Relevant bibliographies by topics / Alaska. Department of Fish and Game. Habitat Division

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Academic literature on the topic 'Alaska. Department of Fish and Game. Habitat Division'

Author: Grafiati
Published: 4 June 2021
Last updated: 11 February 2022

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Journal articles on the topic "Alaska. Department of Fish and Game. Habitat Division"

1

Thornton, Thomas F., and Harvey Kitka. "An Indigenous Model of a Contested Pacific Herring Fishery in Sitka, Alaska." International Journal of Applied Geospatial Research 6, no. 1 (January 2015): 94–117. http://dx.doi.org/10.4018/ijagr.2015010106.

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This paper uses GIS and spatiotemporal analysis of a historically and culturally modified marine ecosystem to evaluate Pacific herring abundance, declines, vulnerabilities, and future prospects, about which a Native Tribe and state fisheries managers disagree. In 2008, the Sitka Tribe of Alaska (STA) requested that an area within its traditional waters be closed to commercial sac roe fishing to protect spawning Pacific herring (Clupea pallasi), a key species for Native subsistence and marine ecosystem health. This proposal was opposed by the Alaska Department of Fish and Game (ADF&G), which estimated that adequate biomass was available to accommodate all herring users' needs. The disagreement exposes divisions between the Tribe's and the State's conceptualizations of the status, health, and management priorities for fisheries and marine ecosystems. The Tribe's model is one of cultivated abundance, wherein herring eggs are harvested conservatively and habitat is enhanced to make coastal spawning areas more productive, stable, and resilient. The State's paradigm, in contrast, follows a constitutional mandate to manage fisheries for Maximum Sustained Yield (MSY). A single-species biomass model is used to estimate a “surplus” herring for commercial roe harvesting within management areas. This work analyses and compares the spatiotemporal prescriptions of State and Indigenous models of herring fisheries management as they are used within debates over a closed area (Proposal 239), and assesses their relative potential for improving herring fisheries and marine ecosystem management using a combination of GIS spatial and scientific analysis and traditional ecological knowledge.
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2

Sutherland, Bob. "Harvest estimates of the Western Arctic caribou herd, Alaska." Rangifer 25, no. 4 (May 1, 2005): 177. http://dx.doi.org/10.7557/2.25.4.1782.

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A generalized least squares regression model was developed to estimate local harvest of the Western Arctic caribou (Rangifer tarandus granti) herd. This model provides herd and community level harvest based on community size, proximity of the herd to the village. The model utilizes community harvest survey information from the Alaska Department of Fish and Game, Subsistence Division and cooperation from the nonprofit organizations Maniliq and Kawerak. The model will assist in an annual selection of communities to survey. The predicted local resident harvest of the Western Arctic caribou herd is 14 700 with 95% lower and upper confidence limits of 10 100 and 19 700 respectively.
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3

Rooper, Christopher N., Lewis J. Haldorson, and Terrance J. Quinn II. "Habitat factors controlling Pacific herring (Clupea pallasi) egg loss in Prince William Sound, Alaska." Canadian Journal of Fisheries and Aquatic Sciences 56, no. 6 (June 1, 1999): 1133–42. http://dx.doi.org/10.1139/f99-050.

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Recruitment for many marine fishes is believed to be determined at an early life history stage. Pacific herring (Clupea pallasi) spawn in the intertidal and shallow subtidal zones and have a demersal egg stage that is susceptible to egg removals during incubation. Data were collected by the Alaska Department of Fish and Game in four years in Prince William Sound, Alaska, to identify important factors contributing to egg removals. We constructed analysis of variance models based on physical and biological variables to determine which environmental factors control egg loss rates. The habitat variables examined at each study transect were depth, wave exposure, north-south location, substrate, vegetation, mean bird abundance, abundance of loose eggs, and fish predation. Depth of spawn was the primary factor determining egg loss. Cumulative time of air exposure over incubation was substituted into the model for depth. Using the model, the total estimated egg loss from spawning to hatching ranged from 67 to 100% with an average of 75% (SE = 3.3%) in 1995. Eggs were originally deposited from 4 to -6 m depth relative to mean low water. The majority of eggs that remained in the spawning beds to hatching were deposited from 1 to -4 m depth. Egg removals due to avian predation were probably responsible for extreme egg loss rates at shallow depths.
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4

Crosby, Clara, John Bauer, and Dale Gardner. "THE ALASKA SHORELINE CLEANUP GUIDANCE AND STANDARDS MANUAL." International Oil Spill Conference Proceedings 2008, no. 1 (May 1, 2008): 1209–13. http://dx.doi.org/10.7901/2169-3358-2008-1-1209.

