Arctic Char in Northern Alaska
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Dolly Varden (Salvelinus Malma) Robert H. Armstrong and Marge
Dolly Varden (Salvelinus malma) Robert H. Armstrong and Marge Hermans The Dolly Varden is one of the most beautiful fishes in Resident Dolly Varden, which live their entire lives Southeastern Alaska (Southeast). This species is also in streams or small lakes and ponds, are small. They highly prized as a sport fish and for delicious eating. seldom grow longer than 10 in. (26 cm). Those that The sea-run Dolly Varden has an overall silvery inhabit larger lakes often grow to 12 in. (30 cm) or appearance with olive-green to brown on its dorsal more, but they still generally weigh less than 1 lb (0.5 surface and numerous red to orange spots on its sides kg). These freshwater fish seldom live more than 8 to (Fig 1). At maturity the lower body of the breeding 10 years. Exceptions are Dolly Varden weighing up to male turns brilliant red. 9 lb (4 kg) in the few Southeast lakes that contain kokanee (small landlocked sockeye salmon [Onchorhynchus nerka]). These larger fish feed on kokanee and tend to live longer, up to 19 years (Armstrong 1991). Sea-run Dolly Varden, fish that spend part of their lives in salt water, usually grow to 15-22 in. (38-56 cm) long and weigh 1-3 lb (0.5-1.4 kg). Occasionally, large fish weighing more than 10 lb (5 kg) are hauled from large mainland rivers such as the Taku River near Juneau. Research has shown that sea-run Dolly Varden are not nearly as abundant in Southeast as most people believe. -
The Arctic Char (Salvelinus Alpinus) “Complex” in North America Revisited
The Arctic char (Salvelinus alpinus) “complex” in North America revisited Eric B. Taylor Hydrobiologia The International Journal of Aquatic Sciences ISSN 0018-8158 Hydrobiologia DOI 10.1007/s10750-015-2613-6 1 23 Author's personal copy Hydrobiologia DOI 10.1007/s10750-015-2613-6 CHARR II Review Paper The Arctic char (Salvelinus alpinus) ‘‘complex’’ in North America revisited Eric B. Taylor Received: 1 July 2015 / Revised: 16 November 2015 / Accepted: 5 December 2015 Ó Springer International Publishing Switzerland 2015 Abstract The Arctic char (Salvelinus alpinus) law. This research has significantly revised what species ‘‘complex’’ has fascinated biologists for constitutes the S. alpinus species ‘‘complex’’, provided decades particularly with respect to how many species insights into the ecology and genetics of co-existence, there are and their geographic distributions. I review and promoted conservation assessment that better recent research on the species complex, focussing on represents biodiversity within Salvelinus. A geograph- biodiversity within northwestern North America, ically and genetically comprehensive analysis of which indicates (i) what was once considered a single relationships among putative taxa of Pan-Pacific taxon consists of three taxa: S. alpinus (Arctic char), S. Salvelinus is still required to better quantify the malma (Dolly Varden), and S. confluentus (bull trout), number of taxa and their origins. (ii) morphological and genetic data indicate that S. alpinus and S. malma, and S. malma and S. confluentus Keywords Dolly Varden Á Arctic char Á Bull trout Á exist as distinct biological species in sympatry, (iii) Geographic distribution Á Taxonomy Á Conservation sympatric forms of S. alpinus exist in Alaska as in other areas of the Holarctic, (iv) Dolly Varden comprises two well-differentiated subspecies, S. -
Bonneville Cutthroat Trout (Oncorhynchus Clarki Utah) Bonneville Cutthroat Trout Is One of Three Cutthroat Trout Subspecies Native to Utah
FISH Bonneville Cutthroat Trout (Oncorhynchus clarki utah) Bonneville cutthroat trout is one of three cutthroat trout subspecies native to Utah. Bonneville cutthroat trout historically occurred in the Pleistocene Lake Bonneville basin, which included portions of Idaho, Nevada, Utah, and Wyoming (Kershner 1995). The desiccation of Lake Bonneville into the smaller Great Salt Lake and fragmentation of other stream and lake habitats may have led to three slightly differentiated groups of Bonneville cutthroat trout. These groups are found in the Bonneville basin proper, the Bear River drainage, and the Snake Valley (Behnke 1992). There are five known populations of pure strain Bonneville cutthroat trout on the Fishlake National Forest inhabiting approximately 38 miles of stream habitat. There are several recently reintroduced populations, and several small potential remnant populations. Habitat for the Bonneville cutthroat trout is widely distributed and variable. It ranges from high elevation (3,500 m mean sea level) streams with coniferous and deciduous riparian trees to low elevation (1,000 m mean sea level) streams in sage-steppe grasslands containing herbaceous riparian zones. As such, Bonneville cutthroat trout have adapted to a broad spectrum of habitat conditions throughout their range (Kershner 1995). Sexual maturity is typically reached during the second year for males and the third year for females (May et al. 1978). Both the age at maturity and the annual timing of spawning vary geographically with elevation, temperature, and life history strategy. Lake resident trout may begin spawning at two years of age and usually continue throughout their lives, while adfluvial individuals may not spawn for several years. -
