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Journal articles on the topic 'Managing wildlife'

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Published: 4 June 2021
Last updated: 3 February 2022

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1

Davis, David E., and Stanley H. Anderson. "Managing Our Wildlife Resources." Journal of Wildlife Management 50, no. 4 (October 1986): 762. http://dx.doi.org/10.2307/3800997.

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2

Nelson, Lisa. "Managing Human-Wildlife Interaction." International Journal of Public Administration 31, no. 3 (February 2008): 287–97. http://dx.doi.org/10.1080/01900690701590488.

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3

Child, Graham. "Managing wildlife successfully in Zimbabwe." Oryx 29, no. 3 (July 1995): 171–77. http://dx.doi.org/10.1017/s0030605300021098.

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Zimbabwe's approach to wildlife conservation started to change radically just over 30 years ago. Recognition of the fact that wildlife will only survive outside protected areas if the people who share the habitat are given responsibility for and derive benefits from wildlife has had positive effects for the conservation of the macrofauna. The author, the country's former Director of National Parks and Wild Life Management, describes the history of wildlife management in Zimbabwe and how the new approach is working.
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4

Healy, William M., and Gordon W. Gullion. "Managing Northern Forests for Wildlife." Journal of Wildlife Management 50, no. 1 (January 1986): 173. http://dx.doi.org/10.2307/3801510.

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5

Pirotta, Enrico, and David Lusseau. "Managing the wildlife tourism commons." Ecological Applications 25, no. 3 (April 2015): 729–41. http://dx.doi.org/10.1890/14-0986.1.

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6

McCALLUM, HAMISH. "Models for managing wildlife disease." Parasitology 143, no. 7 (June 2016): 805–20. http://dx.doi.org/10.1017/s0031182015000980.

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SUMMARYModelling wildlife disease poses some unique challenges. Wildlife disease systems are data poor in comparison with human or livestock disease systems, and the impact of disease on population size is often the key question of interest. This review concentrates specifically on the application of dynamic models to evaluate and guide management strategies. Models have proved useful particularly in two areas. They have been widely used to evaluate vaccination strategies, both for protecting endangered species and for preventing spillover from wildlife to humans or livestock. They have also been extensively used to evaluate culling strategies, again both for diseases in species of conservation interest and to prevent spillover. In addition, models are important to evaluate the potential of parasites and pathogens as biological control agents. The review concludes by identifying some key research gaps, which are further development of models of macroparasites, deciding on appropriate levels of complexity, modelling genetic management and connecting models to data.
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7

Gill, R. Bruce. "Managing wildlife ethics issues ethically." Human Dimensions of Wildlife 5, no. 4 (December 2000): 72–82. http://dx.doi.org/10.1080/10871200009359196.

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8

Burdge, Ryan, and Daniel Cristol. "Managing Golf Courses as wildlife habitat." Wildlife Professional 2, no. 1 (2008): 32. http://dx.doi.org/10.4004/1933-2866(2008)2[32:fffw]2.0.co;2.

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9

Davis, Charles. "Managing Wildlife within U.S. National Forests." Human Dimensions of Wildlife 12, no. 4 (August 10, 2007): 205–17. http://dx.doi.org/10.1080/10871200701442759.

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10

Thirgood, Simon. "New perspectives on managing wildlife diseases." Journal of Applied Ecology 46, no. 2 (April 2009): 454–56. http://dx.doi.org/10.1111/j.1365-2664.2009.01629.x.

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11

Bobek, B., K. Perzanowski, D. Merta, and S. Kossak. "The systems of managing wildlife and forest in central Europe." Forestry Chronicle 70, no. 5 (October 1, 1994): 550–54. http://dx.doi.org/10.5558/tfc70550-5.

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Central European countries share many similarities in the composition of forest habitats and wildlife species. However, the former political division of Europe produced substantial differences in wildlife management systems and land ownership. Forests are generally regarded as a source of lumber with the requirements of wildlife neglected most of the time. There is an urgent need to introduce measures enhancing forest habitats for wildlife. Most important seems to be maintaining and possibly increasing biodiversity by altering present logging systems. In future, production of timber should become only one of several functions of forests including conservation of wildlife, recreation, and other values.
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12

Hadidian, John. "Wildlife in U.S. Cities: Managing Unwanted Animals." Animals 5, no. 4 (November 11, 2015): 1092–113. http://dx.doi.org/10.3390/ani5040401.

