inlet, the easterly arm of Kotzebue Sound. During recent geologic times however, when sea level was lower, the Noatak, Kobuk, and Selawik Rivers were joined. Now they have separate deltas with many lakes and swamps and intricately webbed channel systems. The deltas are composed of silt, sand, and gravel .
The Kobuk River is ice covered 6 months of the year and in general, late October to late May is a period of relatively low flow . Annually, the hydrograph reflects two flood peaks: the first is associated with spring break-up and the second, a lesser peak, is associated with late summer precipitation . As the snowpack begins to melt toward the end of May, flow in the Kobuk River increases with most of the runoff occurring during June. Flow during the summer (July through September) is dominated by variable precipitation events .
Most of the major tributaries of the Kobuk River flow from the north drain the mountains in the southern Brooks Range. From east to west, these include the Reed River, Beaver Creek, Mauneluk River, Kogoluktuk River, Shungnak River, Ambler River, Akillik River, Tutuksuk River, Salmon River, and the Squirrel River . Within the Kobuk Valley National Park, are the Kallarichuk, Salmon, Tutuksuk, Kaliguricheark, Hunt, and Adillik rivers. All of their headwaters are in the Baird Mountains . The major tributaries flowing north from the Waring mountains are the Pah River, Pick River, and Niaktuvik Creek . The Pah River drains a lowland area of the basin. Most major tributaries draining high relief areas have higher unit runoff than tributaries draining the lower relief areas .
Walker Lake is at an altitude of 194 m in the "headwaters" of the Kobuk River . Other surface water features within the basin include Lake Selby, Nutuvukti Lake, and Norutak Lake . Additionally, numerous small lakes and ponds occur in the lowlands along the river, some formed as detached oxbows of the meandering river and others formed where permafrost has melted and caused depressions .
Flow records are available from USGS monitoring stations at Ambler (USGS 15744000) and Kiana (USGS 15744500). Average Annual Flow for the Kobuk River at Ambler has ranged from 5,839 cfs to 14,890 cfs over the period of record 1966-78, with peak discharge ranging from 30,000 cfs to 95,000 cfs. Near Kiana, Average Annual Flow has ranged from 10,020 cfs to 24,960 cfs for the period 1977-99 with peaks of 45,000 cfs to 161,000 cfs. Peak flows can result from large volumes of water released when ice jams fail . Flow records are also available for Dahl Creek, a tributary of the Kobuk River with a confluence near the town of Kobuk, from USGS (site number 15743850).
Walker Lake and the Kobuk River, like other Arctic inland waters, are influenced primarily by vegetation of five different general types: 1)phytoplankton, 2)benthic algaes, 3)submerged bryophytes, 4)emergent vascular macrophytes, and 5)adjacent terrestrial plant assemblages. All plants in the Arctic are limited by low temperatures, a short growing season and often nutrients, particularly phosphorous. As a result, Arctic lakes, ponds and rivers tend to be oligotrophic. Most primary production occurs in adjacent terrestrial habitat, which may contribute leaf litter, particulate organic carbon, and exudates such as colored organic matter to nearby streams.
Phytoplankton is more prevalent in ponds and lakes because high residence time allows for accumulated biomass and higher production, whereas in rivers it is advected away from sources of production as “drift”. Common phytoplankters in Arctic lakes are flagellates such as Rhodomonas and Chromulina, and diatoms. Both Walker Lake and the Kobuk are extremely oligotrophic due largely to phosphorous limitation. Production likely resembles open ocean food webs where oligotrophic conditions select for nanoplanktonic organisms that may have high numbers but very low biomass.
Benthic algaes may occur growing within sediments (epipelic) in aquatic soft-bottomed habitats or atop stones (epilithic) in cobbled, hard-bottomed habitats. Benthic production is limited by water depth and turbidity, which can depress light intensity. Walker Lake and the Kobuk River tend to be unusually clear because of oligotrophic conditions and low turbidity due to the absence of glaciers . As a result, benthic algaes may be 60 times more abundant than planktonic in Arctic lakes and ponds, forming a large reservoir of primary production that may have some capacity to overwinter and thus accumulate on an interannual basis. However, high irradiance may also be photoinhibiting during summer and benthic production may be lower in most of Walker Lake due to its depth
Benthic epipelic (sediment growing) primary production is dominated by green and blue-green algaes. Turnover into the sediment limits production, so most of the algal biomass is confined to the top 1-2 cm of sediments. Epipelic algae is probably somewhat abundant in parts of Walker Lake and in the lowland valley stretches of the Kobuk River, and may be an important source of carbon for the food web.
Epilithic (stone growing) algae is dominated by diatoms, which would be expected to be somewhat prevalent in cobbled sections of the Kobuk River, limited mostly by photoinhibition. Phosphorous may be less limiting than in Walker Lake due to edaphic inputs from surrounding tundra. Epilithic algae may form an important source of energy for secondary consumers in the form of aquatic insects. The dominant diatoms found in the nearby Kuparik River include Cymbella minuta, Achnanthes minutissima, Hannea arcus, and Diatoma tenue var. elongatum]]
Mosses are dominated by Schistidium agassizii although experiments on the Kuparuk River show that Hygrohypnum spp. may become abundant with phosphorus fertilization. The two mosses appear to carve out niche space through trade-offs in competitive ability under variable conditions . Bryophytes in general may form an important supply of carbon to aquatic invertebrates because of their rapid uptake of nutrients, resistance to low light and temperature, and resistance to scouring . In general, the contributions of bryophytes to stream ecology is less well understood than other forms of primary production such as epipelic and epilithic algae
Rooted aquatic plants are represented by sedges such as Carex aquatilis, grasses such as Arctophila fulva, and the buttercup Ranunculus pallasii. These plants generally propagate vegetatively via rhizomes because of the short growing season and harsh conditions, re-directing energy from sexual reproduction into vegetative growth.
Of these, C. aquatilis is the dominant in slow waters, lakes and ponds. Most of the biomass of the plant lives below ground while only the basal part of the stem survives the winter. The lifetime production of a plant is about 20-25 leaves in 4-7 years, and overall production is thought to be higher than in terrestrial tundra plants because of freezing protection afforded to organisms in the aquatic environment, and because dead leaf attachments that may shade the plant are removed by water and decomposition .
Adjacent ecosystems may contribute to aquatic production through leaf litter for aquatic invertebrates, dissolved organic carbon for bacterial and rotifer production, or fixed nitrogen to support aquatic primary production. These plant assemblages include 1) moist tundra (in river valley lowlands), 2) boreal forest (up to 2100’), 3) shrub thickets (up to 3000’), and 4) alpine tundra (above 3000’). Tundra tends to dominate the Kobuk River, punctuated by stands of boreal forest and shrub thicket.
1) Moist tundra occurs in moderately drained soils in river valley. It is dominated by cottongrass tussocks, with moss and lichens growing in the moist channels between the tussocks. Cottongrass dies each year, allowing dead leaves to accumulate, forming the tussock topography of the tundra. Also found in this habitat are small shrubs such as dwarf birch, willow and Labrador tea; grasses; and annual herbs and flowers.