R&E Funds Lahontan Cutthroat Surveys
OREGON FISHWORKS Winter 2006 News from the Oregon Department of Fish and Wildlife’s (ODFW) Fish Restoration and Enhancement (R&E) and Salmon and Trout Enhancement Programs (STEP) R&E Funds Lahontan Cutthroat Surveys his summer, crews from ODFW’s Native Fish Investigations Project surveyed Lahontan cutthroat trout populations and distribution in the TWillow and Whitehorse Creek basins in Harney County, funded in part with a $4,000 R&E Program grant. The surveys, which were completed in September, were done as part of an ongoing recovery effort. The last survey for these fish was conducted in 1999. The Willow and Whitehorse Creek basins provide some of the last remaining intact habitat for Oregon’s Lahontan cutthroat trout. Lahontan cutthroat trout in the Willow and Whitehorse Basins were designated as ‘threatened’ under the federal Endangered Species Act in 1991 — the year This 12.4-inch Lahontan cutthroat after angling for them was closed for their conservation. The fishing season was trout was one of the larger ones re-opened in 2001 on a catch-and-release, artificial flies or lures only basis. captured by ODFW survey crews. Populations improved during the 1990s largely due to better grazing Photo by Stephanie Gunckel management practices, which have resulted in much improved habitat conditions for the fish. The Trout Creek Mountains Working Group, a coalition of ranchers, government agencies and others that was formed in the late 1980s to lead Lahontan trout recovery efforts in the area, has been a driving force in the slow comeback of the fish. Although the data is still being evaluated, the overall picture looks promising. -
Westslope Cutthroat Trout
This file was created by scanning the printed publication. Errors identified by the software have been corrected; Chapter 1 however, some errors may remain. Westslope Cutthroat Trout John D. IVIclntyre and Bruce E. Rieman, USDA Forest Service, Intermountain Research Station, 316 E. iViyrtle Street, Boise, Idaho 83702 Introduction Westslope cutthroat trout begin to mature at age 3 but usually spawn first at age 4 or 5 (table 2). Sexu The westslope cutthroat trout inhabits streams on ally maturing adfluvial fish move into the vicinity of both sides of the Continental Divide. On the east side tributaries in fall and winter where they remain un of the divide, they are distributed mostly in Mon til they begin to migrate upstream in the spring tana but also occur in some headwaters in Wyoming (Liknes 1984). They spawn from March to July at and southern Alberta (Behnke 1992). They are in the water temperatures near 10°C (Roscoe 1974; Liknes Missouri Basin downstream to about 60 km below 1984; Shepard et al. 1984). A population of adult fish Great Falls and in the headwaters of the Judith, Milk, in the St. Joe River, Idaho, included 1.6 females for and Marias rivers. On the west side of the Continen each male (Thurow and Bjornn 1978). Average length tal Divide the subspecies occurs in the upper was 334 mm for females and 366 mm for males. A Kootenai River; the Clark Fork drainage in Montana similar population in Big Creek, Montana, included and Idaho downstream to the falls on the Fend Oreille 4.1 females for each male (Huston et al. -
Lake Trout Management Plan
LAKE TROUT MANAGEMENT PLAN DEPARTMENT OF INLAND FISHERIES AND WILDLIFE DIVISION OF FISHERIES AND HATCHERIES PREPARED BY PAUL JOHNSON REGIONAL FISHERIES BIOLOGIST REGION E MARCH 2001 LAKE TROUT LIFE HISTORY Description The lake trout (Salvelinus namaycush) lacks the distinctive coloration of its close relative, the eastern brook trout. Lake trout are usually either dark green or grayish brown in color, with white or pale yellow bean-shaped spots. In clear waters lake trout are often so silvery that the white spots are difficult to see. In stained waters they are very dark, almost black. Generally, a narrow border of white is present along the anterior margins of the pectoral, pelvic, and anal fins. This is most pronounced during spawning; however, at no time is this border as accentuated as it is on the fins of the brook trout. Lake trout fins are not orange or orange-red, like those of the brook trout. Distribution Lake trout are distributed throughout Canada. In the United States their natural range was restricted to northern New England, the Great Lakes, New York, Pennsylvania, Michigan, Minnesota, Montana, Idaho, and Alaska. In Maine they were originally found in about 100 lakes throughout the State. However, lake trout have been successfully reared in hatcheries. Consequently, their range has been extended considerably in the United States. In Maine they have been introduced into waters from Aroostook County in the north, to York County in the south. Throughout their native range lake trout are known by a wide variety of common names. In Maine they are called togue, whereas in other parts of the country and Canada they are referred to as mackinaw, salmon trout, lakers, grey trout, namaycush, Great Falls char, or mountain trout. -
