Human-Black Bear Conflict a Review of the Most Common Management Practices
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Black Bear Tracking Dog License Application (PDF)
For Office Use Only LICENSE DURATION 1 Year or 5Years Black Bear License # ________________ Fee Paid $ _______________ LICENSE FEE Tracking Dog License ☐ ☐ $25.00 1 Year Check # _____________ Application ☐ 00 $100. 5 Year ☐ M.O. # ______________ For more information on this license visit www.dec.ny.gov/permits/25006.html *APPLICANT INFORMATION name / date of birth ____________________________________________ _____________________________________ _________ ___________________ Last First M.I. DOB (mm/dd/yyyy) address _______________________________________ _______________ ________________________________________________________ Street Address Apartment/Unit City ______________________________________________________________________________ ________________ ______________________ County State Zip Code email / ____________________________________________________________________________________ ( _________ ) _________ - ______________ telephone Email Telephone *Provide your NYS Hunting License ID # (must be current year license) *FACILITY / BUSINESS INFORMATION (Complete this section if different from above.) facility / business name ____________________________________________________________________________________________________________________________ address _________________________________________ _______________ _____________________________________________________ Street Address Apartment/Unit City _______________________________________ ___________ ___________________ ( _________ ) __________ - ________________ County State Zip -
Deer, Elk, Bear, Moose, Lynx, Bobcat, Waterfowl
Hunt ID: 1501-CA-AL-G-L-MDeerWDeerElkBBearMooseLynxBobcatWaterfowl-M1SR-O1G-N2EGE Great Economy Deer and Moose Hunts south of Edmonton, Alberta, Canada American Hunters trekking to Canada for low cost moose, along with big Mule Deer and Whitetail and been pleasantly surprised by the weather and temperatures that they were greeted by when they hunted British Columbia, located in Canada, north of Washington State. Canada should be and is cold but there are exceptions, if you know where to go. In BC if you stay on the western Side of the Rocky Mountains the weather is quite mild because it is warmed by the Pacific Ocean. If you hunt east of the Rocky Mountains, what I call the Canadian Interior it can be as much as 50 degrees colder depending on the time of the year. The area has now preference point requirements, the Outfitter has his allotted vouchers so you can get a reasonably priced license and, in most cases, less than you can get for the same animal in the US as a non-resident. You don’t even buy the voucher from the Outfitter it is part of his hunt cost because without it you could not get a license anyway. Travel is easy and the residents are friendly. Like anywhere outside the US you will need a easy to acquire Passport if you don’t have one, just don’t wait until the last minute to get one for $10 from your local Post office by where you live. The one thing in Canada is if you have a felony on your record Canada will not allow you into their safe Country. -
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 -
Public Attitudes Toward and Awareness of Trapping Issues In
ATTITUDES TOWARD AND AWARENESS OF TRAPPING ISSUES IN CONNECTICUT, INDIANA AND WISCONSIN Conducted for the International Association of Fish and Wildlife Agencies And the Furbearer Resources Technical Work Group Conducted by Responsive Management May 2001 ATTITUDES TOWARD AND AWARENESS OF TRAPPING ISSUES IN CONNECTICUT, INDIANA AND WISCONSIN May 2001 CONDUCTED BY RESPONSIVE MANAGEMENT NATIONAL OFFICE Mark Damian Duda, Executive Director Peter E. De Michele, Ph.D., Director of Research Steven J. Bissell, Ph.D., Qualitative Research Director Ping Wang, Ph.D., Quantitative Research Associate Jim Herrick, Ph. D., Research Associate Alison Lanier, Business Manager William Testerman, Survey Center Manager Joy Yoder, Research Associate 130 Franklin Street, PO Box 389 Harrisonburg, VA 22801 Phone: 540/432-1888 Fax: 540/432-1892 E-mail to: [email protected] www.responsivemanagement.com EXECUTIVE OVERVIEW Executive Overview of Findings, Implications and Conclusions The purpose of this project was to assist the International Association of Fish and Wildlife Agencies (IAFWA) and the Furbearer Resources Technical Work Group in better understanding public awareness of, opinions on, and attitudes toward trapping. There were five phases to this project. Phase I was a series of focus groups with members of the general population in Connecticut, Wisconsin, and Indiana (Chapter 1). Phase II consisted of focus groups with two important stakeholder groups: Wildlife professionals (Chapter III), and Veterinarians (Chapter 1). Phase III consisted of utilizing the focus group results to develop a comprehensive group of questions regarding the most salient issues related to public opinion on, and attitudes toward trapping. These survey questions formed the basis of the development of three separate survey instruments that can be used by wildlife agencies to periodically assess attitudes toward trapping on a local, state or national level (Chapter IV). -
