Canada Lynx (Lynx Canadensis) in Eastern North American
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MINNESOTA MUSTELIDS Young
By Blane Klemek MINNESOTA MUSTELIDS Young Naturalists the Slinky,Stinky Weasel family ave you ever heard anyone call somebody a weasel? If you have, then you might think Hthat being called a weasel is bad. But weasels are good hunters, and they are cunning, curious, strong, and fierce. Weasels and their relatives are mammals. They belong to the order Carnivora (meat eaters) and the family Mustelidae, also known as the weasel family or mustelids. Mustela means weasel in Latin. With 65 species, mustelids are the largest family of carnivores in the world. Eight mustelid species currently make their homes in Minnesota: short-tailed weasel, long-tailed weasel, least weasel, mink, American marten, OTTERS BY DANIEL J. COX fisher, river otter, and American badger. Minnesota Conservation Volunteer May–June 2003 n e MARY CLAY, DEMBINSKY t PHOTO ASSOCIATES r mammals a WEASELS flexible m Here are two TOM AND PAT LEESON specialized mustelid feet. b One is for climb- ou can recognize a ing and the other for hort-tailed weasels (Mustela erminea), long- The long-tailed weasel d most mustelids g digging. Can you tell tailed weasels (M. frenata), and least weasels eats the most varied e food of all weasels. It by their tubelike r which is which? (M. nivalis) live throughout Minnesota. In also lives in the widest Ybodies and their short Stheir northern range, including Minnesota, weasels variety of habitats and legs. Some, such as badgers, hunting. Otters and minks turn white in winter. In autumn, white hairs begin climates across North are heavy and chunky. Some, are excellent swimmers that hunt to replace their brown summer coat. -
Food Habits of Black Bears in Suburban Versus Rural Alabama
Food Habits of Black Bears in Suburban versus Rural Alabama Laura Garland, Auburn University, School of Forestry and Wildlife Sciences, Auburn, AL 36849 Connor Ellis, 18832 #1 Gulf Boulevard Indian Shores, FL 33785 Todd Steury, Auburn University, School of Forestry and Wildlife Sciences, Auburn, AL 36849 Abstract: Little is known about the food habits of black bears (Ursus americanus) in Alabama. A major concern is the amount of human influence in the diet of these bears as human and bear populations continue to expand in a finite landscape and bear-human interactions are increasing. To better understand dietary habits of bears, 135 scats were collected during late August to late November 2011–2014. Food items were classified into the cat- egories of fruit, nuts/seeds, insects, anthropogenic, animal hairs, fawn bones, and other. Plant items were classified down to the lowest possible taxon via visual and DNA analysis as this category composed the majority of scat volumes. Frequency of occurrence was calculated for each food item. The most commonly occurring foods included: Nyssa spp. (black gum, 25.2%), Poaceae family (grass, 24.5%), Quercus spp. (acorn, 22.4%), and Vitis spp. (muscadine grape, 8.4%). Despite the proximity of these bear populations to suburban locations, during our sampling period we found that their diet primarily comprised vegetation, not anthropogenic food; while 100% of scat samples contained vegetation, only 19.6% of scat samples contained corn and no other anthropogenic food sources were detected. Based on a Fisher’s exact test, dietary composition did not differ between bears living in subur- ban areas compared to bears occupying more rural areas (P = 0.3891). -
FISHER Pekania Pennanti
WILDLIFE IN CONNECTICUT WILDLIFE FACT SHEET FISHER Pekania pennanti Background J. FUSCO © PAUL In the nineteenth century, fishers became scarce due to forest logging, clearing for agriculture, and overexploitation. By the 1900s, fishers were considered extirpated from the state. Reforestation and changes in land-use practices have restored the suitability of the fisher’s habitat in part of its historic range, allowing a population to recolonize the northeastern section of the state. Fishers did not recolonize suitable habitat in northwestern Connecticut, since the region was isolated from a source population. Fishers were rare in western Massachusetts, and the developed and agricultural habitats of the Connecticut River Valley were a barrier to westward expansion by fishers in northeastern Connecticut. A