Northwestern Naturalist Research Articles

Preface to a Special Issue: Recent Advances in Bat Research in Northwestern Canada and Alaska

Until recently, bats were among the least studied terrestrial vertebrates in northwestern Canada and Alaska (Parker and others 1997; Jung and others 2006). Concern over the anticipated westward spread of white-nose syndrome (WNS), as well as other drivers (for example, landscape change, climate change), has resulted in a growing scientific and management interest in bats in this vast region (Blejwas and others 2014; Olson and others 2014; Wilson and others 2014), with recent studies producing interesting new findings (for example, Slough and Jung 2008; Boland and others 2009; Randall and others 2011). In particular, our knowledge of the diversity and distribution of species in northwestern Canada and Alaska has advanced significantly in recent years (see papers in this issue), and these data represent the necessary first step in baseline and environmental impact studies as well as conservation planning. Bats living at high latitudes face unique environmental conditions (such as short, bright summers), and several studies have begun to illuminate how the life history and ecology of bats in the far north are unique and where they may (or may not) differ with conspecifics at more southerly latitudes (for example, Talerico 2008; Reimer and others 2014). Unfortunately, much of the recent work has remained unpublished and unavailable to others with an interest in bats in the region. As such, our primary goal with this special issue is to bring to light recent advances in bat research in northwestern Canada and Alaska. The impetus for this special issue arose from a symposium and workshop on ‘‘Bat Ecology in Alaska: Assessing the Risk of WNS’’, organized by Karen Blejwas (Alaska Department of Fish and Game) and Link Olson (University of Alaska Museum), and held in conjunction with the Alaska Chapter of The Wildlife Society’s 2012 annual conference in Anchorage, Alaska. The symposium marked the first gathering of bat researchers from Alaska and northwestern Canada (Fig. 1) and spawned the Northern Bat Working Group (NBWG), a network of likeminded scientists and enthusiasts recognizing, and striving to address, the need for better communication and coordination among bat researchers and managers. Karen Blejwas and Miranda Terwilliger (US National Park Service) were elected the group’s first Co-Chairs. Another outcome was the notion of a special journal issue to capture some of the recent advances in our knowledge of bats in the region. The 13 papers that comprise this special issue are a combination of select presentations delivered at the 2012 symposium and others solicited from researchers we knew were producing interesting findings on bats in the region. (Our apologies to those we may have missed.) For the purpose of this special issue, our region of interest included Alaska, Yukon, Northwest Territories, and the northern portions ($546N latitude) of Alberta and British Columbia. This area spans several ecoregions, including the northern Pacific Coast and the expansive boreal forest of the interior. Much of the work presented in this issue advances our knowledge of the diversity and distribution of bats in the region. This is indicative of the expansiveness and remoteness of the region and the concomitant logistical challenges faced by bat biologists. Other works included in this special issue provide an NORTHWESTERN NATURALIST 95:173–175 WINTER 2014

Unusual Coloration of a Hairy Woodpecker from Oregon

Northwestern Naturalist does not hold copyright on any articles or notes published in the journal. The attached file is the published version of the article. If you wish to consult the rest of the issue visit the publisher's website.

Bison (Bison bison) Fur Used As Drey Material by Red Squirrels (Tamiasciurus hudsonicus): An Indication of Ecological Restoration

Shine R, Harlow PS, Keogh JS, Boeadi. 1998. The influence of sex and body size on food habits of a giant tropical snake, Python reticulatus. Functional Ecology 12:248-258. St. John A. 2002. Reptiles of the Northwest. Auburn, WA: Lone Pine Publishing. 256 p. Weaver RE. 2008. Distribution, abundance, and habitat associations of the night snake (Hypsiglena torquata) in Washington State. Northwestern Naturalist 89:164-170.