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13

Treves, Adrian, Robert B. Wallace, Lisa Naughton-Treves, and Andrea Morales. "Co-Managing Human–Wildlife Conflicts: A Review." Human Dimensions of Wildlife 11, no. 6 (December 2006): 383–96. http://dx.doi.org/10.1080/10871200600984265.

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14

Horan, Richard D., and Christopher A. Wolf. "The Economics of Managing Infectious Wildlife Disease." American Journal of Agricultural Economics 87, no. 3 (August 2005): 537–51. http://dx.doi.org/10.1111/j.1467-8276.2005.00746.x.

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15

Smith, G. C., D. Parrott, and P. A. Robertson. "Managing wildlife populations with uncertainty: cormorantsPhalacrocorax carbo." Journal of Applied Ecology 45, no. 6 (December 2008): 1675–82. http://dx.doi.org/10.1111/j.1365-2664.2008.01380.x.

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16

Higginbottom, Karen, Ronda Green, and Chelsea Northrope. "A Framework for Managing the Negative Impacts of Wildlife Tourism on Wildlife." Human Dimensions of Wildlife 8, no. 1 (January 2003): 1–24. http://dx.doi.org/10.1080/10871200390180118.

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17

Harper, Craig A. "Strategies for Managing Early Succession Habitat for Wildlife." Weed Technology 21, no. 4 (December 2007): 932–37. http://dx.doi.org/10.1614/wt-07-024.1.

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Early succession plant communities consisting of a diverse mixture of grasses, forbs, and scattered shrubs are required by a variety of wildlife species. Early seral stages follow some form of disturbance but can become dominated by shrubs and trees rather quickly, especially in areas with abundant rainfall and relatively long growing seasons, such as the southeastern United States. In the absence of natural disturbance regimes, the quality and maintenance of these plant communities for wildlife is largely dependent upon management. Prescribed fire, disking, herbicide applications, and mowing are practices commonly used to maintain early succession plant communities for various wildlife species throughout this region. Prescribed fire consumes vegetative debris, provides open structure at ground level, and facilitates travel and foraging for wildlife throughout the field. Burning during the dormant season may promote cool-season grasses if they are present in the field. Burning in late March or early April generally promotes warm-season grasses and forbs. Late growing-season fire (September) will reduce woody encroachment and may encourage additional forb cover. Disking promotes vegetation decomposition, provides open structure at ground level, and generally promotes annual plant species. Disking in the fall and winter stimulates more forb growth than disking in the spring, which will stimulate undesirable nonnative warm-season grasses if present in the seedbank. Selective herbicides can influence plant composition and can be used to encourage grasses where forbs dominate, to promote forbs where grasses dominate, and to reduce woody cover. Mowing during midsummer encourages additional grasses in fields dominated by forbs but is not recommended for field maintenance because mowing produces thatch, which limits the ability of several wildlife species to travel and forage through the field, suppresses the seedbank, and destroys nests and young wildlife. Several practices can be used in combination to meet specific objectives. Succession should be set back every 2 to 4 yr, depending on plant response and focal wildlife species. It is important to intersperse disturbance in space and time, so that a variety of cover types are always available, even to those animals with small home ranges.
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18

Short, Michael. "Managing human risk during an oiled wildlife response." International Oil Spill Conference Proceedings 2017, no. 1 (May 1, 2017): 2164–83. http://dx.doi.org/10.7901/2169-3358-2017.1.2164.