2) Boreal forest, also known as taiga, consists of spruce stands mixed with hardwoods that follow Arctic river valleys. There are two forms of boreal forest on the Kobuk, associated with southern or northern slopes.
Southern slopes are dominated by white spruce associated birch, aspen or balsam poplar hardwoods. Ground cover may be characterized by heaths of bearberry, crowberry, Labrador tea, blueberry, cranberry and arctic willow. Lichens and mosses may also be found on the substrate.
Northern facing slopes and poorly drained valleys are dominated by black spruce, with an understory of spongy moss and low brush. The spruce may grow very slowly, such that a two inch diameter tree may be one hundred years old; trees are often stunted and scattered.
3) Shrub thickets are characterized also by at least two somewhat different plant assemblages, determined by elevation and hydrology.
Lowland shrub thickets are found on alluvial plains and gravel bars of low-incline, meandering streams. Low-lying willow and alder dominate, interspersed with dwarf fireweed, horsetail, prickly rose, and annual flowers. These communities grow rapidly on floodplains that are disturbed regularly by ice breakup and spring floods.
Alpine shrub thickets are found at higher elevations and give way to alpine tundra above about 3000’. At drier sites dwarf and resin birch dominate; while at wetter sites willow and alder dominate, interspersed by reindeer lichens, heaths, and other alpine tundra plants.
4) Alpine tundra occurs at higher elevations, in well drained, coarse, rocky soils. It is characterized by mat-forming heathers, moss campion, saxifrage, and reindeer lichen, as well as sedges, grasses, herbs and wildflowers.
Fires structure these plant communities episodically. Pioneer species include fireweed, Labrador tea, willow, and alders. Secondary successional species include quaking aspen (south facing slopes), paper birch (east or west slopes), and balsam poplars on river plains. Late successional assemblages include white- or black spruce-associated boreal forest species and reindeer lichens.
This is a list of common moist tundra species, a community that can be expected to characterize much of the Kobuk River valley:
willow (Salix spp.)
dwarf birch (Alnus crispa)
Labrador tea (Ledum spp.)
Lapland rosebay (Rhododendron lapponicum)
mountain alder (Alnus crispa)
mountain avens (Dryas spp.)
arrow grass (Triglochin spp.)
pendant grass (Arctophyla fulva)
bog rosemary (Andromeda polifolia)
louseworts (Pedicularis spp.)
rushes (Juncus spp.).
Secondary production in Arctic inland waters is distinctly different from that in temperate or tropical fresh water systems. Limited primary production because of thermal, light or nutrient limitation leads to an oligotrophic system. Foodwebs tend to resemble open ocean foodwebs, weighted at the lower levels with very small organisms, requiring many steps , and having many individuals with very low biomass. Primary production supplies mainly ciliates, rotifers, copepods, cladocerans or aquatic insects. Secondary production provides food for predatory copepods, fairy shrimp (Anostraca), and to a lesser degree predatory aquatic insects (which appear to be rare in the Arctic). Aquatic insects, copepods, and fairy shrimp all may supply larval fish . Secondary production derives from three main sources: 1) phytoplankton from water bodies with high residence time, such as Walker Lake, or oxbow ponds in the lower Kobuk River Valley; 2) benthic algae and bryophytes, which persist in shallow waters in both Walker Lake and the Kobuk River main stem; and 3) adjacent terrestrial plant communities.
Planktonic foodwebs rely on waters with high residence time, so most input of plankton derives from Walker Lake, some of which may appear in the upper Kobuk River as “drift”. Phytoplankton is consumed largely by daphnia, which may comprise up to 80% of zooplankton found in Arctic ponds. In fishless ponds, larger species of copepods tend to dominate. In ponds with fishes, smaller species make up most of the zooplankton as they are probably less vulnerable to predation. Zooplankton production is also controlled by low temperatures, low primary production and the short growing season. Species have generally adapted to these constraints by producing just one generation per year, which overwinters by producing diapausal eggs or embryos.
While plankton has been considered centrally important to Arctic lake ecosystems such as Walker Lake and in the Kobuk River, oligotrophic conditions leave the zooplankton largely depauperate. However, nutrient limitation is not as severe on the benthos, due largely to the accumulation of phosphate there. Growth of epilithon and epipelon are fueled by green and blue-green algaes which support populations of bacteria, ciliates and rotifers,; these films, in conjunction with bryophytes and leaf drop, support aquatic insects, cladocerans such as Eurycercus lamellatu and possibly, snails, which are fed upon directly by fishes.
In addition to benthic algaes, bryophytes provide a source of production through both direct and indirect (facilitative) ways. Bryophytes support populations of aquatic insects which graze directly on their tissue, but they also facilitate the growth of epiphytic algaes and as collectors for fine particulate organic matter, which promotes bacterial decomposition and the formation of epipelon, also an important source of grazing for aquatic insects.
Plant primary production that is biologically available to the aquatic system is in the form of leaf production or in the form of dissolved organic carbon. Both are important in Arctic systems because limited in-stream production (due to oligotrophic conditions) causes terrestrial inputs to become relatively more important. In addition, the low rates of decomposition relative to primary production found in the Arctic have created a thick organic layer; up to 13% of the world’s soil C is stored in Arctic soils. This high reserve of C creates an important terrestrial-water link not typically found in other ecosystems. Particulate matter that is washed into adjacent streams can accumulate in the benthos (as with bryophytes), forming an important source of epipelon.
Peat from adjacent plant communities may also be a large source of dissolved organic carbon, which may be used by bacteria and consumed by aquatic filter-feeders, such as dipterid larvae.
The aquatic macroinvertebrate community of the Kobuk River provides a critical resource to several higher order trophic level consumers from both aquatic and terrestrial habitats including predatory fish, mammals, and birds. The macroinvertebrate assemblage, largely dictated by the unique environmental conditions, disturbance regimes, food availability, and habitat features of the Kobuk River drainage, is less diverse than similar sized temperate region rivers and dominated by a few families of aquatic Diptera. There are several reasons for this apparent discrepancy in invertebrate fauna diversity including routine localized disturbances such as freezing of the water column, variable seasonal discharge during spring melt, scouring of the river bed surface through the release of anchor ice and seasonal food availability; all of which may adversely affect the survival rates of most aquatic macroinvertebrates in the region.
The Kobuk River dipteran community are largely composed of Chironomidae (non-biting midges), Ceratopogonidae (biting midges), and to a lesser extent, Simuliidae (black flies) and Empididae (dagger flies). Primary productivity on the Kobuk River, similar to many high Arctic rivers, is largely composed of fine particulate organic matter (from the direct leaching of peat) and the dipterans (especially the chironomid midges) seem particularly suited to capitalize on this important carbon source due to their functional feeding adaptations. Specifically, these types of species acquire the majority of their food resources through direct filtering and collection of minute food particles suspended in the water column, although some are predators. Due to minimal coarse particulate organic matter and other sources and nutrients, it appears that the filter feeding/collector and highly tolerant dipterans are uniquely situated to dominate the aquatic invertebrate community of the Kobuk River. In addition, these families and others show several ecological and physiological adaptations allowing them to persist under the harsh Arctic environmental conditions.