Stevens Point Northern Aquaculture Demonstration Facility
University of Wisconsin- Stevens Point Northern Aquaculture Demonstration Facility • Greg Fischer • Facilities Operation Manager New Species for Wisconsin Aquaculture • Arctic Char?? WHY ARCTIC CHAR • Coldwater Species • Rapid growth – 1 kg(2.2 lbs) <17months • High quality flesh • Good market price with limited availability • High culture densities-120kg/m³(1.0lb/gal) • High fillet yield 50% + @market size 1-3 kg (2.2-6.6lbs) Comparsion between Arctic Char, Rainbow Trout, and Brook Trout in Weig ht Over Time from 20 g rams 900 800 700 600 AC -10 500 B K T-06 gms 400 R B T-08 300 200 100 0 0 30 60 90 120 150 180 210 240 270 300 330 360 390 Days of growth Days from 20 gms to 1.0 pd AC -10 R B T- 08 B K T-06 0 50 100 150 200 250 S eries2 Evaluation of photoperiod manipulation on Arctic Char growth, processing attributes, and sexual maturity in a coldwater recirculating system at UWSP-NADF Materials and Methods . The purpose of this study was to evaluate and compare arctic charr production attributes reared under two different photoperiods (24 hr and natural) in an RAS system. Troutlodge Inc. provided Nauyuk Lake (Canada) strain arctic charr eggs. Cultured 17 months from egg to market size (1.0 kg) (2.0 lbs) . Reared 10 months in RAS system . Project was conducted inside main aquatic barn at NADF. Materials and Methods Egg and Fry Culture . Eyed eggs incubated in Heath Stack .Flow thru 8.0°C(48F) degassed & aerated ground water. Fry were transferred to shallow (406 mm x 1219 mm) flow-thru fiberglass tank inserts. -
Onseriation of Bull Trout
United States - De artment of Iariculture Demographic and Forest Service Intermountain Research Statlon Habit4 Reauirements General Technical Report INT-302 for ~onseriationof September 1993 Bull Trout Bruce E. Rieman John D. Mclntyre THE AUTHORS CONTENTS BRUCE E. RlEMAN is a research fishery biologist with Page the lntermountain Research Station, Forestry Sciences Introduction ................................................................... 1 Laboratory in Boise, ID. He received a master's degree Ecology ......................................................................... 1 in fisheries management and a Ph.D. degree in for- Biology and Life History ............................................ 2 estry, wildlife, and range sciences from the University Population Structure.................................................. 3 of Idaho. He has worked in fisheries management and Biotic Interactions ...................................................... 3 research for 17 years with the ldaho Department of Habitat Relationships ................................................ 4 Fish and Game and the Oregon Department of Fish Summary ...................................................................7 and Wildlife. He joined the Forest Service in 1992. His Implications of Habitat Disturbance .............................. 7 current work focuses on the biology, dynamics, and' Extinction Risks ......................................................... 9 conservation of salmonid populations in the Intermoun- Viability ................................................................... -
Lake Superior Food Web MENT of C
ATMOSPH ND ER A I C C I A N D A M E I C N O I S L T A R N A T O I I O T N A N U E .S C .D R E E PA M RT OM Lake Superior Food Web MENT OF C Sea Lamprey Walleye Burbot Lake Trout Chinook Salmon Brook Trout Rainbow Trout Lake Whitefish Bloater Yellow Perch Lake herring Rainbow Smelt Deepwater Sculpin Kiyi Ruffe Lake Sturgeon Mayfly nymphs Opossum Shrimp Raptorial waterflea Mollusks Amphipods Invasive waterflea Chironomids Zebra/Quagga mussels Native waterflea Calanoids Cyclopoids Diatoms Green algae Blue-green algae Flagellates Rotifers Foodweb based on “Impact of exotic invertebrate invaders on food web structure and function in the Great Lakes: NOAA, Great Lakes Environmental Research Laboratory, 4840 S. State Road, Ann Arbor, MI A network analysis approach” by Mason, Krause, and Ulanowicz, 2002 - Modifications for Lake Superior, 2009. 734-741-2235 - www.glerl.noaa.gov Lake Superior Food Web Sea Lamprey Macroinvertebrates Sea lamprey (Petromyzon marinus). An aggressive, non-native parasite that Chironomids/Oligochaetes. Larval insects and worms that live on the lake fastens onto its prey and rasps out a hole with its rough tongue. bottom. Feed on detritus. Species present are a good indicator of water quality. Piscivores (Fish Eaters) Amphipods (Diporeia). The most common species of amphipod found in fish diets that began declining in the late 1990’s. Chinook salmon (Oncorhynchus tshawytscha). Pacific salmon species stocked as a trophy fish and to control alewife. Opossum shrimp (Mysis relicta). An omnivore that feeds on algae and small cladocerans. -
Brook Trout Outcome Management Strategy