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ABSTRACT 2017-066 Human risks during an oiled wildlife response (OWR) can be divided principally amongst physical, chemical and biological hazards. This paper identifies the risks associated with these hazards to oiled wildlife responders, other responders and the general public. Hazards and risks are managed by specific risk management procedures. These commonly include identifying individual steps in the activity, identifying associated hazards and risks, quantifying the risks and then applying treatments and controls to eliminate or reduce risk exposure to an acceptable level. For treatments and controls to manage risks effectively these are applied as a part of pre-incident contingency planning, during incidents and post incidents. Treatments and controls identified in the paper include responder training, registration of personnel, incident planning, use of safety data sheet recommendations, personal protection equipment, minimising exposure times, applying call in procedures and communication systems, making available emergency supportive equipment, providing food and fluids, vaccinations for responders, applying dangerous wildlife risk reduction practices, safe manual handling and transportation practices, safe motor driving and vessel handling practices, fatigue management practices, working in pairs as a minimum requirement, safety precautions when working near water and at industrial sites, equipment maintenance and safe use, safe practices around sharps, compliant waste disposal practices, reporting mechanisms for near misses and injuries and the systems to prevent their re-occurrence. Mental health hazards during incidents and post incident phases are also a key feature to manage and are often overlooked. Risks associated with mental health include stress and trauma. Supportive treatments and controls include response planning, professional counselling and medical support. The information to develop this paper was taken from a range of international responses.
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19

Higham, James E. S., and Lars Bejder. "Managing Wildlife-based Tourism: Edging Slowly Towards Sustainability?" Current Issues in Tourism 11, no. 1 (January 2008): 75–83. http://dx.doi.org/10.2167/cit345.0.

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20

Dau, Jim. "Managing reindeer and wildlife on Alaska's Seward Peninsula." Polar Research 19, no. 1 (January 2, 2000): 57–62. http://dx.doi.org/10.3402/polar.v19i1.6530.

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21

DeVos, James C., Duane L. Shroufe, and Vashti C. Supplee. "Managing wildlife by ballot initiative: The arizona experience." Human Dimensions of Wildlife 3, no. 2 (June 1998): 60–66. http://dx.doi.org/10.1080/10871209809359126.

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22

Dau, Jim. "Managing reindeer and wildlife on Alaska's Seward Peninsula." Polar Research 19, no. 1 (February 2000): 57–62. http://dx.doi.org/10.1111/j.1751-8369.2000.tb00328.x.

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23

Wallace, Pip. "Managing human disturbance of wildlife in coastal areas." New Zealand Geographer 72, no. 2 (May 16, 2016): 133–43. http://dx.doi.org/10.1111/nzg.12124.

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24

Bunnefeld, N., and A. Keane. "Managing wildlife for ecological, socioeconomic, and evolutionary sustainability." Proceedings of the National Academy of Sciences 111, no. 36 (August 29, 2014): 12964–65. http://dx.doi.org/10.1073/pnas.1413571111.

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25

Warburton, B., and P. Livingstone. "Managing and eradicating wildlife tuberculosis in New Zealand." New Zealand Veterinary Journal 63, sup1 (March 12, 2015): 77–88. http://dx.doi.org/10.1080/00480169.2014.981315.

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26

Fortmann, Louise. "Voices from communities managing wildlife in Southern Africa." Society & Natural Resources 10, no. 4 (July 1997): 403. http://dx.doi.org/10.1080/08941929709381037.

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27

Orams, Mark. "Creating Effective Interpretation for Managing Interaction Between Tourists and Wildlife." Australian Journal of Environmental Education 10 (1994): 21–34. http://dx.doi.org/10.1017/s0814062600003062.

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AbstractEcotourism associated with wildlife is becoming increasingly popular. The effects on wildlife of this increasing popularity are causing concern. Environmental interpretation programs may be a means of minimising negative effects if they are able to change tourists' behaviour. A review of cognitive psychology literature and theories of learning shows that simply increasing information and understanding does not necessarily result in more appropriate human behaviour. However, there are several techniques, such as the creation and resolution of cognitive dissonance and the use of the affective domain, which may create more effective interpretation. This paper reviews relevant theories of learning and offers guidelines for the creation of effective interpretation programs in the context of tourist - wildlife interaction.
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28

Dunlap, Thomas R., and Dian Olson Belanger. "Managing American Wildlife: A History of the International Association of Fish and Wildlife Agencies." Journal of American History 76, no. 2 (September 1989): 639. http://dx.doi.org/10.2307/1908080.

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29

Allin, Craig W., and Dian Olson Belanger. "Managing American Wildlife: A History of the International Association of Fish and Wildlife Agencies." American Historical Review 95, no. 2 (April 1990): 579. http://dx.doi.org/10.2307/2163930.