Those species able to survive through the Arctic winter on the Kobuk River are primarily univoltine, exhibit a long life cycle which may exceed an entire year, experience periods of dormancy, and may use particular advantageous physiological adaptations to endure the cold winter months. Because development is difficult and slow paced under climatic extremes such as the Arctic, most aquatic invertebrate species are only able to produce one generation per year and the lifecycle duration of many species may range over a several year period before adult emergence. Several Arctic aquatic invertebrate species (most notably those of the Chironomidae family) have been shown to tolerate freezing during the winter, either through larval dehydration or by creating specific proteins which protect the internal cavity of the species. Other successful adaptations by Arctic macroinvertebrates include drifting to more thermally favorable habitat, over-wintering larval eggs, and dormancy or diapause.
Plecoptera (stoneflies), Ephemeroptera (mayflies), and Trichoptera (caddisflies) also make up a portion of the Kobuk River macroinvertebrate assemblage, but to a much lesser extent than the dipterans. The lack of diversity and abundance of species from these orders may largely be dictated by the available food resources present within the Kobuk drainage at any one time and/or an inability to adapt to extremely severe winter conditions. The family Nemouridae likely represent a significant proportion of the stonefly order, while the Baetidae and Heptageniidae represent the dominant mayfly families. Tricopterans are even more sparsely populated and may be restricted to particular microhabitats especially higher up in the watershed. Finally, several orders of insects rarely make an appearance on the Kobuk River, including the Hemiptera, Odonata, Megaloptera, and Coleoptera.
The Kobuk River drainage contains at least 18 species of fish along the roughly 450 km of main stem and thousands of streams, lakes, ponds and sloughs. All the species are native and none are listed as threatened or endangered. Fishing is an important part of the native culture in the Kobuk River and fish often constitute the main part of the diet (e.g. ). Fish comprises more than half of the subsistence harvest in many households on the Kobuk River and an average of 104.3 kilograms (230 pounds) of fish per person are consumed annually in rural Alaska.
Walker Lake is a large glacial lake located close to the headwaters of the Kobuk River approximately 400 km upstream from Hotlam Inlet. The lake contains a variety of fish species: whitefishes, chars, northern pike, longonse sucker, burbot, slimy sculpin and ninespine stickleblack, among others There are many other lakes in the Kobuk River drainage that, in some cases, contain similar assemblages and provide essential overwintering and feeding areas to the fish of the Kobuk River. The river supports many migratory populations of whitefish, and to a lesser degree chum salmon and, Dolly Varden, whose abundances are seasonal. Some species are permanently present in the main stem, such as Alaska blackfish, which is well adapted to the severe winter conditions of the Arctic Kobuk River. The lower floodplains of the Kobuk River, especially close to the Kobuk River delta, contain many shallow lakes and sloughs that create a high diversity of habitats normally used for feeding and overwintering.
The order salmoniformes has the highest richness among the Kobuk species, which is typical of Arctic freshwater ecosystems. The families present are Salmonidae (with three subfamilies: Coregoninae, Salmoninae and Thymallinae), Esocidae, Lotidae, Dalliidae, Catostomidae, Cottidae and Gasterosteidae (Table 1). The subfamilies Coregoninae and Salmoninae are the most significant in the Kobuk River with at least six and five species respectively. All other families have only one species represented.
Table 1. Families and species of fish represented in the Kobuk River.
The following descriptions refer to the biology of each fish species, with emphasis on the Kobuk River ecosystem.
Sheefish (Stendous leucichthys), also called Inconnu (unknown fish), are large piscivorous and of the whitefish family. They grow slowly and reach up to 27 kg in the Kobuk River. The northernmost range limit of sheefish in Alaska occurs in the lower reaches of the Noatak River. There, the fish only feed, and spawning occurs in the more southern Kobuk River. Sheefish in the Kobuk River, Selawik River, and Kotzebue Sound constitute one single population. Feeding and wintering grounds of this population are in the lower reaches of the Kobuk River, Hotham Inlet, and Selawik River drainage
In the spring before the ice breaks up, the sheefish start the slow upstream migration in the Kobuk River; both mature and immature fish start the migration together. They usually do not enter the tributaries of the Kobuk River. Instead, the fish move to the feeding grounds of the lower reaches of the Kobuk for about one month, and then spawners migrate to spawning grounds, most of which can be found in the area between the Kobuk Village and the Reed River during summer and fall. Sheefish have been reported as far upstream as the Lower Kobuk Canyon, where rapids and falls seem to block their upstream migration. The optimum riverbed composition is differentially sized coarse gravel, with no silt and some sand. Major spawning grounds seem to be located between 38 and 48 km above the Kobuk Village where depths vary from approximately 1 to 3 meters. Females spawn on the surface of the water and then the males fertilize the eggs. Spawning usually occurs in the afternoon and evening. Non spawning fish stay in the feeding grounds not far from the mouth of the Kobuk River for the rest of the summer. It is not certain if they spawn every year or alternates years. Other immature sheefish summer in Kotzebue Sound and Hotlam Inlet, among other areas.
After spawning, they undertake a rapid migration to areas close to Noorvik and Kiana. They may feed for a short period of time before migrating slowly to the overwintering areas of the lower Kobuk River and/or slightly brackish water of the Hotham Inlet and Selawik Lake (Alt 1977). The young migrate downstream with the spring floods where the early years of life are spent. Sheefish younger than 4 years old are not normally found in the upper reaches of the Kobuk River. They rarely feed while migrating to the spawning grounds, although they are still in good condition when they reach the grounds in late September. The diet varies according to size, age and season. The young start feeding on plankton, but soon prey upon insect larvae and zooplankton. Important in the adult diet are isopods, Mysis and other whitefishes, char, smelt, blackfish, suckers, burbot, sticklebacks and sculpins which are abundant in the Kobuk River drainage.
Most subsistence fishing occurs in late August and September, although native people prefer to harvest them late in the season because they have higher fat content, the eggs are ripe, and sheefish can be aged and frozen which is a more preferable method than drying. Three types of gear are usually used for fishing; gill nets, beach seines, and rods and reels.
Broad whitefish (Coregonus nasus) are called the Kobuk River fish because they are more abundant in the Kobuk River than in other rivers of the region, but not in such large numbers as some of its relatives. They are the largest whitefish in the Kobuk River after sheefish, have a high fat content, and are an important species for the subsistence of the native people . They grow slowly and the largest broad whitefish recorded in Alaska measured 67 cm. This species has a variety of ecological forms in the Kobuk River system, and are seasonally present in most of the available habitats (Table 2) . Some fish overwinter in Hotlam Inlet and Selawik Lake, others in the main stem of the Kobuk River and delta, and others in the deep lakes that are found along the river. In spring, when the ice breaks up, the broad whitefish search for the most productive feeding areas before spawning in a very complex movement pattern. Some move into the lower reaches of the Kobuk River and delta; others move out of the lakes into the streams, main stem and/or to other lakes and sloughs; others move into the tundra and floodplain lakes; others migrate to the upper reaches in search of other lakes, and others spend the summer in Hotlam-Selawik estuary, coastal lagoons and other rivers.
