Winter habitat associations of eastern spotted skunks in Virginia

2017 ◽  
Vol 81 (6) ◽  
pp. 1042-1050 ◽  
Author(s):  
Emily D. Thorne ◽  
Charles Waggy ◽  
David S. Jachowski ◽  
Marcella J. Kelly ◽  
W. Mark Ford
Keyword(s):  
Habitat Associations ◽  
Winter Habitat

Winter habitat associations of seed-eating passerines on Scottish farmland

Bird Study ◽  
2003 ◽  
Vol 50 (2) ◽  
pp. 116-130 ◽  
Author(s):  
Mark H. Hancock ◽  
Jeremy D. Wilson
Keyword(s):  
Habitat Associations ◽  
Winter Habitat ◽  
Seed Eating

Winter habitat associations of Purple Sandpiper (Calidris maritima) and Harlequin Duck (Histrionicus histrionicus) in Atlantic Canada

2019 ◽  
Vol 222 ◽  
pp. 214-225
Author(s):  
Sarah E. Gutowsky ◽  
Robert A. Ronconi ◽  
Lee F.G. Gutowsky ◽  
Mark F. Elderkin ◽  
Julie Paquet ◽  
...  
Keyword(s):  
Habitat Associations ◽  
Atlantic Canada ◽  
Winter Habitat ◽  
Histrionicus Histrionicus

Winter Habitat Associations of a Low-Density Moose (Alces americanus) Population in Central Labrador

2009 ◽  
Vol 16 (3) ◽  
pp. 471-480 ◽  
Author(s):  
Thomas S. Jung ◽  
Tony E. Chubbs ◽  
Colin G. Jones ◽  
Frank R. Phillips ◽  
Robert D. Otto
Keyword(s):  
Habitat Associations ◽  
Low Density ◽  
Winter Habitat ◽  
Alces Americanus

Using Ships of Opportunity to Assess Winter Habitat Associations of Seabirds in Subarctic Coastal Alaska

2015 ◽  
Vol 89 (2) ◽  
pp. 111-128 ◽  
Author(s):  
Neil M. Dawson ◽  
Mary A. Bishop ◽  
Kathy J. Kuletz ◽  
Alain F. Zuur
Keyword(s):  
Habitat Associations ◽  
Winter Habitat

Winter habitat selection by female moose in western interior montane forests

2006 ◽  
Vol 84 (12) ◽  
pp. 1823-1832 ◽  
Author(s):  
Kim G. Poole ◽  
Kari Stuart-Smith
Keyword(s):  
Habitat Selection ◽  
Snow Depth ◽  
Causative Factor ◽  
Habitat Associations ◽  
Late Winter ◽  
Managed Forests ◽  
Winter Habitat ◽  
Gps Collars ◽  
Winter Range ◽  
Crown Closure

Winter range has been identified as an important component of moose ( Alces alces (L., 1758)) conservation in managed forests, yet there have been few studies on habitat associations in montane ecosystems. We investigated habitat selection by moose at landscape and stand scales during late winter in southeastern British Columbia using global positioning system (GPS) collars on 24 adult moose cows in each of two winters. The strongest determinant of late-winter range at the landscape scale was decreasing elevation, while moose also selected for areas of gentler slopes and higher solar insolation. Elevation likely is a surrogate for snow depth, which is probably the primary causative factor influencing late-winter distribution of moose. Within late-winter range, topographic variables had little influence on moose habitat selection. Lower crown closure was the strongest determinant of stand-scale selection, although the resultant model was weak. We found no disproportionate selection for stands with high crown closure, and there was little evidence for greater use of cover stands with increasing snow as winter progressed. Within late-winter range, moose selected forage habitats (42% use vs. 30% availability) over cover habitats (22% use vs. 37% availability). The delineation of late-winter moose range can be based on snow depth, or elevation as its surrogate.

Winter habitat associations of four grassland sparrows in Florida dry prairie

2013 ◽  
Vol 125 (3) ◽  
pp. 502-512 ◽  
Author(s):  
Marianne G. Korosy ◽  
Joshua S. Reece ◽  
Reed F. Noss
Keyword(s):  
Habitat Associations ◽  
Winter Habitat

Habitat Association of Klebsiella Species

1985 ◽  
Vol 6 (2) ◽  
pp. 52-58 ◽  
Author(s):  
Susan T. Bagley
Keyword(s):  
Drinking Water ◽  
Gastrointestinal Tract ◽  
Surface Waters ◽  
Industrial Effluents ◽  
Opportunistic Pathogen ◽  
Habitat Associations ◽  
Habitat Association ◽  
Klebsiella Species ◽  
Almost All ◽  
Polluted Waters

AbstractThe genus Klebsiella is seemingly ubiquitous in terms of its habitat associations. Klebsiella is a common opportunistic pathogen for humans and other animals, as well as being resident or transient flora (particularly in the gastrointestinal tract). Other habitats include sewage, drinking water, soils, surface waters, industrial effluents, and vegetation. Until recently, almost all these Klebsiella have been identified as one species, ie, K. pneumoniae. However, phenotypic and genotypic studies have shown that “K. pneumoniae” actually consists of at least four species, all with distinct characteristics and habitats. General habitat associations of Klebsiella species are as follows: K. pneumoniae—humans, animals, sewage, and polluted waters and soils; K. oxytoca—frequent association with most habitats; K. terrigena— unpolluted surface waters and soils, drinking water, and vegetation; K. planticola—sewage, polluted surface waters, soils, and vegetation; and K. ozaenae/K. rhinoscleromatis—infrequently detected (primarily with humans).

scholarly journals Identifying priority core habitats and corridors for effective conservation of brown bears in Iran

2021 ◽  
Vol 11 (1) ◽  
Author(s):  
A. Mohammadi ◽  
K. Almasieh ◽  
D. Nayeri ◽  
F. Ataei ◽  
A. Khani ◽  
...  
Keyword(s):  
Protected Areas ◽  
Brown Bear ◽  
Population Connectivity ◽  
Habitat Associations ◽  
Area Network ◽  
Zagros Mountains ◽  
Range Limit ◽  
Brown Bears ◽  
Core Areas ◽  
Effective Conservation

AbstractIran lies at the southernmost range limit of brown bears globally. Therefore, understanding the habitat associations and patterns of population connectivity for brown bears in Iran is relevant for the species’ conservation. We applied species distribution modeling to predict habitat suitability and connectivity modeling to identify population core areas and corridors. Our results showed that forest density, topographical roughness, NDVI and human footprint were the most influential variables in predicting brown bear distribution. The most crucial core areas and corridor networks for brown bear are concentrated in the Alborz and Zagros Mountains. These two core areas were predicted to be fragmented into a total of fifteen isolated patches if dispersal of brown bear across the landscape is limited to 50,000 cost units, and aggregates into two isolated habitat patches if the species is capable of dispersing 400,000 cost units. We found low overlap between corridors, and core habitats with protected areas, suggesting that the existing protected area network may not be adequate for the conservation of brown bear in Iran. Our results suggest that effective conservation of brown bears in Iran requires protection of both core habitats and the corridors between them, especially outside Iran’s network of protected areas.

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