Brook Trout Outcome Management Strategy Introduction Brook Trout symbolize healthy waters because they rely on clean, cold stream habitat and are sensitive to rising stream temperatures, thereby serving as an aquatic version of a “canary in a coal mine”. Brook Trout are also highly prized by recreational anglers and have been designated as the state fish in many eastern states. They are an essential part of the headwater stream ecosystem, an important part of the upper watershed’s natural heritage and a valuable recreational resource. Land trusts in West Virginia, New York and Virginia have found that the possibility of restoring Brook Trout to local streams can act as a motivator for private landowners to take conservation actions, whether it is installing a fence that will exclude livestock from a waterway or putting their land under a conservation easement. The decline of Brook Trout serves as a warning about the health of local waterways and the lands draining to them. More than a century of declining Brook Trout populations has led to lost economic revenue and recreational fishing opportunities in the Bay’s headwaters. Chesapeake Bay Management Strategy: Brook Trout March 16, 2015 - DRAFT I. Goal, Outcome and Baseline This management strategy identifies approaches for achieving the following goal and outcome: Vital Habitats Goal: Restore, enhance and protect a network of land and water habitats to support fish and wildlife, and to afford other public benefits, including water quality, recreational uses and scenic value across the watershed. Brook Trout Outcome: Restore and sustain naturally reproducing Brook Trout populations in Chesapeake Bay headwater streams, with an eight percent increase in occupied habitat by 2025. -
Stream Habitat Needs for Brook Trout and Brown Trout in the Driftless Area
Stream Habitat Needs for Brook Trout and Brown Trout in the Driftless Area Douglas J. Dietermana,1 and Matthew G. Mitrob aMinnesota Department of Natural Resources, Lake City, Minnesota, USA; bWisconsin Department of Natural Resources, Madison, Wisconsin, USA This manuscript was compiled on February 5, 2019 1. Several conceptual frameworks have been proposed to organize in Driftless Area streams. Our specific objectives were and describe fish habitat needs. to: (1) summarize information on the basic biology 2. The five-component framework recognizes that stream trout pop- of Brook Trout and Brown Trout in Driftless Area ulations are regulated by hydrology, water quality, physical habi- streams, (2) briefly review conceptual frameworks or- tat/geomorphology, connectivity, and biotic interactions and man- ganizing fish habitat needs, (3) trace the historical agement of only one component will be ineffective if a different com- evolution of studies designed to identify Brook Trout ponent limits the population. and Brown Trout habitat needs in the context of 3. The thermal niche of both Brook Trout Salvelinus fontinalis and these conceptual frameworks, (4) review Brook Trout- Brown Trout Salmo trutta has been well described. Brown Trout interactions and (5) discuss lingering un- 4. Selected physical habitat characteristics such as pool depths and certainties in habitat management for these species. adult cover, have a long history of being manipulated in the Driftless Area leading to increased abundance of adult trout. Brook Trout and Brown Trout Biology 5. Most blue-ribbon trout streams in the Driftless Area probably pro- vide sufficient habitat for year-round needs (e.g., spawning, feeding, Brook Trout. -
Effects of Rainbow Trout on Brook Trout Population Size in Tributaries to Lake Superior in Cook County, Minnesota
Effects of Rainbow Trout on Brook Trout Population Size in Tributaries to Lake Superior in Cook County, Minnesota Craig Tangren Biology Department Bemidji State University This study looked at the effects of Rainbow Trout stocking on the size of Brook Trout populations above migratory barriers. Linear mixed effects models were used to determine if there was a relationship between Brook Trout and Rainbow Trout catch rates. Age 1 or older Brook Trout populations were influenced by relative abundance of age 1 or older Rainbow Trout, according to the best supported model based on AIC scores. Population responses varied by stream, ranging along a gradient from high catch rates with a positive relationship to a negative relationship with low relative abundances. Streams with a positive relationship are likely more productive, with more prey and smaller territories, which allows for greater relative abundance. Streams with a weak relationship may have Brook Trout populations limited by the capacity for natural reproduction, a factor which would not influence Rainbow Trout. A clear negative relationship in some streams is likely due to density-dependent effects. This study did not perform an analysis comparing Brook Trout population sizes before and after the presence of Rainbow Trout. It is possible, but undetermined, that Brook Trout populations in this study would be larger if not for the introduction of Rainbow Trout. Management of Brook Trout and Rainbow Trout populations should be considered on a stream-by-stream basis due to the wide variation in population responses, and particular attention should be paid to the potential effects of Rainbow Trout introduction on streams with low abundances of Brook Trout.