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30

Monz, Christopher, and Abigail M. Kidd. "Understanding and managing wildlife jams in national parks: An evaluation in Grand Teton National Park." UW National Parks Service Research Station Annual Reports 39 (December 15, 2016): 73–80. http://dx.doi.org/10.13001/uwnpsrc.2016.5291.

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As recreation and tourism in parks and protected areas continues to increase, managers face rising concerns of degradation of natural resources and the visitor experience. Many park visitors are seeking opportunities to view or photograph wildlife. Visitor behavior in prime wildlife-viewing areas often involves visitors parking along roadways and exiting their cars to view wildlife. This creates a phenomenon known as a “wildlife jam”, as visitors park informally along a roadway, often becoming pedestrians as they view wildlife, while other motorists attempt to drive through. To date, no studies have comprehensively investigated this phenomenon. Our study characterizes the nature of wildlife jams on the Moose-Wilson Road in Grand Teton National Park. Global Positioning System (GPS) technology was used to collect high-accuracy data on location and duration of the jams. Observations during jams characterize size (how many visitors and cars were involved) and visitor behaviors during jams. Preliminary results suggest that jam characteristics including presence of park staff, species involved, and location, can affect the duration, extent, and visitor behaviors that occur. Understanding the nature of these jams will enable park managers to minimize the potential negative effects of jams on wildlife and the visitor experience. Featured photo by letdown102 on Flickr. https://flic.kr/p/57jUok
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31

Locke, Christina M., Christine M. Anhalt‐Depies, Susan Frett, Jennifer L. Stenglein, Sarah Cameron, Vivek Malleshappa, Taylor Peltier, Benjamin Zuckerberg, and Philip A. Townsend. "Managing a large citizen science project to monitor wildlife." Wildlife Society Bulletin 43, no. 1 (February 21, 2019): 4–10. http://dx.doi.org/10.1002/wsb.943.

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32

Suchet, Sandie. "'Totally Wild'? Colonising discourses, indigenous knowledges and managing wildlife." Australian Geographer 33, no. 2 (July 2002): 141–57. http://dx.doi.org/10.1080/00049180220150972.

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33

Hammitt, William E., Cary D. McDonald, and Francis P. Noe. "Wildlife management: Managing the hunt versus the hunting experience." Environmental Management 13, no. 4 (July 1989): 503–7. http://dx.doi.org/10.1007/bf01867684.

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34

Barlow, Rebecca, Stephen Grado, Darren Miller, and Donald Grebner. "Opportunity Costs of Managing for Wildlife Habitat in the North Central Hills Region of Mississippi." Southern Journal of Applied Forestry 31, no. 1 (February 1, 2007): 39–46. http://dx.doi.org/10.1093/sjaf/31.1.39.

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Abstract Nonmarketed forest outputs need to be quantitatively measured and valued to project monetary gains and losses associated with varying these outputs relative to timber production. Of particular importance to many landowners is the quantity and value of timber production forgone relative to the creation or maintenance of wildlife habitat. We used scenario planning and a geographic information system to estimate potential monetary gains or losses for the North Central Hills region in Mississippi by manipulating timber growing stock to produce more or less habitat for northern bobwhite (Colinus virginianus), white-tailed deer (Odocoileus virginianus), and eastern wild turkey (Meleagris gallopavo silvestris). As expected, timber management–only scenarios, which maximized net present value (NPV), produced higher equivalent annual income values per hectare and allocated fewer habitat hectares for all wildlife species versus managing for wildlife habitat quality. Inclusion of fee hunting reduced cost differences between NPV only and improved wildlife habitat management scenarios. Simulations comparing management regimes maximizing NPV and optimizing wildlife habitat resulted in quantitative measures, which will be useful for land managers evaluating tradeoffs inherent in multiple-use management.
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35

Lokken, Nils A. A., Douglas A. Clark, Else G. Broderstad, and Vera H. Hausner. "Inuit Attitudes towards Co-Managing Wildlife in Three Communities in the Kivalliq Region of Nunavut, Canada." ARCTIC 72, no. 1 (March 31, 2019): 58–70. http://dx.doi.org/10.14430/arctic67868.