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ABSTRACT The Alaska Department of Environmental Conservation (ADEC) Spill Prevention and Response Division is compiling a Shoreline Cleanup Guidance and Standards Manual that captures statewide standards for oil-impacted shoreline cleanup and the lessons learned from previous spill response efforts, including the MIV Selendang AYU (2004), the M/V Kuroshima (1997), and the T/V Exxon Valdez (1989) oil spills. Important elements of the manual include the capture of cleanup endpoint criteria and prescribed controls required for specific techniques. The criteria and controls have been developed as a result of experience from previous oil spill cleanups. The criteria, reviewed and approved by State resources agency representatives from the Alaska Departments of Environmental Conservation, Fish and Game, and Natural Resources, now sets the statewide standard for shoreline cleanup of persistent oiling. The manual presents not only the State of Alaska'S shoreline endpoint standards but also the State'S requirements, policies, and expectations for cleanup of oil-impacted shorelines, including: the cleanup approval process; prescribed controls required for specific techniques; and the identification of current, ‘alternative’, or chemical shoreline treatment techniques that may be considered during shoreline cleanup operations. The manual describes many common shoreline cleanup techniques and outlines “best-use” practices, but does not identify new techniques or technologies. Conditions specific to Alaska are summarized, including primary shoreline types and primary oil types that are transported in bulk or most likely to be of concern. In most instances, the primary users will be incident management teams facilitating development of incident-specific shoreline cleanup plans. The manual will also serve ADEC staff, Responsible Parties, State and federal trustee agencies, and land managers.
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5

Berger, Joel, and Carol Cunningham. "Consequences of the Extirpation of Predators on Moose." UW National Parks Service Research Station Annual Reports 19 (January 1, 1995): 11–13. http://dx.doi.org/10.13001/uwnpsrc.1995.3229.

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This year was the first of our five year project. We established three primary study areas to examine possible biological effects of large predators on moose. Sites where fieldwork was conducted included apparent heavy predation by grizzly bears [the eastern slopes of the Talkeetna Mountains (Alaska)], little or no predation (Grand Teton National Park), and human predation (Bridger-Teton National Forest), the latter two in the southern portion of the Greater Yellowstone Ecosystem. Data were gathered in Alaska from April until August and, in Wyoming, for all months from February until August (except during April). At the southern Greater Yellowstone sites, information was collected on pregnancy rates, calf production, twinning, and juvenile and adult survivorship. Ecological and behavioral data gathered from all three sites included home range locations, foraging associations and rates, habitat use, group size, social interactions, migration, and responses to humans and potential predators. Twenty animals were radio-collared at the Wyoming site; as of December 1995 only 15 survived. One apparently starved to death, one was poached, one was legally shot, and two died of unknown causes. We improved our sample by using 13 females previously radio-collared on national forest lands by University of Wyoming and Wyoming Department of Game and Fish personnel. Of these, two died during the 1994-1995 winter and three had slipped their collars.
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Books on the topic "Alaska. Department of Fish and Game. Habitat Division"

1

Estes, Christopher C. Annual summary of Alaska Department of Fish and Game instream flow reservation applications. Anchorage: Alaska Dept. of Fish and Game, Division of Sport Fish, 1995.

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2

Estes, Christopher C. Annual summary of Alaska Department of Fish and Game instream flow reservation applications. Anchorage: Alaska Dept. of Fish and Game, Division of Sport Fish, 1993.

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3

Estes, Christopher C. Annual summary of Alaska Department of Fish and Game instream flow reservation applications. Anchorage, Alaska: Alaska Dept. of Fish and Game, Division of Sport Fish, 1991.

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Estes, Christopher C. Annual summary of Alaska Department of Fish and Game instream flow reservation applications. Anchorage, Alaska: Alaska Dept. of Fish and Game, Division of Sport Fish, 1992.

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5

Estes, Christopher C. Annual summary of Alaska Department of Fish and Game instream flow reservation applications. Anchorage: Alaska Dept. of Fish and Game, Division of Sport Fish, 1994.

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6

Montana. Legislature. Legislative Audit Division. Upland game bird habitat enhancement program Department of Fish, Wildlife and Parks, Wildlife Division: Performance audit. Helena, MT: Legislative Audit Division, State of Montana, 2000.

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7

Alaska Department of Fish and Game Exxon Valdez oil spill response operations report: Habitat Division, 1989-1992. Juneau, Alaska (P.O. Box 25526, Juneau 99802-5526): The Division, 1992.

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8

Review of North Slope, Alaska caribou research: Report to the Alaska Department of Fish and Game, December 1991. Washington, D.C. (1101 14th St., N.W., Washington 20005): Wildlife Management Institute, 1991.

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