First Confirmed Record of Breeding Brown Creepers in the Northwest Territories, Canada

The Brown Creeper (Certhia americana) is a small, bark-foraging songbird found throughout the forested regions from Central America north to south-central Canada and Alaska. Its avoidance of edges, cryptic plumage, and highpitched songs and calls contribute to a low detection rate for this species on most surveys (Hejl and others 2002; Alberta Sustainable Resource Development 2003). The abundance and distribution of the species at the northern edge of its range is poorly understood and is likely currently underestimated (Hejl and others 2002; Alberta Sustainable Resource Development 2003). Although creepers are known to occur along the Pacific coast to south-central Alaska, no confirmed breeding records have been reported above 606N latitude east of the continental divide (Hejl and others 2002). In this note, we document the 1st known occurrences of breeding Brown Creepers in the Northwest Territories, Canada. We observed breeding activity at 2 Brown Creeper territories within 100 m of point-count stations initiated for long-term forest songbird monitoring by the Canadian Wildlife Service (CWS) in the Liard Valley of the Northwest Territories. The study area for regional songbird monitoring spans over 700 km, and includes over 195 point-count stations and several line transects and census routes (Machtans and Latour 2003). The Liard Valley is in the far southwest corner of the Northwest Territories, just north of the British Columbia border and east of the Yukon border. Our observations were made in the low relief boreal forest region east of the Liard River. The Liard Valley typically has higher average temperatures and more precipitation than many regions of the northern boreal forest (Machtans and Latour 2003). Forests are typically old and, on average, taller than in other areas of the Northwest Territories. Vegetation and site characteristics for the Liard Valley are described in Machtans (2000) and Machtans and Latour (2003). From 15 June to 12 July 2008, several observations of Brown Creepers were made at 2 locations near Fort Liard, Northwest Territories (606139N, 1236229W) that confirmed breeding by this species in the area. On 15 June 2008, 2 Brown Creepers were heard and observed foraging during point-count surveys in the area (UTM Zone 10: 480493E 6697423N, NAD1983; hereafter location A). Upon further investigation, at least 3 juvenile creepers were flushed from the trunk of a tree, which provoked distraction displays from one or both parents. This display consisted of several aggressive flights to within 2 m of the observer’s head. On 21 June 2008, an audio recording of a singing Brown Creeper was obtained using a high quality hand held digital recorder (Edirol R-09, Roland Corporation) near the same location. On 6 July 2008, at least 4 Brown Creepers were foraging approximately 300 m from the original location. Several pictures were taken of the birds observed on 6 July (Fig. 1). On 12 July 2008, these birds were again observed and an inactive nest was found near the original sighting at location A (Fig. 2). The nest was 5.5 m above the ground in a 35-m-tall Trembling Aspen (Populus tremuloides) snag with a diameter at breast height (dbh) of 39 cm. On 15 June 2008, a Brown Creeper was heard and observed for about 10 min during a pointcount survey at a location approximately 4.6 km away from location A (UTM Zone 10: 480601E 6692793N, NAD1983; hereafter location B). On NORTHWESTERN NATURALIST 90:156–159 AUTUMN 2009 156 NORTHWESTERN NATURALIST 90(2)

Observations of Humpback Whales, Megaptera novaeangliae, in the Beaufort Sea, Alaska