Most undertake the upstream spawning migration from as early as June until September and actual spawning takes place from September to November. They are the last whitefish in the Kobuk River to spawn. After spawning, they migrate back to their overwintering areas, which are mainly located in lakes or the lower reaches of the Kobuk River delta and Hotlam Inlet. Spawning takes place on gravel bottoms, where the young emerge the following spring and most move downstream. They are bottom feeders, eating zooplankton when young, and chironomid, mosquito larvae, and crustaceans as adults.
Table 2. Summary of the main seasonal locations of broad whitefish in the Kobuk River drainage.
Humpback whitefish (Coregonus pidschian) occur in at least two ecological forms in the Kobuk River drainage: diadromous and resident. The diadromous start migrating from the lower reaches of the Kobuk River drainage in June and spawn in the upper reaches in October. The young emerge in late winter and spring and migrate downstream to the lower reaches of the river and the estuary. They return after 4 to 6 years when they are sexually mature. The resident fish move from lakes to the main stem, tributaries or other lakes along the Kobuk River in spring and feed throughout the summer . They spawn generally in the upper reaches of Kobuk River and then return to the lakes to overwinter. The young mainly feed on zooplankton, while the adult’s diet consists of crustaceans and chironomid larvae. They grow slowly; a 5+ year old fish measure approximately 26 cm, and a 10 year old fish 40 cm. They are harvested in great numbers and are the primary food source for most of the villages along the river .
Round whitefish (Prosopium cylindraceum) are the only whitefish of the genus Prosopium in the Kobuk River, and are generally found in freshwater. They are more abundant in the upper Kobuk River than in the lower reaches downstream from Noorvik. They are present in smaller numbers than the other whitefishes and the maximum weight in the drainage is up to two kg. Spawning migrations to the shallow gravel grounds of the upper reaches occurs from late September to October, although they can spawn on the inshore of the lakes . They grow slowly, reaching sexual maturity after approximately 7 years and measuring about 50 cm at 12 years in the Kobuk River. They primarily feed on the immature stages of insects and other invertebrates . Finally, the Round whitefish is not regarded as valuable by native people because it is said to taste like “the metal of a wet knife” .
Least cisco (Coregonus sardinella) are the smallest and potentially the most abundant whitefish in the Kobuk River, although their migration patterns cause abundances to change seasonally. Least cisco overwinter in the lower reaches of the Kobuk River and also reaches the brackish waters of Hotlam Inlet and Selawik Lake. The species have been observed as far inland as Walker Lake. Least cisco move into lakes to feed soon after the ice breaks up and spend the summer feeding in lakes . In the fall, fish move out of the lakes to the main Kobuk River to spawn. The spawning substrate is composed of gravel and sand, and it appears that least cisco find these substrates in reaches downstream from Shungnak. They spawn from late September to early October at night and normally do not feed during the spawning run. The eggs can be found in a variety of colors: orange, pink, white and yellow. The eggs and the eyes of the fish are very appreciated by the native people. The eggs winter in the gravel and hatch early in the spring; the young migrate downstream to deeper, slower waters. They feed on diverse types of zooplankton, Mysis relicta, insect larvae, and also plant material. Many predators feed on the eggs, including eagles, pike, sheefish, lake trout, burbot and humans.
Bering Cisco (Coregonus laurettae) is mainly found in the Hotlam Inlet and its lagoons, although it may be present in reduced numbers in the lower reaches and delta of the Kobuk River.
Chum salmon (Oncorhynchus keta) undertake moderate runs in the Kobuk River during the summer along with a few individuals of pink salmon. (Oncorhynchus gorbuscha) Chum have been observed as far inland as Walker Lake Subsistence fisheries target this species in the Kobuk River when salmon migrate upstream from late June through early September, and they make up to approximately 10% of the total food source in the households of the Kobuk River. Young emerge the following spring and migrate directly to the sea. They usually remain at sea from two to four years before returning as adults to spawn.
Lake trout (Salvelinus namaycush) are the largest freshwater fish in Alaska. Lake trout are char with a limited distribution to a few deeper headwater lakes in the upper Kobuk River, such as Walker Lake and Selby Lake. They usually inhabit large, deep, cold lakes where they can complete their life cycle. Spawning usually occurs on the rocky and clean bottoms of lakes from late August through late November. Kobuk natives have observed a few lake trout spawning in the main stem of the river. The spawning frequency for females in Walker Lake is once every two years and the youngest age at maturity is 12 years for both males and females. Lake trout in Walker Lake grow slowly, and lengths range from approximately 200 to 900 mm and 80 to 8500 g. The oldest ever aged was 26 years. The diet varies according to age, size, locality, and available food, such as zooplankton, insects, fishes, algae and worms. Mature trout feed almost exclusively on fish when available and in the Kobuk lakes they may feed upon whitefish, grayling, sticklebacks, sculpins and suckers, among others.
Arctic char (Salvelinus alpinus) occur in its resident form in Walker Lake, Selby Lake and other lakes in the middle and upper Kobuk River. Arctic char spawn every other year after reaching sexual maturity at 6 to 9 years. Spawning occurs mainly in lakes from August through October on gravel bottoms at sufficient depth to be protected from winter ice. These fish grow slowly, , and weights over 10 pounds are not uncommon in some Alaska lakes. Artic char are opportunistic feeders; they prey on fish, crustaceans, worms and macroinvertebrates.
Dolly Varden (Salvelinus malma) are char found in the Kobuk River system. In Northern Alaska, they occur in lake resident, stream resident, and anadromous forms. They may occur in all of these possible forms in the Kobuk River drainage, but this has not been studied. They spawn in streams, usually from mid-August to November and have been observed while spawning in several Kobuk River tributaries. The optimum substrate is mainly composed of gravel in which the eggs overwinter. After hatching the following spring, the young rear in streams from three to four years before their first migration to sea. Once at sea, they begin a complex pattern of migration, wintering in and migrating to and from fresh water. In the Arctic, young and adults winter in springs and spring-fed areas of streams, and the adults go to sea to feed every year immediately after the ice breaks up. Mature spawners normally migrate back from the sea to their natal stream in August; in contrast, the non spawners return later and not necessarily to their natal stream. The diet varies according to age and size of the fish, locality, and the available food; young feed mainly on insects and crustaceans, and adults incorporate fish, fish eggs and worms into their diets. The fishery in the Kobuk River is of lesser importance compared to that of the Noatak where thousands of migratory Dolly Varden overwinter in the lower part of the river.