project to reintroduce this native mammal into northwestern Connecticut was initiated by the Wildlife Division in 1988. Funds from reimbursement of trapping wild turkeys in Connecticut for release in Maine were used to purchase fishers caught by cooperating trappers in New Hampshire and Vermont. In what is termed a "soft release," fishers were penned and fed at the release site for a couple of weeks prior to being released. Through radio and snow tracking, biologists later found that the fishers that were released in northwestern Connecticut had high survival rates and successfully reproduced. As a result of this project, a viable, self-sustaining population of this native mammal is now established in western Connecticut. Fishers found throughout eastern Connecticut are a result of natural range expansion. In 2005, Connecticut instituted its first modern day regulated trapping season for fishers. Most northern states have regulated fisher trapping seasons. -
2021 Fur Harvester Digest 3 SEASON DATES and BAG LIMITS
2021 Michigan Fur Harvester Digest RAP (Report All Poaching): Call or Text (800) 292-7800 Michigan.gov/Trapping Table of Contents Furbearer Management ...................................................................3 Season Dates and Bag Limits ..........................................................4 License Types and Fees ....................................................................6 License Types and Fees by Age .......................................................6 Purchasing a License .......................................................................6 Apprentice & Youth Hunting .............................................................9 Fur Harvester License .....................................................................10 Kill Tags, Registration, and Incidental Catch .................................11 When and Where to Hunt/Trap ...................................................... 14 Hunting Hours and Zone Boundaries .............................................14 Hunting and Trapping on Public Land ............................................18 Safety Zones, Right-of-Ways, Waterways .......................................20 Hunting and Trapping on Private Land ...........................................20 Equipment and Fur Harvester Rules ............................................. 21 Use of Bait When Hunting and Trapping ........................................21 Hunting with Dogs ...........................................................................21 Equipment Regulations ...................................................................22 -
Lynx, Felis Lynx, Predation on Red Foxes, Vulpes Vulpes, Caribou
Lynx, Fe/is lynx, predation on Red Foxes, Vulpes vulpes, Caribou, Rangifer tarandus, and Dall Sheep, Ovis dalli, in Alaska ROBERT 0. STEPHENSON, 1 DANIEL V. GRANGAARD,2 and JOHN BURCH3 1Alaska Department of Fish and Game, 1300 College Road, Fairbanks, Alaska, 99701 2Alaska Department of Fish and Game, P.O. Box 305, Tok, Alaska 99780 JNational Park Service, P.O. Box 9, Denali National Park, Alaska 99755 Stephenson, Robert 0., Daniel Y. Grangaard, and John Burch. 1991. Lynx, Fe/is lynx, predation on Red Foxes, Vulpes vulpes, Caribou, Rangifer tarandus, and Dall Sheep, Ovis dalli, in Alaska. Canadian Field-Naturalist 105(2): 255- 262. Observations of Canada Lynx (Fe/is lynx) predation on Red Foxes ( Vulpes vulpes) and medium-sized ungulates during winter are reviewed. Characteristics of I 3 successful attacks on Red Foxes and 16 cases of predation on Caribou (Rangifer tarandus) and Dall Sheep (Ovis dalli) suggest that Lynx are capable of killing even adults of these species, with foxes being killed most easily. The occurrence of Lynx predation on these relatively large prey appears to be greatest when Snowshoe Hares (Lepus americanus) are scarce. Key Words: Canada Lynx, Fe/is lynx, Red Fox, Vulpes vulpes, Caribou, Rangifer tarandus, Dall Sheep, Ovis dalli, predation, Alaska. Although the European Lynx (Felis lynx lynx) quently reach 25° C in summer and -10 to -40° C in regularly kills large prey (Haglund 1966; Pullianen winter. Snow depths are generally below 80 cm, 1981), the Canada Lynx (Felis lynx canadensis) and snow usually remains loosely packed except at relies largely on small game, primarily Snowshoe high elevations. -
PICA Project Report (Action A2.2 & 2.3)
