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studies [2023/03/21 09:27]
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studies [2023/06/17 08:23] (current)
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| ====== Studies ====== | ====== Studies ====== |
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| | [[https://besjournals.onlinelibrary.wiley.com/doi/full/10.1111/j.1365-2664.2005.01123.x|2005: Statistical methods for analysing responses of wildlife to human disturbance |
| | HAIGANOUSH K. PREISLER, ALAN A. AGER, MICHAEL J. WISDOM]] |
| | |
| | {{ ::theeconomicvalueofquiet_finalreport.pdf |March 2011: The Economic Value of Quiet, prepared by URS-Scott Wilson for the Department of Environment, Food and Rural Affairs (DEFRA)}} |
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| | [[https://academic.oup.com/heapro/article/28/1/133/577113| 2013: Is this the new smoking? An expert panel review of the York University OHV health benefits study]] |
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| | [[https://www.lsohc.mn.gov/materials/16_Mtg/DEC_14_2016_ORV_WHITE_PAPER_BackcountryHuntersAnglersofAmerica.pdf| 2016: Cumulative and Universal: ATV Impacts on the Landscape and Wildlife; Backcountry Hunters and Anglers.]] |
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| | [[https://ecoshare.info/wp-content/uploads/2018/06/Wisdom-et-al._2018_Trail-recreation-effects-on-elk_Forest-EcologyMgmt.pdf|2018: Elk responses to trail-based recreation on public forests Michael J. Wisdom, Haiganoush K. Preisler, Leslie M. Naylor, Robert G. Anthony, |
| | Bruce K. Johnson, Mary M. Rowland; Forest Ecology and Management.]] |
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| {{ :st:s41467-020-16899-x.pdf |2020: Roads as a contributor to landscape-scale variation | {{ :st:s41467-020-16899-x.pdf |2020: Roads as a contributor to landscape-scale variation |
| in bird communities}} | in bird communities: "Species |
| | with smaller national populations generally have lower relative abundance with increasing |
| | road exposure, whereas the opposite is true for more common species. Smaller-bodied and |
| | migratory species are also more negatively associated with road exposure. By creating |
| | environmental conditions that benefit generally common species at the expense of others, |
| | road networks may echo other anthropogenic disturbances in bringing about large-scale |
| | simplification of avian communities"}} |
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| | {{ :studies:winter_rec_science_2021_emailweb.pdf |2021: Environmental Impacts of Winter Recreation; Best Available Science, 2021}} |
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| {{ ::st:s41598-023-27670-9.pdf |2023: Partial COVID‑19 closure of a national park reveals negative | {{ ::st:s41598-023-27670-9.pdf |2023: Partial COVID‑19 closure of a national park reveals negative |
| influence of low‑impact recreation on wildlife spatiotemporal ecology; "We found consistent negative effects of human presence on species, regardless of status as large carnivores, meso-carnivores, or herbivores. Based on best-fitting models, 12 of 14 species used a fewer number of sites in the year that the park was open to recreation (Fig. 2). Declines in use of sites were relatively modest but were 10% or greater for 6 of those 12 species (black bear, coyote, elk, lynx, white- tailed deer (Odocoileus virginianus), and wolves"}} | influence of low‑impact recreation on wildlife spatiotemporal ecology; "We found consistent negative effects of human presence on species, regardless of status as large carnivores, meso-carnivores, or herbivores. Based on best-fitting models, 12 of 14 species used a fewer number of sites in the year that the park was open to recreation (Fig. 2). Declines in use of sites were relatively modest but were 10% or greater for 6 of those 12 species (black bear, coyote, elk, lynx, white- tailed deer (Odocoileus virginianus), and wolves"}} |
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