Arctic grayling (Thymallus arcticus) are ubiquitous in the Kobuk River from the lower reaches to Walker Lake. They are considered one of the most beautiful fish in Alaska due to a sail-like dorsal fin with purple and red spots. They are freshwater residents in the main Kobuk River, tributaries and lakes, and migrate among habitats for spawning in the spring, feeding during the summer and overwintering. They are even able to complete their life cycle in short river sections or in a lake without the need for migration. They probably spend the winter in the deeper lakes and pools of the main stem. Their tolerance to low dissolved oxygen allows them to survive in places where other salmonids would die due to the severity of the long Arctic winters. In spring, they usually start the upstream migration to the same spawning sites. After spawning, they move to the feeding areas. Fry emerge in approximately three weeks and generally start the overwintering migration to the downstream reaches in the early fall. They are omnivorous but they prefer aquatic insects, fish eggs and occasionally small fish. They are important for the subsistence fisheries in the Kobuk River. A popular harvest method consists of setting up gill nets at the mouth of the small streams draining from lake systems in the spring after the ice breaks up .
Northern pike (Esox lucius) occur seasonally in many of the lakes, streams, sloughs and main stem of the Kobuk River drainage Northern pike in the Kobuk River weigh up to 10 pounds, but in Alaska can reach 20 pounds. Spawning occurs in spring soon after the ice melts; eggs are laid in the grassy shores of lakes, streams or probably in the slow areas of the main Kobuk River. Incubation takes around 30 days in Alaska and emerging fry feed on insects and small crustaceans. The diet of adult pike is mainly composed of fish and occasionally other aquatic and terrestrial animals. In spring, they migrate from the overwintering areas to spawn, and later, to feeding grounds for the summer. The fisheries are quite important for the households of the Kobuk River villages, who harvest them in spring when they leave the lakes after the ice breaks up. They also catch pike during the winter in deep areas of the Kobuk River .
Burbot (Lota lota) are nocturnal, voracious bottom feeders which inhabit probably the deepest waters of the Kobuk River system. They have been reported in the main stem, and Walker Lake and may be present in most of deep lakes along the Kobuk River and its brackish estuary. Burbot grow slowly and are long lived; burbot older than 20 years are common in Alaska They spawn under the ice during the winter and mill together forming a ball while spawning. Spawning occurs in lakes and rivers; sedentary fish do not undertake important spawning or feeding migrations. They move to shallow waters to spawn on sand, gravel or cobble grounds. Young feed mainly on invertebrates, and adults prey almost exclusively on fish (whitefish, sculpins, suckers, pike, among others).
Alaska blackfish (Dallia pectoralis) are small freshwater fish which rarely exceed 20 cm in length. They are well adapted to the harsh conditions of the Artic with the ability to survive at low levels of oxygen, partial freezing and they have the capacity to breathe atmospheric oxygen. Alaska blackfish probably occur in most habitats of the Kobuk River system due to their ability to thrive in any conditions. They are sluggish bottom feeders that may be abundant in the tundra and floodplain lakes and sloughs of the main stem. They can survive in stagnant tundra pools, swamps and shallow lakes during the summer where vegetation can be abundant. Spawning occurs during the spring and summer and their fertilized eggs adhere to aquatic vegetation because they are demersal and sticky. Hatching occurs in about 10 days when water temperatures are approximately 12 to 13 degrees Celsius. The young are about 6 mm at hatching and their yolk sacs last for about ten days. Small individuals eat mostly copepods and Cladocera, shifting as they grow larger to insect larvae, snails, and more rarely small fishes. They are preyed upon by many terrestrial and aquatic animals. The fisheries can be very important in the Artic when the other food supplies are less available or consumed in the late winter.
Longnose sucker (Catostomous catostomus) is the only sucker located in Alaska. They are present in the Kobuk River system and have been found as far inland as Walker Lake. Breeding occurs from May through July, depending on the location and temperature of the water. They spawn in shallow and gravel substrates of lakes and streams and may migrate to suitable spawning areas Post spawning mortality can be as high as 30% they may not spawn annually. Young emerge from the gravel after approximately one month and begin feeding. By October, adults and young have left the upper reaches or the spawning areas and moved downstream to overwinter. These fish are bottom feeders and prey on small insect larvae, other invertebrates, aquatic plants, algae and fish eggs. They are normally preyed upon by larger fish such as burbot and northern pike. In spring, after the ice breaks up, Kobuk people set up gillnets at the mouth of small creeks draining from lake systems in search of suckers and other fishes that leave the overwintering lakes to the streams .
Slimy sculpin (Cottus cognatus) are small, fresh to brackish water fish present on the bottoms of the Kobuk River and lakes of the drainage They average about three inches in length; they have poor swimming qualities, in part because they do not have a swim bladder. These fish are quite sedentary and prefer gravel and rocky substrates. They generally move to shallow waters to spawn in the spring just after the ice breaks up. They feed mainly on insects, crustaceans, fish eggs, and small fish. They may be an important food resource for the numerous piscivorous fish of the Kobuk River.
Ninespine stickleback (Pungitius pungitius) are small fish which can survive in marine, brackish and fresh water though they require freshwater to spawn. They overwinter in deep waters but move to shallower waters to spawn from May to July. Their diet is mainly composed of copepods and chironomids, but they also feed upon other invertebrates and fish eggs. These fish may be an important food source for the piscivorous fish species of the Kobuk River. There is no fishery for ninespine stickleback, although they are so abundant some areas that they are used for human and dog food.
For the purposes of this article the river basin has been divided into three sections: the upper river, middle river and the delta. The faunas of the upper and middle Kobuk River Basin are characteristic of that of the interior of Alaska. However, many species which occur in the delta of the Kobuk are marine obligate and do not occur in the upstream sections of river. These species (such as marine mammals and polar bear) are more indicative of coastal mammal assemblages in the Arctic and are not covered in this article.
The headwaters of the Kobuk lie high in the Endicott Mountains of the Central Brooks Range within the southern portion of the Gates of the Arctic National Park and Preserve. This alpine habitat differs from the broad valley of the middle Kobuk and consequently the animal assemblages are not identical although there is considerable overlap. Montane species such as the Alaska marmot and Dall’s sheep can be found at the higher elevations indicative of the upper watershed.
The middle Kobuk delineated by the Baird Mountains to the north, and the Kobuk Sand Dunes and the Warring Mountains to the south is the northeren limit of the boreal forest. Kobuk Valley National Park encompasses over 6 thousand square kilometers of the Kobuk valley and the National Park Service estimates that 119 birds, 32 mammals, and 1 amphibian species occur in the park. The following list anmes animals known to occur in the Kobuk River basin. Descriptions specific to Kobuk River populations follow the entries. An effort has been made to high-light animal interactions with the riverine ecosystem.