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We explored Inuit attitudes towards co-managing wildlife in the Kivalliq Region of Nunavut, Canada, working in partnership with the hunters and trappers’ organizations of Igluligaarjuk (Chesterfield Inlet), Tikirarjuaq (Whale Cove), and Qamani’tuaq (Baker Lake). In mixed-methods interviews, study participants in the two coastal communities described dissatisfaction with polar bear (Ursus maritimus) management outcomes, in contrast to a general satisfaction with (or indifference to) the management of other species. Interviewees expressed concern about grizzly bear (Ursus arctos) and, more prominently, caribou (Rangifer tarandus groenlandicus) populations in Qamani’tuaq, the inland community. Researchers have predicted that conflicts specific to polar bear management could lead to regulations being ignored or even defied and endanger the entire system of wildlife co-management. Our results indicate that dissatisfaction over decisions is specific to polar bear management outcomes and does not necessarily apply to the broader system of wildlife co-management. The results suggest that the Nunavut wildlife co-management system is quite functional: polar bear issues aside, Inuit in Qamani’tuaq, Tikirarjuaq, and Igluligaarjuk are largely content with the current functioning of the wildlife co-management regime.
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36

Rutberg, Allen T. "MANAGING WILDLIFE WITH CONTRACEPTION: WHY IS IT TAKING SO LONG?" Journal of Zoo and Wildlife Medicine 44, no. 4s (December 2013): S38—S46. http://dx.doi.org/10.1638/1042-7260-44.4s.s38.

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37

KATO, Eri. "A Possibility of Multiple Communities Managing Crop-raiding by wildlife." JOURNAL OF RURAL PLANNING ASSOCIATION 36, no. 4 (March 30, 2018): 548–53. http://dx.doi.org/10.2750/arp.36.548.

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38

Mousavi, Zahra, and Saeed Behzadi. "Introducing an Appropriate Geoportal Structure for Managing Wildlife Location Data." International Journal of Natural Sciences Research 7, no. 1 (2019): 32–48. http://dx.doi.org/10.18488/journal.63.2019.71.32.48.

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39

Che, Deborah, and Ted Cable. "Managing prairie dogs for prairie heritage, biodiversity, and wildlife tourism." Journal of Heritage Tourism 5, no. 4 (November 2010): 285–96. http://dx.doi.org/10.1080/1743873x.2010.517842.

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40

Davis, Phillip Brock, Ian A. Munn, James E. Henderson, and Bronson K. Strickland. "Economic tradeoffs of managing for timber production or wildlife habitat." Journal of Wildlife Management 81, no. 8 (September 1, 2017): 1363–71. http://dx.doi.org/10.1002/jwmg.21330.

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41

Curtin, Susanna. "Managing the wildlife tourism experience: The importance of tour leaders." International Journal of Tourism Research 12, no. 3 (August 5, 2009): 219–36. http://dx.doi.org/10.1002/jtr.747.

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42

Artois, M. "Managing problem wildlife in the ‘Old World’: a veterinary perspective." Reproduction, Fertility and Development 9, no. 1 (1997): 17. http://dx.doi.org/10.1071/r96090.

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This paper focuses on mammalian pest species mainly in Europe and Africa and on implications for animal health, human safety, wildlife management and animal welfare. Three examples of problem species are presented: the wild boar (Sus scrofa), the stray dog (Canis familiaris) and the red fox (Vulpes vulpes). Several species are reservoirs or vectors of transmissible diseases of man and of economically valuable domestic species. The control of these and other infections and the limitation of the nuisance or damage caused by these pest species involves lethal or non-lethal methods which are briefly reviewed. Some control measures require veterinary expertise, and veterinary involvement in managing problem species is likely to increase. With regard to fertility control, methods are considered which will allow an appropriate choice of the best technique for the management of problem animals in various habitats. For desirable native species, traditional methods of control, especially hunting in the case of game species, is preferable to contraception. For exotic or feral species, control of fertility seems to be a worthwhile option.
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43

Prato, Tony. "Adaptively Managing Wildlife for Climate Change: A Fuzzy Logic Approach." Environmental Management 48, no. 1 (March 4, 2011): 142–49. http://dx.doi.org/10.1007/s00267-011-9648-x.

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44

Cagnacci, Francesca, and Ferdinando Urbano. "Managing wildlife: A spatial information system for GPS collars data." Environmental Modelling & Software 23, no. 7 (July 2008): 957–59. http://dx.doi.org/10.1016/j.envsoft.2008.01.003.