Humpback Whales, Megaptera novaeangliae, are found in all of the world’s oceans (Reeves and others 2002). Humpback Whales, however, have generally not been found in the Arctic Ocean with the exception of the Barents Sea where warmer waters from the North Atlantic Drift provide rich nutrients for food resources, and ice free zones in the summer (Zabavnikov and others 2005). In the North Pacific, Asian stocks of Humpback Whales summer in the eastern Bering Sea, with some individuals occasionally entering the Arctic Ocean via the Bering Strait and summering along the Siberian coast of the Chukchi Sea (Tomilin 1937; Sleptsov 1961; Johnson and Wolman 1984; Angliss and Allen 2008). Further penetration into the Arctic Ocean, especially into the Beaufort Sea, has probably been prevented by the whales’ natural avoidance of colder waters and associated polar pack ice (Chittleborough 1965; Dawbin 1966). We report on the 1st confirmed sighting of Humpback Whales for the Beaufort Sea, Alaska. During August 2007, FEX LP contracted Agvik Marine LLC to barge oil drilling equipment from Cape Simpson to West Dock (Prudhoe Bay), Alaska, as part of a demobilization of onshore drilling activities conducted the previous 2 winters. On 1 August 2007, at UTM 454911E, 7879755N (WGS84) (about 87 km east of Point Barrow), KAH observed a whale at about 250 m from the barge, and initially identified the individual as a Humpback Whale based on the unique characteristics of the dorsal fin and flukes, and characteristic arching back. Five minutes later the same whale (presumably) approached to within about 75 m of the barge where it was photographed (Fig. 1) and confirmed by BA, an experienced Inupiat hunter, to be a Humpback Whale. During this close encounter, the whale turned on its side revealing the characteristic long pectoral flipper. At this time KAH and the barge’s captain observed a calf with the adult whale. The adult was last seen about 3 min later about 175 m from the barge, slowly traveling to the east. No photographs were taken of the calf or the undersides of the adult’s flukes. At the time of the encounter, the sea state was a Beaufort 3 (large wavelets with occasional whitecaps), the wind was from the east at 10 knots (about 19 km/hr), and visibility was excellent. The barge, hampered by the loss of an outboard engine, was reduced to traveling at ,6 km/hr. Other than approaching the barge, the whales showed no undue reaction to the vessel. Although adult whales were sighted at 3 locations during an 8-min period, we could not positively ascertain whether more than 1 adult whale was present. We believe that we observed only a single cow/calf pair, although it was possible some of the sightings were of an additional Humpback Whale. Further, 2 Gray Whales (Eschrichtius robustus) were observed minutes before the 1st Humpback Whale sighting. While an extralimital sighting of a Humpback Whale in the Beaufort Sea is unusual in itself, the presence of a calf is particularly noteworthy. Based on limited understanding of whales in the North Pacific, it is possible that the whales we observed were part of the Western North Pacific stock that breeds in Asian waters, especially near the Mariana, Ryukyu, and Bonin islands, and summers in the Bering Sea; although the Central North Pacific stock, which breeds among the Hawaiian Islands (Angliss and Allen 2008), may also summer in portions of the Bering Sea. Regardless of origin (Asia or NORTHWESTERN NATURALIST 90:160–162 AUTUMN 2009 160 NORTHWESTERN NATURALIST 90(2)

Kleptoparasitism of a Coyote (Canis latrans) by a Golden Eagle (Aquila chrysaetos) in Northwestern Canada

calves in the diet of nesting Golden Eagles in Finnmark, northern Norway. Ornis Fennica 84: 112-118. Kroll AM. 1993. Haul out patterns and behavior of harbor seals, Phoca vitulina, during the breeding season at Protection Island, Washington [thesis]. Seattle, WA: University of Washington, 142 p. norberg H, kojola I, AlKIO P, nylund M. 2006. Predation by Golden Eagle Aquila chrysaetos on semi-domesticated reindeer Rangifer tarandus calves in northeastern Finnish Lapland. Wildlife Biology 12:393-402. Parrish JK, Marvier M, Paine RT. 2001. Direct and indirect effects: Interactions between bald eagles and common murres. Ecological Applications 11: 1858-1869. Sherrod SK, Estes JA, White CM. 1975. Depreda tion of sea otter pups by bald eagles at Amchitka Island, Alaska. Journal of Mammalogy 56:701 703. Sherrod SK, White CM, Williamson FSL. 1976. Bi ology of the bald eagle on Amchitka Island, Alas ka. The Living Bird 15:143-182. skorupa JP. 1989. Crowned Eagles Strephanoaetus co ronatus in rainforest: Observations on breeding chronology and diet at a nest in Uganda. Ibis 131: 294-298. stalmaster M. 1987. The bald eagle. New York, NY: Universe Books. 227 p. thompson SP. 1989. Observations of bald eagles eat ing glaucous-winged gull eggs in western Wash ington. Northwestern Naturalist 70:13-14. Tjernberg M. 1981. Diet of the Golden Eagle Aquila chrysaetos during the breeding season in Sweden. Ecography 4:12-19. Watson JW, Stinson D, McAllister KR, Owens TE. 2002. Population status of bald eagles breeding in Washington at the end of the 20th century. Jour nal of Raptor Research 36:161-169.

BIODIVERSITY CONSERVATION—A PLACE HOLDER: INTRODUCTION TO PAPERS IN THIS ISSUE

Biodiversity conservation in the US Pacific Northwest is gaining new attention as large reserves are recognized as not being a panacea for protection of all rare species. In February 2005, a workshop at Oregon State University, held in conjunction with the joint annual meetings of the Society for Northwestern Vertebrate Biology and the Oregon Chapter of the Wildlife Society, focused on key topics of concern relative to the advancement of biodiversity conservation in the region. Articles in this issue of Northwestern Naturalist provide overviews of these topics. As an introduction, I describe the origin of conservation biology at another conference 25 y ago and 2 key developments occurring in intervening years—the definition of “biodiversity” and the need to advance and integrate several socioeconomic aspects of the discipline. Both of these developments support the concept of conservation biology as a “place holder”.