PICA Project Report (Action A2.2 & 2.3) Investigation of Pallas’s cat activity patterns and temporal interactions with sympatric species Authors: Katarzyna Ruta, Gustaf Samelius, David Barclay, Emma Nygren PICA - “Conservation of the Pallas’s cat through capacity building, research, and global planning” 1. Introduction: 1.1 Activity patterns of wild felids: Activity patterns form a part of species’ adaptation to their environment (Beltran & Delibes, 1994) and are therefore a fundamental aspect of animal behaviour (Nielsen, 1983; Weller & Bennett, 2001). Felids are generally considered to be crepuscular and nocturnal in their activity (Kitchener, 1991), although they are well adapted to function in a wide range of light conditions (Sunquist & Sunquist, 2002). Numerous abiotic pressures and biotic interactions are known to shape the temporal behaviour of (cat-like) carnivores (Marinho et al., 2018), including changes in temperature (Beltran & Delibes, 1994; Podolski et al., 2013), light (Huck et al., 2017; Heurich et al., 2014) and season (Podolski et al., 2013; Manfredi et al., 2011), sex and reproductive status of the animal (Kolbe & Squires, 2007; Schmidt, 1999; Schmidt et al., 2009), predation risk (Caro, 2005; Farías et al., 2012) and human disturbance (Wolf & Ale, 2009; Ale & Brown, 2009). Owing to the dietary constraints of carnivores whose preys have their own well-defined circadian rhythms (Halle, 2000; Zielinski, 2000), the availability and vulnerability of prey is, however, considered as one of the main influences on predator temporal activity (Zielinski, 1988; Lodé, 1995). According to Optimal Foraging Theory, predators are expected to synchronize their daily activity with the activity of their most profitable prey, increasing the probability of encounters while reducing energy expenditure (MacArthur & Pianka, 1966; Monterroso et al., 2013; Emmons, 1987). -
Estimating Sustainable Bycatch Rates for California Sea Lion Populations in the Gulf of California
Contributed Paper Estimating Sustainable Bycatch Rates for California Sea Lion Populations in the Gulf of California JARED G. UNDERWOOD,∗‡ CLAUDIA J. HERNANDEZ CAMACHO,∗† DAVID AURIOLES-GAMBOA,† AND LEAH R. GERBER∗ ∗Ecology, Evolution and Environmental Science, School of Life Sciences, Arizona State University, College & University Drive, Tempe, AZ 85287-1501, U.S.A. †Centro Interdisciplinario de Ciencias Marinas-IPN, Av. IPN s/n Col. Playa Palo de Santa Rita, La Paz BCS 23096, Mexico´ Abstract: Commercial and subsistence fisheries pressure is increasing in the Gulf of California, Mexico. One consequence often associated with high levels of fishing pressure is an increase in bycatch of marine mammals and birds. Fisheries bycatch has contributed to declines in several pinniped species and may be affecting the California sea lion (Zalophus californianus) population in the Gulf of California. We used data on fisheries and sea lion entanglement in gill nets to estimate current fishing pressure and fishing rates under which viable sea lion populations could be sustained at 11 breeding sites in the Gulf of California. We used 3 models to estimate sustainable bycatch rates: a simple population-growth model, a demographic model, and an estimate of the potential biological removal. All models were based on life history and census data collected for sea lions in the Gulf of California. We estimated the current level of fishing pressure and the acceptable level of fishing required to maintain viable sea lion populations as the number of fishing days (1 fisher/boat setting and retrieving 1 day’s worth of nets) per year. Estimates of current fishing pressure ranged from 101 (0–405) fishing days around the Los Machos breeding site to 1887 (842–3140) around the Los Islotes rookery. -
How to Avoid Incidental Take of American Marten