Long-Term Trends in Food Habits of the Raccoon Dog, Nyctereutes Viverrinus, in the Imperial Palace, Tokyo
Bull. Natl. Mus. Nat. Sci., Ser. A, 42(3), pp. 143–161, August 22, 2016 Long-term Trends in Food Habits of the Raccoon Dog, Nyctereutes viverrinus, in the Imperial Palace, Tokyo Akihito1, Takako Sako2, Makito Teduka3 and Shin-ichiro Kawada4* 1The Imperial Residence, 1–1 Chiyoda, Chiyoda-ku, Tokyo 100–0001, Japan 2Imperial Household Agency, 1–1 Chiyoda, Chiyoda-ku, Tokyo 100–8111, Japan 3Field Work Office, 4–29–2 Asahi-cho, Akishima, Tokyo 196–0025, Japan 4 Department of Zoology, National Museum of Nature and Science, 4–1–1 Amakubo, Tsukuba, Ibaraki 305–0005, Japan *E-mail: [email protected] (Received 31 March 2016; accepted 22 June 2016) Abstract The food habits of the raccoon dogs in the Imperial Palace were examined by fecal analysis focused on the long term trend for five years. A total of 95 taxa (including 58 taxa identi- fied as genera or species) of plant seeds were detected from 163 collected feces in 164 weekly sur- veys. Among them, eight taxa were selected as the food resources for the raccoon dogs in the Imperial Palace. The intakes of these taxa showed seasonal succession, i.e. Aphananthe aspera in January, Idesia polycarpa in February, Rubus hirsutus from May to July, Cerasus spp. in May and June, Morus spp. in June, Machilus thunbergii in July and August, Aphananthe aspera from Sep- tember to December until the following January, and also Ficus erecta in September and Celtis sinensis in December. In March and April, plant harvest is rather poor, and therefore raccoon dogs feed on the inside endosperm of Ginkgo biloba and family Fagaceae to supply the insufficient nutrients as observed by broken seed coats from feces. -
Brown Bear (Ursus Arctos) John Schoen and Scott Gende Images by John Schoen
Brown Bear (Ursus arctos) John Schoen and Scott Gende images by John Schoen Two hundred years ago, brown (also known as grizzly) bears were abundant and widely distributed across western North America from the Mississippi River to the Pacific and from northern Mexico to the Arctic (Trevino and Jonkel 1986). Following settlement of the west, brown bear populations south of Canada declined significantly and now occupy only a fraction of their original range, where the brown bear has been listed as threatened since 1975 (Servheen 1989, 1990). Today, Alaska remains the last stronghold in North America for this adaptable, large omnivore (Miller and Schoen 1999) (Fig 1). Brown bears are indigenous to Southeastern Alaska (Southeast), and on the northern islands they occur in some of the highest-density FIG 1. Brown bears occur throughout much of southern populations on earth (Schoen and Beier 1990, Miller et coastal Alaska where they are closely associated with salmon spawning streams. Although brown bears and grizzly bears al. 1997). are the same species, northern and interior populations are The brown bear in Southeast is highly valued by commonly called grizzlies while southern coastal populations big game hunters, bear viewers, and general wildlife are referred to as brown bears. Because of the availability of abundant, high-quality food (e.g. salmon), brown bears enthusiasts. Hiking up a fish stream on the northern are generally much larger, occur at high densities, and have islands of Admiralty, Baranof, or Chichagof during late smaller home ranges than grizzly bears. summer reveals a network of deeply rutted bear trails winding through tunnels of devil’s club (Oplopanx (Klein 1965, MacDonald and Cook 1999) (Fig 2). -
Effect of Pheromone Trap Density on Mass Trapping Of
SCIENTIFIC NOTE 281 EFFECT OF PHEROMONE TRAP DENSITY ON MASS TRAPPING OF MALE POTATO TUBER MOTH Phthorimaea operculella (ZELLER) (LEPIDOPTERA: GELECHIIDAE), AND LEVEL OF DAMAGE ON POTATO TUBERS Patricia Larraín S.1*, Michel Guillon2, Julio Kalazich3, Fernando Graña1, and Claudia Vásquez1 ABSTRACT Potato tuber moth (PTM), Phthorimaea operculella (Zeller), is one of the pests that cause the most damage to potatoes (Solanum tuberosum L.) in both field crops and storage, especially in regions where summers are hot and dry. Larvae develop in the foliage and tubers of potatoes and cause direct losses of edible product. The use of synthetic pheromones that interfere with insect mating for pest control has been widely demonstrated in numerous Lepidoptera and other insect species. An experiment was carried out during the 