PREDATION ON RED TREE VOLES BY OWLS AND DIURNAL RAPTORS

*HAYES MP 1997. Status of the Oregon spotted frog (Rana pretiosa sensu stricto) in the Deschutes Basin and selected other systems in Oregon and northeastern California with a rangewide synopsis of the species' status. Unpublished report prepared for the Nature Conservancy, Portland, OR. 57 p. + Appendices. Available from U. S. Fish and Wildlife Service, 26000 SE 98th Avenue, Portland, OR 97266. LICHT LE. 1986. Food and feeding behavior of sympatric red-legged frogs, Rana aurora, and spotted frogs, Rana pretiosa, in southwestern British Columbia. Canadian Field Naturalist 100:22-31. MCALLISTER KR, LEONARD WP, STORM RM. 1993. Spotted frog (Rana pretiosa) surveys in the Puget Trough of Washington, 1989-1991. Northwestern Naturalist 74:10-15.

Common Garter Snake Predation on Ring-Billed Gull Chicks in Washington

SHERROD SK, WHITE CM, WILLIAMSON FSL. 1976. Biology of the bald eagle on Amchitka Island, Alaska. Living Bird 15:143-182. STALMASTER MV. 1987. The bald eagle. New York, NY: Universe Books. 227 p. STALMASTER MV, PLETTNER RG. 1992. Diets and foraging effectiveness of bald eagles during extreme winter weather in Nebraska. Journal of Wildlife Management 56:355-367. THOMPSON SP. 1989. Observations of bald eagles eating glaucous-winged gull eggs in western Washington. Northwestern Naturalist 70:13-14. TODD CS, YOUNG LS, OWEN RB, JR, GRAMLICH FJ. 1982. Food habits of bald eagles in Maine. Journal of Wildlife Management 46:636-645. VERMEER K. 1963. The breeding biology of the glaucous-winged gull on Mandarte Island, B.C. Occasional Papers of the British Columbia Provincial Museum, No. 13. 104 p. WATSON JW, GARRETT MG, ANTHONY RG. 1991. Foraging ecology of bald eagles in the Columbia River Estuary. Journal of Wildlife Management 55: 492-499.

Scale and conservation planning in the real world

Conservation planning is carried out on a variety of geopolitical and biogeographical scales. Whereas considerable consensus is emerging about the most appropriate procedures for identifying conservation areas, the spatial implications of conducting conservation planning at divergent scales have received little attention. Here we explore the consequences of planning at different geopolitical scales, using a database of the mammalian fauna from the Northern Provinces of South Africa. The conservation network resulting from treating the region as one unit is compared with networks generated separately for the provinces nested in that region. These outcomes are evaluated in terms of (i) their land use efficiencies, (ii) their spatial overlap, and (iii) the impact of algorithm attributes. Although land use efficiencies are greater on broader scales, on average the spatial congruence between the broad-scale regional network and fine-scale provincial networks was less than 14%. Algorithms using different selection rules fail to improve this disturbing outcome. Consequently, scale has an overwhelming influence on areas identified as conservation networks in geopolitical units. This should be recognized in conservation planning.

An Active Bald Eagle Nest Associated with Unusually Close Human Activity

Department of Psychology and Regional Primate Research Center, University of Washington, Box 351525, Seattle, Washington 98195 USA. Submitted 14 September 1998, accepted 15 April 1999. Corresponding Editor: K. A. Engel. prised 2.5% of items at 17 nests on Vancouver Island (Vermeer and Morgan 1989. Northwestern Naturalist 70:21-26), and 3 crows were found in 102 nests in Puget Sound (Knight and others 1990. Canadian Field Naturalist 104: 545-551). Although scavenging cannotbe ruled out as the source of nest remains, the observations reported here suggest that at least some were due to predation. The present observations document the real predation threat of bald eagles on crows. This threat justifies the study of predator vigilance and response in crows when bald eagles are present. Predation of crows by bald eagles requires heightened vigilance in crows, thereby