How to Avoid Incidental Take Of American Marten While Trapping or Snaring Mink and other Furbearers. Jon Stone The purpose of this information is to reduce injury and mortality to the Endangered American Marten population caused by trapping mink and/or other furbearers. Marten are similar in appearance and habits to mink, and their ranges overlap with other furbearer species, and with each other. Therefore, it is important for trappers to know how to distinguish marten from mink, to recognize their preferred habitat types, and to avoid capturing or harvesting marten. Trappers must also learn what to do if a marten is caught incidentally. American marten Current Status Researchers speculate the current American marten (Martes americana) population on Cape Breton Island may be less than 50 animals. Consequently, in the summer of 2001, the marten population on Cape Breton Island was provincially listed as "endangered" under the Nova Scotia Endangered Species Act. Thought to be extirpated from the mainland, several marten re-introductions have been attempted. It seems these reintroductions have been successful, as there have been some very recent records of marten in southwest Nova Scotia. The status of the marten on the mainland is considered "data deficient," (meaning more research is required before giving it a designation). The harvesting of marten is not permitted in Nova Scotia. Time is of the Essence Small, localized populations, like the marten on Cape Breton Island, are vulnerable to local extinction. Factors such as inbreeding (a genetic effect), as well as habitat loss, accidental capture, starvation, and certain random events like disease, fire, and unusual weather events could eliminate the entire population. -
Canada Lynx Lynx Canadensis Fact Sheet Natural Resources April 2011 Conservation Service
Canada Lynx Lynx canadensis Fact Sheet Natural Resources April 2011 Conservation Service and seral lodgepole pine, is the primary vegetation type occupied. Cedar-hemlock forests may also be important. Mature forests with downed logs and windfalls provide cover for denning, escape, and protection from severe weather. Landscapes with a variety of forest age classes and cover types support large numbers of snowshoe hares for lynx foraging. Recent burns and cutting units may provide herbaceous summer foods for snowshoe hares and older, regenerating burns and cutting units provide Official Status: Threatened. woody browse for winter snowshoe hare Threatened species are species that are likely to populations. Cold, dry snow conditions give lynx a become endangered within the foreseeable future competitive advantage with their long legs and large throughout all or a significant portion of their range. feet, which act as snowshoes. Listed Federal Register Volume 63, No. 58, March 24, 2000. Historical Status The Canada lynx once occupied 16 of the contiguous United States (Maine, New Hampshire, Vermont, New York, Massachusetts, Pennsylvania, Michigan, Wisconsin, Minnesota, Washington, Oregon, Idaho, Montana, Wyoming, Utah, and Colorado) as well as present day range in mountainous and boreal forest habitats throughout Canada and Alaska. Present Status Small populations of lynx remain in only three of the 16 contiguous states originally inhabited: Montana, Life History Washington, and Maine. If lynx still exist in any of Mating occurs through March and April; kittens are the other lower 48 states, they are very rare. born during May and June after a 62-day gestation Habitat period. Litter size averages 2 (1-4). -
The Scientific Basis for Conserving Forest Carnivores: American Marten, Fisher, Lynx and Wolverine in the Western United States
United States The Scientific Basis for Conserving Forest Carnivores Department of Agriculture Forest Service American Marten, Fisher, Lynx, Rocky Mountain and Wolverine Forest and Range Experiment Station in the Western United States Fort Collins, Colorado 80526 General Technical Report RM-254 Abstract Ruggiero, Leonard F.; Aubry, Keith B.; Buskirk, Steven W.; Lyon, L. Jack; Zielinski, William J., tech. eds. 1994. The Scientific Basis for Conserving Forest Carnivores: American Marten, Fisher, Lynx and Wolverine in the Western United States. Gen. Tech. Rep. RM-254. Ft. Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 184 p. This cooperative effort by USDA Forest Service Research and the National Forest System assesses the state of knowledge related to the conservation status of four forest carnivores in the western United States: American marten, fisher, lynx, and wolverine. The conservation assessment reviews the biology and ecology of these species. It also discusses management considerations stemming from what is known and identifies information needed. Overall, we found huge knowledge gaps that make it difficult to evaluate the species’ conservation status. In the western United States, the forest carnivores in this assessment are limited to boreal forest ecosystems. These forests are characterized by extensive landscapes with a component of structurally complex, mesic coniferous stands that are characteristic of late stages of forest development. The center of the distrbution of this forest type, and of forest carnivores, is the vast boreal forest of Canada and Alaska. In the western conterminous 48 states, the distribution of boreal forest is less continuous and more isolated so that forest carnivores and their habitats are more fragmented at the southern limits of their ranges. -
