Asian Otter Conservation Workshop, November 2013, Bengaluru, India
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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 -
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. -
The 2008 IUCN Red Listings of the World's Small Carnivores
The 2008 IUCN red listings of the world’s small carnivores Jan SCHIPPER¹*, Michael HOFFMANN¹, J. W. DUCKWORTH² and James CONROY³ Abstract The global conservation status of all the world’s mammals was assessed for the 2008 IUCN Red List. Of the 165 species of small carni- vores recognised during the process, two are Extinct (EX), one is Critically Endangered (CR), ten are Endangered (EN), 22 Vulnerable (VU), ten Near Threatened (NT), 15 Data Deficient (DD) and 105 Least Concern. Thus, 22% of the species for which a category was assigned other than DD were assessed as threatened (i.e. CR, EN or VU), as against 25% for mammals as a whole. Among otters, seven (58%) of the 12 species for which a category was assigned were identified as threatened. This reflects their attachment to rivers and other waterbodies, and heavy trade-driven hunting. The IUCN Red List species accounts are living documents to be updated annually, and further information to refine listings is welcome. Keywords: conservation status, Critically Endangered, Data Deficient, Endangered, Extinct, global threat listing, Least Concern, Near Threatened, Vulnerable Introduction dae (skunks and stink-badgers; 12), Mustelidae (weasels, martens, otters, badgers and allies; 59), Nandiniidae (African Palm-civet The IUCN Red List of Threatened Species is the most authorita- Nandinia binotata; one), Prionodontidae ([Asian] linsangs; two), tive resource currently available on the conservation status of the Procyonidae (raccoons, coatis and allies; 14), and Viverridae (civ- world’s biodiversity. In recent years, the overall number of spe- ets, including oyans [= ‘African linsangs’]; 33). The data reported cies included on the IUCN Red List has grown rapidly, largely as on herein are freely and publicly available via the 2008 IUCN Red a result of ongoing global assessment initiatives that have helped List website (www.iucnredlist.org/mammals). -
3. Aonyx Congicus Red List 2020
Aonyx congicus - Lönnberg, 1910 ANIMALIA - CHORDATA - MAMMALIA - CARNIVORA - MUSTELIDAE - Aonyx - congicus Common Names: Congo Clawless Otter (English), Cameroon Clawless Otter (English), Kleinkrallen- Fingerotter (German), Kongo-Fingerotter (German), Loutre à joues blanches du Cameroun (French), Loutre à joues blanches du Congo (French), Nutria Inerme de Camerún (Spanish; Castilian), Paraonyx tacheté (French), Small-clawed Otter (English), Small-toothed Clawless Otter (English), Zaire Clawless Otter (English) Synonyms: No Synonyms Taxonomic Note: Allen (1924) and Davis (1978) treated A. capensis and A. congicus as being conspecific, arguing that they represent clinal variations of the same species. However, mainly based on tooth size and skin differences, Rosevear (1974), Van Zyll de Jong (1987), Wozencraft (1993), and Larivière (2001) considered A. capensis and A. congicus as separate species, but this remains debated, and Wozencraft (2005) did not retain A. congicus as a valid species, contrary to the opinion of the IUCN SSC Otter Specialist Group (www.otterspecialistgroup.org) (Jacques et al. 2009). The name Aonyx congica is often found in the literature but A. congicus is the correct spelling as Aonyx, from the Greek ‘onux’, is masculine (Van Bree et al. 1999). Red List Status NT, A3cde (IUCN version 3.1) Red List Assessment Assessment Information Date of Assessment: 31/01/2020 Reviewed: 27/02/2020 Assessor(s): Jacques, H., Reed-Smith, J., Davenport, L. & Somers, M.J. Reviewer(s): Hussain, S.A., Duplaix, N. Contributor(s): Hoffmann, M. Facilitators/Compilers: NA Assessment Rationale All of Africa's otter species are threatened by alteration and/or degradation of freshwater habitats and riparian vegetation which are the preferred settlements of human population. -
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. -
Small Carnivores of Karnataka: Distribution and Sight Records1
Journal of the Bombay Natural History Society, 104 (2), May-Aug 2007 155-162 SMALL CARNIVORES OF KARNATAKA SMALL CARNIVORES OF KARNATAKA: DISTRIBUTION AND SIGHT RECORDS1 H.N. KUMARA2,3 AND MEWA SINGH2,4 1Accepted November 2006 2 Biopsychology Laboratory, University of Mysore, Mysore 570 006, Karnataka, India. 3Email: [email protected] 4Email: [email protected] During a study from November 2001 to July 2004 on ecology and status of wild mammals in Karnataka, we sighted 143 animals belonging to 11 species of small carnivores of about 17 species that are expected to occur in the state of Karnataka. The sighted species included Leopard Cat, Rustyspotted Cat, Jungle Cat, Small Indian Civet, Asian Palm Civet, Brown Palm Civet, Common Mongoose, Ruddy Mongoose, Stripe-necked Mongoose and unidentified species of Otters. Malabar Civet, Fishing Cat, Brown Mongoose, Nilgiri Marten, and Ratel were not sighted during this study. The Western Ghats alone account for thirteen species of small carnivores of which six are endemic. The sighting of Rustyspotted Cat is the first report from Karnataka. Habitat loss and hunting are the major threats for the small carnivore survival in nature. The Small Indian Civet is exploited for commercial purpose. Hunting technique varies from guns to specially devised traps, and hunting of all the small carnivore species is common in the State. Key words: Felidae, Viverridae, Herpestidae, Mustelidae, Karnataka, threats INTRODUCTION (Mukherjee 1989; Mudappa 2001; Rajamani et al. 2003; Mukherjee et al. 2004). Other than these studies, most of the Mammals of the families Felidae, Viverridae, information on these animals comes from anecdotes or sight Herpestidae, Mustelidae and Procyonidae are generally records, which no doubt, have significantly contributed in called small carnivores. -
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.