Herpetofauna of Glacier National Park

The current distribution of amphibians and reptiles in Glacier National Park, Montana was documented from museum records and field surveys conducted in 1990 to 1992. Eight species were recorded at 141 sites at elevations from 1000 m to 2300 m. Rana luteiventris was the most common amphibian, occurring parkwide to elevations of 1800 m. Ambystoma macrodacEylum occurred in woodlands and wet meadows west of the Continental Divide at elevations between 1050 and 1500 m. This salamander was uncommon on the east side of the park with most sightings recorded in the lower Waterton Valley; none were found in the upper Missouri River drainage. Buto boreas was widely distributed to elevations up to 2250 m, but was not abundant at most locations. Ascaphus truei was found in small, cold, high gradient streams throughout the Middle Fork drainage, but occurred intermittently in the North Fork and upper Missouri ltiver drainages. A single population of A. truei was located in the South Saskatchewan River drainage. The range of Hyla regilla was restricted. Most sightings were made near the community of West Glacier, Montana, or at breeding ponds along the Middle Fork, Flathead River, a few km upstream. Chrysemys picta occurred mostly in the lower Lake McDonald valley at elevations between 1000 and 1120 m. A few turtles were seen in the North Fork drainage south of Polebridge, Montana. Thamnophis elegans was more abundant than the similarly distributed T. sirtalis. The widespread introduction of sport fish in park waters may have reduced amphibian populations in some drainages, notably in some of the high elevation valleys east of the Continental Divide. This content downloaded from 207.46.13.52 on Sat, 22 Oct 2016 04:48:40 UTC All use subject to http://about.jstor.org/terms 18 NORTHWESTERN NATURALIST 78(1) an, and terrestrial habitats. Intensive area searches were employed instead of more rigorous sampling methods (i.e., time-constrained searches, trapping, etc.) to ensure maximum coverage within the budget constraints and time available for the survey. Searches were conducted along major stream courses and their principal tributaries from the valley terminus to tree line. Some sites were revisited during successive years, however, most were searched only once. Sighting data were sorted by drainage within the 4 watersheds in the park (Appendix). Site locations were resolved to the nearest 50 m by UTM coordinates determined from standard 7.5', 1:24,000 USGS quad maps. UTM and elevation data were processed via a Unix-based Sun SPARC IPX Geographic Information System (GIS) running GRASS, Version 4.1. Survey data were used to generate range maps for each species. Adjustments were made during GIS processing of location data to minimize errors in the generation of species range maps arising from habitat variability across similar elevations, and to accommodate special circumstances such as disjunct or geographically restricted species distributions. To deal with variable weather influences, exposures, and radically different microhabitats at the same elevation within a watershed, range maps generated by the GIS excluded the highest 5% of recorded elevations for most species. This adjustment was not made for painted turtles, Chrysemys picta, or Pacific treefrogs, Hyla regilla, because both species occupy restricted geographic and altitudinal ranges in the park. The range map for tailed frogs, Ascaphus truei, includes only streams with documented sightings, because this species occupies a highly disjunct range in Glacier National Park. Frogs and toads were collected with a telescoping capture net fitted with a 25 cm diameter bag of 5 mm mesh size. A small handheld dip net was used for capturing tadpoles and salamander larvae. Captured specimens were identified in the field (Stebbins 1985) and in some cases measured and released. Garter snakes were hand-captured for positive identification and released. Field data included location, weather, water temperatures, habitat types, proximity of fish, and developmental stage of specimens. Field work was limited to daylight hours from late May through September 1990 to 1992. Night searches were not made due to the presence of dangerous predators in the study area; occasional night observations were made opportunistically in the vicinity of back country cabins and field camps. Field investigations were supplemented by examination of specimens and collection records from the Glacier Park Museum. Thirteen other museums issued collection permits for herpetofaunal studies in Glacier National Park also provided data. Because the present survey was undertaken to assess current conditions, museum data were not incorporated into the GIS range maps. However, past sighting and collection records are discussed in the accompanying species accounts.