Bears, both grizzly and black, are found throughout the region, as are wolves, coyotes, and foxes. Other fur bearers are locally and seasonally abundant. In salmon bearing watersheds such as the Kobuk, mammals play an important ecological role in nutrient cycling. Many species of anadromous salmon and trout are semelparous (i.e. they die after spawning) and their carcasses represent a significant seasonal nutrient contribution to the system in which they perish. Aquatic macroinvertebrates and juvenile salmonids have been shown to be enriched with marine-derived nitrogen (15 N) in systems supporting anadromous salmonids . Riparian vegetation adjacent to these streams are also 15 N enriched, indicating that animal vectors (most famously bears, wolves and eagles) are distributing marine derived nutrients via salmon within the system . In Washington studies have documented 18 species of terrestrial animals feeding on spent salmon carcasses . Similar results are reported from central California where herbivores such as deer and western gray squirrels were observed feeding directly on carcasses . The California study also showed that apoximately 25% of the nitrogen in grape leaves grown in riverside vineyards was derived from marine sources, presumably salmon.
Gray Wolf (Canis lupus)
Wolves occur throughout the Kobuk Valley, traveling in packs or family groups as they hunt. The main prey of wolves in the central Brooks Range is caribou; however, other prey species may be used extensively if caribou are not available, principally Dall sheep, small mammals, moose, snowshoe hare, and beaver. Denning usually occurs on dry, well drained slopes where excavation of soils is not hindered by frozen ground. Litters average five or six pups. Wolves are a source of income for village residents who trap and hunt them.
American Black Bear (Ursus americanus)
Upon emergence from hibernation in the spring, freshly sprouted green vegetation is the main food item, but black bears will readily take anything they encounter. As summer progresses, feeding shifts to salmon if they are available. In areas without salmon, bears rely primarily on vegetation throughout the year. Berries, especially blueberries, are an important late summer-fall food item. An "average" adult male in summer weighs about 180-200 pounds .
American Marten (Martes americana)
American Mink (Mustela vison)
Brown or Grizzly Bear (Ursus arctos)
Brown bears (barren-ground grizzlies) occur throughout the Kobuk River Basin. They are among the earth's largest predators, but in the Brooks Range they feed mostly as vegetarians, eating berries, sedges, hedysarum, and other plants. They also feed on small mammals and may spend hours excavating ground squirrel burrows, locally disrupting much of the ground surface in the pursuit of their prey. The bears will kill moose calves and caribou fawns and occasionally adults. Some scavenging also occurs. Brown bear populations concentrate along major streams and rivers . Along the tributary streams of the middle and lower Kobuk brown bears will feed on salmon and other anadromous fish. Brown bears gain weight rapidly during the late summer and fall. At this time most mature males weigh between 500 and 900 pounds with extremely large individuals weighing as much as 1,400 pounds. Females weigh one half to three quarters as much. There is an average of one brown bear for each 100 square miles of habitat in the Arctic .
Canada Lynx (Lynx canadensis)
Least Weasel (Mustela nivalis)
Northern River Otter (Lontra canadensis)
Red Fox (Vulpes vulpes)
Short-tailed Weasel (Mustela erminea)
Wolverine (Gulo gulo)
Barren-ground Caribou (Rangifer tarandus groenlandicus) The Western Arctic caribou herd migrates through the Kobuk valley twice a year on their annual migration between calving grounds nrth of the Brooks range and wintering grounds. The western Arctic caribou herd is most widely dispersed in midwinter, when bands are scattered throughout the forests on the south slopes of the Brooks Range and in the adjacent lowlands, and again in midsummer, when they are scattered over the Arctic slope west of the Sagavanirktok River. Spring movement to summer ranges begins in March, when bands of females travel northward up the Alatna, John, and North Fork of the Koyukuk drainages and cross the summit of the Brooks Range into the valleys of such rivers as the Killik, Chandler, and Anaktuvuk, which they follow or cross in a generally westward movement to calving grounds at the head of the Utukok and Colville Rivers. Males and some yearlings begin moving somewhat later. After calving in late May, the animals join increasingly larger groups to move to higher country on the North Slope and in the foothills of the Brooks Range. Once there they gradually disperse, using summer range from the Arctic Ocean to the summits of the Brooks Range by late July. A southward drifting of caribou begins in August. Migration continues through the rut in October, until the wintering grounds are reached. Some Caribou winter in the Kobuk Valley but exact timing and route of annual migrations and wintering grounds is highly unpredictable.
Lichen are composed of blue green algae and fungi existing in a symbiotic relationship. Lichenized algae are among the principal nitrogen fixing agents in Arctic terrestrial environments and are the primary forage of caribou. It is likely that caribou mobilize a significant amount of nitrogen through their consumption of lichen.
Dall’s Sheep (Ovis dalli) Dall sheep are present in the higher elevations of the Brooks Range.
Moose (Alces alces) Moose were scarce in the region 50 years ago but the population has steadily increased in recent years and now numbers several thousand. There is some indication that moose populations have been high in the past and have fluctuated along with climatic shifts.
Small mammals form the base of the Arctic food chain and are a critical element in the survival of many raptors and large mammals. Singing, tundra, and red-backed voles and brown and collared lemmings convert plant resources to flesh on which a variety of predators depend. Collectively, small rodents may have a profound localized effect on tundra vegetation. Larger rodents include the Arctic ground squirrel and Alaskan marmot. Arctic ground squirrels occur primarily on well drained soils along rivers or on slopes. They are commonly observed and can often be a problem at cabins, food caches, and camps.
Alaska Marmot (Marmota broweri)
American Beaver (Castor canadensis) Beavers are Through the cutting of wood and the construction of dams, beaver retain sediments and organic matter, create and maintain wetlands, modify nutrient cycling and decomposition dynamics, modify riparian structure and dynamics, influence the character of materials transported downstream, and ultimately influence plant and animal community composition and diversity . With regard to the latter point, the activities of beaver have been shown to replace invertebrate taxa normally adapted to running- waters with pond taxa , generate a striking increase in the biomass of lotic invertebrates per unil area , and influence fish assemblages .
Arctic Ground Squirrel (Spermophilus parryii)
Brown Lemming (Lemmus trimucronatus)
Muskrat (Ondatra zibethicus)
North American Porcupine (Erethizon dorsatum)
Northern Collared Lemming (Dicrostonyx groenlandicus)
Northern Red-backed Vole (Clethrionomys rutilus)
Red Squirrel (Tamiasciurus hudsonicus)
Singing Vole (Microtus miurus)
Taiga Vole (Microtus xanthognathus)
Tunda Vole (Microtus oeconomus)
Barren ground Shrew (Sorex ugyunak)
Common or Masked Shrew (Sorex cinereus)
Dusky Shrew (Sorex monticolus)
Pygmy Shrew (Sorex hoyi)
Alaska Tiny Shrew (Sorex yukonicus)
Tundra Shrew (Sorex tundrensis)
Snowshoe Hare (Lepus americanus)Wood Frog (Rana sylvatica)), produces an abundance of glucose, which acts as an antifreeze in its blood and tissues allowing it to survive the harsh Arctic winter.
Birds that breed in the Arctic benefit from an abundance of food because plants and insect life flourish in the long daylight hours of the Arctic spring and summer. The long days also greatly increase the overall time birds can spend foraging, radically increasing their overall caloric intake. Being able to fly allows birds to avoid the harsh environmental conditions of the Arctic winter which few large predators can survive, yet still arrive early enough to enjoy the benefits of the Arctic summer.