2004-2005 season in Valle del Elqui, Coquimbo Region, Chile, to evaluate the effectiveness of different pheromone trap densities to capture P. operculella males for future development of a mass trapping technique, and a subsequent decrease in insect reproduction. The study evaluated densities of 10, 20, and 40 traps ha-1, baited with 0.2 mg of PTM sexual pheromone, and water- detergent for captures. Results indicated that larger numbers of male PTM were captured per trap with densities of 20 and 40 traps per hectare, resulting in a significant reduction (P < 0.05) of tuber damage in these treatments compared with the control which used conventional chemical insecticide sprays. Key words: potato tuber moth, Phthorimaea operculella, mass trapping, pheromone. INTRODUCTION researched (El-Sayed et al., 2006). It interferes with insect mating, reducing the future larvae population and The potato tuber moth is a pest which economically subsequent damage. -
Wildlife Crossings of Florida 1-75
54 TRANSPORTATION RESEARCH RECORD 1279 Wildlife Crossings of Florida 1-75 GARY L. LlVINK The Florida Department of Transportation is constructing 1-75 The Interstate highway would run 40 mi across the center of across the SR-84 (Alligator Alley) alignment in south Florida. the remaining habitat for the only known population of Flor This alignment crosses approximately 40 mi of habitat of the only ida panther. The panthers would need to cross the highway known population of the endangered Florida panther. Panther in order to provide food during periods of deteriorating hab movement and behavior are being monitored by radio tracking. Radio-collared panthers have been crossing the alignment, pro itat during wet seasons, to permit dispersals of young pan viding information on locations of crossings and habitat type being thers, and to maintain the genetic viability of the population. used. This information was used to develop measures to provide Therefore, measures to provide safe crossing of I-75 for the safe crossings of 1-75 for the panther. Measures taken include panthers were evaluated. creation of L3 wildlife crossings, which are lUU ft long and 8 ft Fortunately, the Florida Game and Fresh Water Fish Com high, and the extension of 13 existing bridges to provide 40 ft of mission (FGFWFC) in cooperation with the U.S. Fish and land along the drainage canals under the bridges. The spacing of the crossings is roughly 1 mi apart. Fencing to cause animals to Wildlife Service had ongoing studies of panther behavior and use the crossings will be 10 ft high with outriggers and three movement in the area. -
History and Status of the American Black Bear in Mississippi
History and status of the American black bear in Mississippi Stephanie L. Simek1,5, Jerrold L. Belant1, Brad W. Young2, Catherine Shropshire3, and Bruce D. Leopold4 1Carnivore Ecology Laboratory, Forest and Wildlife Research Center, Mississippi State University, Box 9690, Mississippi State, MS 39762, USA 2Mississippi Department of Wildlife, Fisheries, and Parks, 1505 Eastover Drive, Jackson, MS 39211, USA 3Mississippi Wildlife Federation, 517 Cobblestone Court, Suite 2, Madison, MS 39110, USA 4Department of Wildlife, Fisheries, and Aquaculture, Mississippi State University, Box 9690, Mississippi State, MS 39762, USA Abstract: Historically abundant throughout Mississippi, American black bears (Ursus americanus) have declined due to habitat loss and overharvest. By the early 1900s, the bear population was estimated at ,12 individuals, and Mississippi closed black bear hunting in 1932. However, habitat loss continued and by 1980 suitable habitat was estimated at 20% (20,234 km2) of historic levels (101,171 km2) with the decline continuing. Although black bear abundance is currently unknown, a recent increase in occurrence reports and documented reproduction suggests the population may be increasing. There have been 21 reported nuisance complaints since 2006, of which 7 were apiary damage. Additionally, 31 bear mortalities were reported since 1972; 80% were human caused. Government and private organizations have emphasized education on bear ecology and human–bear coexistence, while habitat restoration through land retirement programs (e.g., -
The Genetic Structure of American Black Bear Populations in the Southern Rocky Mountains