Water Exchanges of the California Vole, Microtus californicus

Previous articleNext article No AccessWater Exchanges of the California Vole, Microtus californicusRonald L. ChurchRonald L. Church Search for more articles by this author PDFPDF PLUS Add to favoritesDownload CitationTrack CitationsPermissionsReprints Share onFacebookTwitterLinkedInRedditEmail SectionsMoreDetailsFiguresReferencesCited by Volume 39, Number 4Oct., 1966 Article DOIhttps://doi.org/10.1086/physzool.39.4.30152356 Views: 2Total views on this site Citations: 15Citations are reported from Crossref Journal History This article was published in Physiological Zoology (1928-1998), which is continued by Physiological and Biochemical Zoology (1999-present). Copyright 1966 University of ChicagoPDF download Crossref reports the following articles citing this article:Jenny L. McGuire, Daniel A. Lauer Linking patterns of intraspecific morphology to changing climates, Journal of Biogeography 47, no.1111 (Sep 2020): 2417–2425.https://doi.org/10.1111/jbi.13954Alan Harper, Anny Peralta-García, Jorge H. Valdez-Villavicencio, Scott Tremor, Chris J. Conroy Current Distribution of the California Vole (Microtus californicus) in Baja California, Mexico, Western North American Naturalist 80, no.22 (Jul 2020): 194.https://doi.org/10.3398/064.080.0207Jasmine M. Crumsey, Jeremy B. Searle, Jed P. Sparks Isotope values of California vole (Microtus californicus) hair relate to historical drought and land use patterns in California, USA, Oecologia 190, no.44 (Jul 2019): 769–781.https://doi.org/10.1007/s00442-019-04457-2Eric D. Forsman, Amy L. Price Water Consumption by Red Tree Voles (Arborimus longicaudus), Northwestern Naturalist 92, no.22 (Sep 2011): 116–119.https://doi.org/10.1898/10-28.1J.L. McGuire Geometric morphometrics of vole (Microtus californicus) dentition as a new paleoclimate proxy: Shape change along geographic and climatic clines, Quaternary International 212, no.22 (Feb 2010): 198–205.https://doi.org/10.1016/j.quaint.2009.09.004Nichole L. Cudworth, John L. Koprowski Microtus californicus (Rodentia: Cricetidae), Mammalian Species 42 (Jan 2010): 230–243.https://doi.org/10.1644/868.1Dick T Stalling, Howard Haines Effect of dehydration on water-turnover rates and hematocrits in the rice rat, oryzomys palustris, Comparative Biochemistry and Physiology Part A: Physiology 72, no.22 (Jan 1982): 301–306.https://doi.org/10.1016/0300-9629(82)90223-7Carol S Daily, Howard B Haines Evaporative water loss and water turnover in chronically and acutely water-restricted spiny mice (acomys cahirinus), Comparative Biochemistry and Physiology Part A: Physiology 68, no.33 (Jan 1981): 349–354.https://doi.org/10.1016/0300-9629(81)90061-XAyesha E. GILL Partial reproductive isolation of subspecies of the California vole, Microtus californicus, Genetica 52-53, no.11 (Dec 1980): 105–117.https://doi.org/10.1007/BF00121821William Z. Lidicker Experimental manipulation of the timing of reproduction in the California vole, Population Ecology 18, no.11 (Nov 2018): 14–27.https://doi.org/10.1007/BF02754079A.J Hulbert, T.J Dawson Water metabolism in perameloid marsupials from different environments, Comparative Biochemistry and Physiology Part A: Physiology 47, no.22 (Feb 1974): 617–633.https://doi.org/10.1016/0300-9629(74)90026-7Howard Haines, Charles F. Shield Reduced evaporation in house mice (Musmusculus) acclimated to water restriction, Comparative Biochemistry and Physiology Part A: Physiology 39, no.11 (May 1971): 53–61.https://doi.org/10.1016/0300-9629(71)90347-1Kenneth D. Abbott Water economy of the canyon mouse Peromyscus crinitus stephensi, Comparative Biochemistry and Physiology Part A: Physiology 38, no.11 (Jan 1971): 37–52.https://doi.org/10.1016/0300-9629(71)90096-XBruce A Wunder Temperature regulation and the effects of water restriction on Merriams's chipmunk, Eutamias merriami, Comparative Biochemistry and Physiology 33, no.22 (Mar 1970): 385–403.https://doi.org/10.1016/0010-406X(70)90357-9Harry N. Coulombe The role of succulent halophytes in the water balance of salt marsh rodents, Oecologia 4, no.33 (Jan 1970): 223–247.https://doi.org/10.1007/BF00377248