Sierra Nevada Red Fox (Vulpes Vulpes Necator): a Conservation Assessment
Sierra Nevada Red Fox (Vulpes vulpes necator): A Conservation Assessment John D. Perrine * Environmental Science, Policy and Management Department and Museum of Vertebrate Zoology University of California, Berkeley Lori A. Campbell** USDA Forest Service Pacific Southwest Research Station Sierra Nevada Research Center Davis, California Gregory A. Green Tetra Tech EC Bothell, Washington Current address and contact information: *Primary Author: J. Perrine, Biological Sciences Department, California Polytechnic State University, San Luis Obispo, CA 93407-0401 [email protected] **L. Campbell, School of Veterinary Medicine, University of California, Davis, One Shields Avenue, Davis, CA 95616 Perrine, Campbell and Green R5-FR-010 August 2010 NOTES IN PROOF • Genetic analyses by B. Sacks and others 2010 (Conservation Genetics 11:1523-1539) indicate that the Sacramento Valley red fox population is native to California and is closely related to the Sierra Nevada red fox. They designated the Sacramento Valley red fox as a new subspecies, V. v. patwin. • In August 2010, as this document was going to press, biologists on the Humboldt-Toiyabe National Forest detected a red fox at an automatic camera station near the Sonora Pass along the border of Tuolomne and Mono Counties. Preliminary genetic analyses conducted at UC Davis indicate that the fox was a Sierra Nevada red fox. Further surveys and analyses are planned. • The California Department of Fish and Game Region 1 Timber Harvest Program has established a Sierra Nevada red fox information portal, where many management-relevant documents can be downloaded as PDFs. See: https://r1.dfg.ca.gov/Portal/SierraNevadaRedFox/tabid/618/Default.aspx Sierra Nevada Red Fox Conservation Assessment EXECUTIVE SUMMARY This conservation assessment provides a science-based, comprehensive assessment of the status of the Sierra Nevada red fox (Vulpes vulpes necator) and its habitat. -
OREGON FURBEARER TRAPPING and HUNTING REGULATIONS
OREGON FURBEARER TRAPPING and HUNTING REGULATIONS July 1, 2020 through June 30, 2022 Please Note: Major changes are underlined throughout this synopsis. License Requirements Trapper Education Requirement By action of the 1985 Oregon Legislature, all trappers born after June 30, Juveniles younger than 12 years of age are not required to purchase a 1968, and all first-time Oregon trappers of any age are required to license, except to hunt or trap bobcat and river otter. However, they must complete an approved trapper education course. register to receive a brand number through the Salem ODFW office. To trap bobcat or river otter, juveniles must complete the trapper education The study guide may be completed at home. Testing will take place at course. Juveniles 17 and younger must have completed hunter education Oregon Department of Fish and Wildlife (ODFW) offices throughout the to obtain a furtaker’s license. state. A furtaker’s license will be issued by the Salem ODFW Headquarters office after the test has been successfully completed and Landowners must obtain either a furtaker’s license, a hunting license for mailed to Salem headquarters, and the license application with payment furbearers, or a free license to take furbearers on land they own and on has been received. Course materials are available by writing or which they reside. To receive the free license and brand number, the telephoning Oregon Department of Fish and Wildlife, I&E Division, 4034 landowner must obtain from the Salem ODFW Headquarters office, a Fairview Industrial Drive SE, Salem, OR 97302, (800) 720-6339 x76002. receipt of registration for the location of such land prior to hunting or trapping furbearing mammals on that land.