THE GENETIC STRUCTURE OF AMERICAN BLACK BEAR POPULATIONS IN THE SOUTHERN ROCKY MOUNTAINS Rachel C. Larson, Department of Forest and Wildlife Ecology, University of Wisconsin – Madison, 1630 Linden Dr., Madison, WI 53706 Rebecca Kirby, Department of Forest and Wildlife Ecology, University of Wisconsin – Madison, 1630 Linden Dr., Madison, WI 53706 Nick Kryshak, Department of Forest and Wildlife Ecology, University of Wisconsin – Madison, 1630 Linden Dr., Madison, WI 53706 Mathew Alldredge, Colorado Parks & Wildlife, Fort Collins, Colorado, 80525 David B. McDonald, Department of Zoology & Physiology, University of Wyoming, 1000 E. University Ave. Laramie, WY 80721 Jonathan N. Pauli, Department of Forest and Wildlife Ecology, University of Wisconsin – Madison, 1630 Linden Dr., Madison, WI 53706 ABSTRACT: Large and wide-ranging carnivores typically display genetic connectivity across their distributional range. American black bears (Ursus americanus) are vagile carnivores and habitat generalists. However, they are strongly associated with forested habitats; consequently, habitat patchiness and fragmentation have the potential to drive connectivity and the resultant structure between black bear subpopulations. Our analysis of genetic structure of black bears in the southern Rocky Mountains of Wyoming and Colorado (n = 296) revealed two discrete populations: bears in northern Wyoming were distinct (FST = 0.217) from bears in southern Wyoming and Colorado, despite higher densities of anthropogenic development within Colorado. The differentiation we observed indicates that bears in Wyoming originated from two different clades with structure driven by the pattern of contiguous forest, rather than the simple distance between populations. We posit that forested habitat and competitive interactions with brown bears reinforced patterns of genetic structure resulting from historic colonization. -
Glimpse of an African… Wolf? Cécile Bloch
$6.95 Glimpse of an African… Wolf ? PAGE 4 Saving the Red Wolf Through Partnerships PAGE 9 Are Gray Wolves Still Endangered? PAGE 14 Make Your Home Howl Members Save 10% Order today at shop.wolf.org or call 1-800-ELY-WOLF Your purchases help support the mission of the International Wolf Center. VOLUME 25, NO. 1 THE QUARTERLY PUBLICATION OF THE INTERNATIONAL WOLF CENTER SPRING 2015 4 Cécile Bloch 9 Jeremy Hooper 14 Don Gossett In the Long Shadow of The Red Wolf Species Survival Are Gray Wolves Still the Pyramids and Beyond: Plan: Saving the Red Wolf Endangered? Glimpse of an African…Wolf? Through Partnerships In December a federal judge ruled Geneticists have found that some In 1967 the number of red wolves that protections be reinstated for of Africa’s golden jackals are was rapidly declining, forcing those gray wolves in the Great Lakes members of the gray wolf lineage. remaining to breed with the more wolf population area, reversing Biologists are now asking: how abundant coyote or not to breed at all. the USFWS’s 2011 delisting many golden jackals across Africa The rate of hybridization between the decision that allowed states to are a subspecies known as the two species left little time to prevent manage wolves and implement African wolf? Are Africa’s golden red wolf genes from being completely harvest programs for recreational jackals, in fact, wolves? absorbed into the expanding coyote purposes. If biological security is population. The Red Wolf Recovery by Cheryl Lyn Dybas apparently not enough rationale for Program, working with many other conservation of the species, then the organizations, has created awareness challenge arises to properly express and laid a foundation for the future to the ecological value of the species. -
Ecology of the European Badger (Meles Meles) in the Western Carpathian Mountains: a Review
Wildl. Biol. Pract., 2016 Aug 12(3): 36-50 doi:10.2461/wbp.2016.eb.4 REVIEW Ecology of the European Badger (Meles meles) in the Western Carpathian Mountains: A Review R.W. Mysłajek1,*, S. Nowak2, A. Rożen3, K. Kurek2, M. Figura2 & B. Jędrzejewska4 1 Institute of Genetics and Biotechnology, Faculty of Biology, University of Warsaw, Pawińskiego 5a, 02-106 Warszawa, Poland. 2 Association for Nature “Wolf”, Twardorzeczka 229, 34-324 Lipowa, Poland. 3 Institute of Environmental Sciences, Jagiellonian University, Gronostajowa 7, 30-387 Kraków, Poland. 4 Mammal Research Institute, Polish Academy of Sciences, Waszkiewicza 1c, 17-230 Białowieża, Poland. * Corresponding author email: [email protected]. Keywords Abstract Altitudinal Gradient; This article summarizes the results of studies on the ecology of the European Diet Composition; badger (Meles meles) conducted in the Western Carpathians (S Poland) Meles meles; from 2002 to 2010. Badgers inhabiting the Carpathians use excavated setts Mustelidae; (53%), caves and rock crevices (43%), and burrows under human-made Sett Utilization; constructions (4%) as permanent shelters. Excavated setts are located up Spatial Organization. to 640 m a.s.l., but shelters in caves and crevices can be found as high as 1,050 m a.s.l. Badger setts are mostly located on slopes with southern, eastern or western exposure. Within their territories, ranging from 3.35 to 8.45 km2 (MCP100%), badgers may possess 1-12 setts. Family groups are small (mean = 2.3 badgers), population density is low (2.2 badgers/10 km2), as is reproduction (0.57 young/year/10 km2). Hunting by humans is the main mortality factor (0.37 badger/year/10 km2).