BIBLIOGRAPHY OF YORKSHIRE GEOLOGY 1941 TO 1943 WITH ADDITIONS TO THAT OF 1939 TO 1940

Additions to the bibliography of Yorkshire geology 1938 to 1940. published in 1944 in the Proceedings of the Yorkshire Geological Society, volume xxv, pages 215 to 220. Bevan, D. J. The natural history of Goathland Dale. I, The geology and topography. North-western Naturalist, xiv, p. 184. 1939. Harris, T. M. On some Jurassic specimens of Saginopteris [from Middle Estuarine of Cayton Bay]. Ann. Mag. Nat. Hist., vi (11), p. 249. 1940. Kent, P. E. Notes on river systems and glacial retreat stages in south Lincolnshire. Proc. Geol. Assoc., 1, p. 164. 1939. Kent, P. E. Note on the age of the uppermost Kimeridge Clay of north Lincolnshire. Trans. Lincs. Nat. Union, x, p. 29. 1939. Kent, P. E. A short outline of the stratigraphy of the Lincolnshire Limestone. Trans. Lincs. Nat. Union, x, p. 48. 1940. Pugh, W. J. The ice age in Britain [refers to glacial lakes of Cleveland]. North-western Naturalist, xiv, pp. 170 and 249. 1939. Stubblefield, C. J. Some aspects of the distribution and migration of trilobites in the British Lower Palaeozoic faunas. Geol. Mag., 1939, p. 49. 1941 to 1943. Anon. Richard Hall Tiddeman [editorial biographical note]. North-western Naturalist, xvii, p. I. 1942. Anon. James Clifton Ward (1843–1900) [editorial biographical note]. North-western Naturalist, xvii, p. 306. 1942. Anderson, W. Water-supply from underground sources of north-east England (Quarter-inch geological sheet 1, 2 and 4). Part III. Well-catalogues for new series one-inch sheets 21 (Sunderland) and 27 (Durham). Geol. Surv. Wartime Pamphlets, no. 19. 1941, 18 pp.

Change in Color Pattern in a Captive Red Squirrel

Previous articleNext article No AccessShorter Articles and DiscussionChange in Color Pattern in a Captive Red SquirrelArthur SvihlaArthur Svihla Search for more articles by this author PDFPDF PLUS Add to favoritesDownload CitationTrack CitationsPermissionsReprints Share onFacebookTwitterLinkedInRedditEmail SectionsMoreDetailsFiguresReferencesCited by The American Naturalist Volume 65, Number 696Jan. - Feb., 1931 Published for The American Society of Naturalists Article DOIhttps://doi.org/10.1086/280351 Views: 4Total views on this site Citations: 1Citations are reported from Crossref PDF download Crossref reports the following articles citing this article:Thomas S. Jung, Brian G. Slough Isabelline Coloration in American Red Squirrels (Tamiasciurus hudsonicus) from the Yukon, Northwestern Naturalist 93, no.22 (Sep 2012): 162–164.https://doi.org/10.1898/nwn12-07.1

List of the Birds of the Willamette Valley, Oregon

Previous articleNext article FreeList of the Birds of the Willamette Valley, OregonO. B. JohnsonO. B. Johnson Search for more articles by this author PDFPDF PLUS Add to favoritesDownload CitationTrack CitationsPermissionsReprints Share onFacebookTwitterLinkedInRedditEmail SectionsMoreDetailsFiguresReferencesCited by The American Naturalist Volume 14, Number 7Jul., 1880 Published for The American Society of Naturalists Article DOIhttps://doi.org/10.1086/272595 Views: 197 Citations: 3Citations are reported from Crossref PDF download Crossref reports the following articles citing this article:Scott F. Pearson, Shannon M. Knapp, Mathew S. Crowther Considering Spatial Scale and Reproductive Consequences of Habitat Selection when Managing Grasslands for a Threatened Species, PLOS ONE 11, no.66 (Jun 2016): e0156330.https://doi.org/10.1371/journal.pone.0156330D. Max Smith A Summary of Birds Detected During the Breeding Season at Killin Wetlands, Northwestern Oregon, Northwestern Naturalist 93, no.33 (Dec 2012): 220–227.https://doi.org/10.1898/12-09.1Oriane W. Taft, Susan M. Haig Historical wetlands in Oregon’s Willamette valley: Implications for restoration of winter waterbird habitat, Wetlands 23, no.11 (Mar 2003): 51–64.https://doi.org/10.1672/0277-5212(2003)023[0051:HWIOWV]2.0.CO;2