Several extensive birdlists exist for the Kobuk River basin. The Gates of the Arctic Bird List is compiled by Gates of the Arctic National Park in which the Kobuk River has it headwaters. Birds found in the middle and lower Kobuk are listed in the Birds of Northwest Alaska checklist compiled by the U.S. Geological Survey and encompassing all birds observed in the Kobuk Valley National Park, the Cape Krusenstern National Monument and the Noatak National Preserve.
Abbreviations and Codes to birds and their habitats
CAKR = Cape Krusenstern National Monument
KOVA = Kobuk Valley National Park
NOAT = Noatak National Preserve
A = Abundant
F = Fairly Common
C = Common
U = Uncommon
O = Occasional
R = Rare
x = Not known to occur
common name is followed by abundance levels in each habitat and an eskimo name
LOONS CAKR KOVA NOAT Eskimo Name
___ Red-throated Loon F* U F* qaqsrauq
___ Arctic Loon R* C* R* malgi
___ Common Loon R* R R taatchiniq
___ Pacific Loon F* O O* -
___ Yellow-billed Loon R* x F* tuulik
GREBES CAKR KOVA NOAT Eskimo Name
___ Horned Grebe R O R sugliq
___ Red-necked Grebe O* O O* suglitchauraq
SHEARWATERS CAKR KOVA NOAT Eskimo Name
___ Short-tailed Shearwater R x x -
CORMORANTS CAKR KOVA NOAT Eskimo Name
___ Pelagic Cormorant R x x -
SWANS & GEESE CAKR KOVA NOAT Eskimo Name
___ Tundra Swan U* U U* kugruk
___ Trumpeter Swan R x x -
___ G. White-fronted Goose U* U* R kigiyuk
___ Snow Goose R R x kanug
___ Emperor Goose R x x nasrauthik
___ Canada Goose O O* O* iqsragutilik
___ Brant O* x x niglignaq
WATERFOWL CAKR KOVA NOAT Eskimo Name
___ Green-winged Teal C* U* C* quinniq
___ Mallard O O R ivugasrugruk
___ Northern Pintail F* C* F* ivugak
___ Northern Shoveler C* U x alluutaq
___ Eurasian Wigeon R x x -
___ American Wigeon C* C* C* ugiihiq
___ Canvasback O* O R -
___ Redhead R x x -
___ Ring-necked Duck R x x -
___ Greater Scaup C* U C* qaqlukpalik
___ Lesser Scaup O U x qaqlutuuq
___ Common Eider C* x R -
___ Steller's Eider R x x -
___ King Eider O x x -
___ Spectacled Eider R x x -
___ Harlequin Duck O R R sagvak tinmiaq
___ Oldsquaw A* C A* ahaaliq
___ Black Scoter U* U U* uvinauyuk
___ Surf Scoter O* C O* tuungaagruk
___ White-winged Scoter R x U* killalik
___ Goldeneye Spp R R R -
___ Bufflehead R x x nunuqsigiilaq
___ Common Merganser U x x -
___ Red-breasted Merganser U* U* U* paisugruk
HAWKS & EAGLES CAKR KOVA NOAT Eskimo Name
___ Osprey R R R* qaluksiigayuk
___ Bald Eagle R x x tinmaiqpuk
___ Northern Harrier C C U* -
___ Sharp-shinned Hawk R R R -
___ Northern Goshawk R R R -
___ Red-tailed Hawk R x x -
___ Rough-legged Hawk O* O* O* kilgiq
___ Golden Eagle O* R O* -
FALCONS CAKR KOVA NOAT Eskimo Name
___ American Kestrel R* R R -
___ Merlin O O O kingavaichaiq
___ Peregrine Falcon R* R x -
___ Gyrfalcon O* O O* -
GALLINACEOUS BIRDS CAKR KOVA NOAT Eskimo Name
___ Spruce Grouse R O* U* napaaqtuum
___ Willow Ptarmigan F* C* F* aqargiq
___ Rock Ptarmigan U* U U* niqsaaqtuniq
CRANES CAKR KOVA NOAT Eskimo Name
___ Sandhill Crane F* U U* tattirgaq
PLOVERS CAKR KOVA NOAT Eskimo Name
___ Black-bellied Plover R* x x -
___ American Golden-Plover F* O U* tullik
___ Pacific Golden Plover R x U* -
___ Semipalmated Plover R* R C* -
___ Killdeer R x x -
SHOREBIRDS CAKR KOVA NOAT Eskimo Name
___ Greater Yellowlegs R x x -
___ Lesser Yellowlegs R U R* tinmiam qipmia
___ Wandering Tattler R R R* -
___ Spotted Sandpiper R R O* -
___ Solitary Sandpiper x U R* -
___ Upland Sandpiper R x U* -
___ Whimbrel O* O U* -
___ Bristle-thighed Curlew R x x -
___ Hudsonian Godwit R x x -
___ Bar-tailed Godwit F* x x -
___ Ruddy Turnstone R x x -
___ Black Turnstone U* x O -
___ Surfbird R R x -
___ Red Knot O x x -
___ Sanderling R R x -
___ Semipalmated Sandpiper C* R C* -
___ Western Sandpiper C* R x -
___ Rufous-necked Stint R x x -
___ Temminck's Stint R x x -
___ Least Sandpiper R R R* -
___ Baird's Sandpiper O* R O -
___ Pectoral Sandpiper C* C C -
___ Sharp-tailed Sandpiper R x x -
___ Rock Sandpiper R x x -
___ Dunlin F* x x -
___ Stilt Sandpiper R x x -
___ Buff-breasted Sandpiper R x R -
___ Ruff R x x -
___ Long-billed Dowitcher F* R C* -
___ Common Snipe U* O* U* -
___ Red Phalarope O x x -
___ Red-necked Phalarope F* U C* saavauraq
JAEGERS, GULLS, & TERNS CAKR KOVA NOAT Eskimo Name
___ Parasitic Jaeger F* x C isrunaq
___ Long-tailed Jaeger F* F C* -
___ Pomarine Jaeger F U x -
___ Bonaparte's Gull R U x tigitigaq
___ Mew Gull F* U C* nauyatchiaq
___ Herring Gull O R O -
___ Thayer's Gull R x x -
___ Slaty-backed Gull R x x -
___ Glaucous-winged Gull R* O x -
___ Glaucous Gull F* U* C* nauyasugruk
___ Black-legged Kittiwake O O x -
___ Ross's Gull R x x -
___ Sabine's Gull O R x aqargiyiaq
___ Ivory Gull R x x -
___ Arctic Tern F* U F* mitqutailaq
___ Aleutian Tern R* x x -
AUKS & PUFFINS CAKR KOVA NOAT Eskimo Name
___ Common Murre R x x -
___ Thick-billed Murre R x x -
___ Black Gullimot R x x -
___ Kittlitz's Murrelet R x x -
___ Horned Puffin R x x -
OWLS CAKR KOVA NOAT Eskimo Name