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45

Horan, Richard D., David Finnoff, Kevin Berry, Carson Reeling, and Jason F. Shogren. "Managing Wildlife Faced with Pathogen Risks Involving Multi-Stable Outcomes." Environmental and Resource Economics 70, no. 3 (February 13, 2018): 713–30. http://dx.doi.org/10.1007/s10640-018-0227-y.

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46

Prato, Tony. "Evaluating and managing wildlife impacts of climate change under uncertainty." Ecological Modelling 220, no. 7 (April 2009): 923–30. http://dx.doi.org/10.1016/j.ecolmodel.2009.01.010.

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47

Mawdsley, Jonathan R., John F. Organ, Daniel J. Decker, Ann B. Forstchen, Ronald J. Regan, Shawn J. Riley, Mark S. Boyce, John E. McDonald, Chris Dwyer, and Shane P. Mahoney. "Artelleet al. (2018) miss the science underlying North American wildlife management." Science Advances 4, no. 10 (October 2018): eaat8281. http://dx.doi.org/10.1126/sciadv.aat8281.

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Artelleet al. (2018) conclude that “hallmarks of science” are largely missing from North American wildlife management based on a desk review of selected hunting management plans and related documents found through Internet searches and email requests to state and provincial wildlife agencies. We highlight three fundamental problems that compromise the validity of the conclusions posited: missing information to support selection of “hallmarks of science,” confusion about the roles and nature of science and management, and failure to engage effectively with the scientists and managers actively managing wildlife populations in North America.
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48

van Vuren, Dirk. "Managing American Wildlife. A History of the International Association of Fish and Wildlife Agencies. Dian Olson Belanger." Quarterly Review of Biology 64, no. 2 (June 1989): 220. http://dx.doi.org/10.1086/416303.

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49

Pukazhenthi, Budhan S., and David E. Wildt. "Which reproductive technologies are most relevant to studying, managing and conserving wildlife?" Reproduction, Fertility and Development 16, no. 2 (2004): 33. http://dx.doi.org/10.1071/rd03076.

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The advent of in vitro fertilisation (IVF) and embryo transfer in the 1970s led to speculation about the potential value of these and other ‘reproductive technologies’ to conserving endangered species. So far, and for the most part, assisted breeding techniques that are routine in domesticated species are not easily adapted to wildlife. Species differences in reproductive form (anatomy/morphology) and function (mechanisms regulating reproductive success) limit the practical applicability for offspring production. Thus, the limiting factor is the lack of basic knowledge about thousands of unstudied species, the foundation that is essential to allowing reproduction to be enhanced and/or controlled. There now is excellent evidence that reproductive technologies are most useful as tools for studying how different species reproduce, especially defining novel and unique mechanisms. The present paper reviews the status and relevance of various reproductive technologies that are useful or have potential for wildlife. Modern examples of progress are provided indicating how these tools are being used to understand ways that wildlife species reproduce and, in some cases, how such knowledge has been used for successful assisted breeding, improved management and conservation.
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50

Miller, Kelly K., and Darryl N. Jones. "Wildlife management in Australasia: perceptions of objectives and priorities." Wildlife Research 32, no. 4 (2005): 265. http://dx.doi.org/10.1071/wr04042.

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The aim of this study was to examine the values and attitudes held by Australasian wildlife managers as they relate to wildlife management issues, and to gain some insight into possible future directions and priorities for Australasian wildlife management. During December 2002 – February 2003, 138 questionnaires were completed by members of the Australasian Wildlife Management Society (AWMS) and registrants of the 2002 AWMS annual conference. Threatened species management, threatened communities/habitats, and management of introduced species were the issues rated as needing the highest priority for the Australasian Wildlife Management Society. Issues such as animal rights, genetically modified organisms and timber harvesting on public lands were the lowest-rating issues. Respondents expressed a strong belief in managing and controlling wildlife to achieve wildlife management objectives, a strong belief that wildlife should be protected and that wildlife managers should minimise the pain and suffering of individual animals, and a belief that resources should be directed towards conserving wildlife populations rather than protecting individual animals from non-threatened populations. While respondents held a strong belief that it is important to consult the community when developing wildlife management policies and programs, there was little support for a comanagerial approach where the community has a significant role to play in decision-making processes.
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