___ Great Horned Owl R O* R nukisagaq
___ Snowy Owl R R x ukpik
___ Northern Hawk-Owl R U R -
___ Great Gray Owl R x x -
___ Short-eared Owl U O U -
___ Boreal Owl R R x -
NIGHTJARS CAKR KOVA NOAT Eskimo Name
___ Lesser Nighthawk R x x -
WOODPECKERS CAKR KOVA NOAT Eskimo Name
___ Northern Flicker R R R* -
___ Three-toed Woodpecker U O O* tuuyuq
KINGFISHERS CAKR KOVA NOAT Eskimo Name
___ Belted Kingfisher x O C* nakuutchiqiq
FLYCATCHERS CAKR KOVA NOAT Eskimo Name
___ Olive-sided Flycatcher x R R -
___ Western Wood Pewee x x R -
___ Alder Flycatcher R R R -
___ Say's Phoebe R* R R* -
___ Eastern Kingbird R x x -
LARKS CAKR KOVA NOAT Eskimo Name
___ Horned Lark O* x C* -
SWALLOWS CAKR KOVA NOAT Eskimo Name
___ Tree Swallow U* O* U* tulugagnauraq
___ Violet-green Swallow R x x -
___ Bank Swallow O* O* O* -
___ Cliff Swallow R R U* -
JAYS, CROWS, & MAGPIES CAKR KOVA NOAT Eskimo Name
___ Gray Jay U* C* O* kiiriq
___ Common Raven C* C C* tulugaq
TITMICE & CHICKADEES CAKR KOVA NOAT Eskimo Name
___ Black-capped Chickadee R R x -
___ Siberian Tit R R* R -
___ Boreal Chickadee O U* R* -
___ American Dipper x U x -
THRUSHES CAKR KOVA NOAT Eskimo Name
___ Arctic Warbler R* R R* -
___ Ruby-crowned Kinglet R U R -
___ Bluethroat R x R* -
___ Northern Wheatear R O C* -
___ Gray-cheeked Thrush O C* O* -
___ Swainson's Thrush R R R -
___ Hermit Thrush R x x kanayuq
___ American Robin R* R R* -
___ Varied Thrush x F C* -
WAGTAILS & PIPITS CAKR KOVA NOAT Eskimo Name
___ Yellow Wagtail C R C* pigaq
___ White Wagtail R x x -
___ Black-backed Wagtail R x x -
___ Red-throated Pipit R x x -
___ American Pipit R* O C* -
WAXWINGS CAKR KOVA NOAT Eskimo Name
___ Bohemian Waxwing R U U* -
SHRIKES CAKR KOVA NOAT Eskimo Name
___ Northern Shrike O* U* O* iraiyaruuq
WARBLERS, SPARROWS,BUNTINGS, & BLACKBIRDS CAKR KOVA NOAT Eskimo Name
___ Orange-crowned Warbler R R U* -
___ Yellow Warbler O C O* sunaqpaluktuuraq
___ Yellow-rumped Warbler R C O* -
___ Blackpoll Warbler R C C* -
___ Northern Waterthrush R* R O* -
___ Wilson's Warbler O U O* -
___ American Tree Warbler F* F A* -
___ Savannah Sparrow A* A A* -
___ Fox Sparrow U U C* -
___ Lincoln's Sparrow x R x -
___ Golden-crowned Sparrow R U O* -
___ White-crowned Sparrow C C* C* -
___ Dark-eyed Junco R U* R* -
___ Lapland Longspur A* O* A* -
___ Snow Bunting R R R amautlikauraq
___ McKay's Bunting R x x -
___ Rusty Blackbird R U R tulukkam ittuq
FINCHES CAKR KOVA NOAT Eskimo Name
___ Rosy Finch R x U -
___ Pine Grosbeak R U* R* qayuttaaq
___ White-winged Crossbill R F* x -
___ Common Redpoll F* F* F* saksakiiraq
___ Hoary Redpoll F* F* F* -
Bird list of the Gates of the Arctic National Park and Preserve:
Loons and Greebes
Red-throated Loon, Pacific Loon, Common Loon, Yellow-billed Loon, Horned Grebe, Red-necked Grebe,
Waterfowl Tundra Swan Trumpeter Swan Greater White-fronted Goose Snow Goose Emperor Goose Canada Goose Brant Mallard Green-winged Teal American Widgeon Northern Pintail Northern Shoveler Canvasback Greater Scaup Lesser Scaup Common Eider King Eider Black Scoter White-winged Scoter Surf Scoter Harlequin Duck Old Squaw Common Goldeneye Bufflehead Red-breasted Merganser
Grouse Spruce Grouse Ruffed Grouse Sharp-tailed Grouse Willow Ptarmigan Rock Ptarmigan
Cranes Sandhill Crane
Shorebirds Semipalmated Plover Black-bellied Plover Lesser Golden Plover Bar-tailed Godwit Whimbrel Lesser Yellowlegs Solitary Sandpiper Spotter Sandpiper Wandering Tattler Red-necked Phalarope Red Phalarope Long-billed Dowitcher Stilt Sandpiper Common Snipe Ruddy Turnstone Surfbird Dunlin Sanderling White-rumped Sandpiper Western Sandpiper Least Sandpiper Semipalmated Sandpiper Baird's Sandpiper Pectoral Sandpiper Upland Sandpiper Buff-breasted Sandpiper
Gulls and Jaegers Parasitic Jaeger Pomarine Jaeger Long-tailed Jaeger Bonaparte's Gull Herring Gull Glaucous Gull Mew Gull Glaucous-winged Gull Sabine's Gull Arctic Tern
Owls Short-eared Owl Great-horned Owl Great Gray Owl Snowy Owl Boreal Owl Northern Hawk-Owl Belted Kingfisher
Woodpeckers Northern Flicker Downy Woodpecker Hairy Woodpecker Three-toed Woodpecker Black-backed Woodpecker
Passerines Olive-sided Flycatcher Say's Phoebe Alder Flycatcher Horned Lark Tree Swallow Violet-green Swallow Bank Swallow Cliff Swallow Gray Jay Common Raven Black-capped Chickadee Siberian Tit Boreal Chickadee Arctic Warbler Ruby-crowned Kinglet Swainson's Thrush Gray-cheeked Thrush Varied Thrush American Robin Northern Wheatear Bluethroat Northern Shrike American(Water) Pipit Yellow Wagtail American Dipper Bohemian Waxwing Orange-crowned Warbler Yellow-rumped(Myrtle) Warbler Blackpole Warbler Yellow Warbler Wilson's Warbler Northern Waterthrush Savannah Sparrow American Tree Sparrow Dark-eyed Junco Golden-crowned Sparrow White-crowned Sparrow Fox Sparrow Lincoln's Sparrow Smith's Longspur Lapland Longspur Snow Bunting Rusty Blackspur White-winged Crossbill Pine Grosbeak Common Redpoll Hoary Redpoll Rosy Finch