DOCSLIB.ORG

Reference List

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Reference List Proposed Major Amendment to the Coachella Valley MSHCP – March 2014 11.0 Literature Cited 1. Aborn DA, and D. Froehlich. 1995. “An Observation of a Summer Tanager Attempting to Eat an Anolis Lizard.” Journal of Field Ornithology 66(4):501–502. 2. Aborn DA, and F.R. Moore. 1997. “Pattern of Movement by Summer Tanagers (Piranga rubra) During Migratory Stopover: A Telemetry Study.” Behavior 134(13–14):1077–100. 3. Abrams L. 1940. Illustrated Flora of the Pacific States: Washington, Oregon, and California. Stanford, California: Stanford University Press. 4. Academy of Natural Sciences of Philadelphia. 1996. “Le Conte's Thrasher (Toxostoma lecontei).” Birds of North America 230:1–24. 5. Academy of Natural Sciences of Philadelphia. 1996. “Summer Tanager: Piranga rubra.” Birds of North America 248:1–23. 6. Adams LW. 1984. “Small Mammal Use of an Interstate Highway Median Strip.” Journal of Applied Ecology 24:175–8. 7. Addicott JF, J.M. Aho, M.F. Antolin, D.K. Padilla, J.S. Richardson, and D.A. Soluk. 1987. “Ecological Neighborhoods: Scaling Environmental Patterns.” OIKOS 49:340–6. 8. Aigner PA, J. Tecklin, and C.E. Koehler. 1995. “Probable Breeding Population of the Black Rail in Yuba County, California.” Western Birds 26(3):157–60. 9. Akcakaya HR. 2000. “Conservation and Management for Multiple Species: Integrating Field Research and Modeling Into Management Decisions.” Environmental Management 26(1):S75–S83. 10. Akcakaya HR. 2000. “Viability Analyses with Habitat-based Metapopulation Models.” Population Ecology 42:45–53. 11. Akcakaya HR. 2001. “Linking Population-level Risk Assessment with Landscape and Habitat Models.” Science of the Total Environment 274:283–91. 12. Akcakaya HR, M.A. Burgman, and L.R. Ginzburg. 1999 May. “Applied Population Ecology.” [Web Page]. Located at: http://www.ramas.com/underg34.htm. Accessed 2002 Aug 4. 13. Alleman AR, E.R. Jacobson, and R.E. Raskin. 1992. “Morphologic and Cytochemical Characteristics of Blood Cells from the Desert Tortoise (Gopherus agassizii).” Am. J. Vet. Res. 53(9):1645–51. 14. Allen E, et al. 1998. Proceedings of the International Symposium on Air Pollution and Climate Change Effects on Forest Ecosystems, Riverside, California, February 5-9, 1996. 15. Allen E, et al. 2000. “Air Pollution and Vegetation Change in (Southern California) Shrublands.” Proceedings of the Symposium on Planning for Biodiversity: Bringing Research and Management Together, February 29-March 3, 2000. 11-1 Proposed Major Amendment to the Coachella Valley MSHCP – March 2014 16. Allen JA, and W.W. Price. 1895. “On a Collection of Mammals from Arizona and Mexico.” Volume 7. New York: American Museum of Natural History Bulletin. p. 123-258. 17. Allen M, W. Hodges, T. Scott, S. Snyder, T. Tennant, and W. Wehtje. 2002. Report to CVAG on Supplemental Activities: July 10, 2002 (Task 1: Documentation of Preserve Design Selection Criteria; Task 2: Evaluation of the Sites Model for Preserve Design; Task 3: Natural Community Map Evaluation, Natural Community and Mapping Unit Accuracy). Unpublished report to Coachella Valley Association of Governments (CVAG) prepared by listed associates of the Center for Conservation Biology, University of California Riverside. 18. Allen MF. 2003. Interim Report to the California Department of Fish and Game. Unpublished report on monitoring approaches for the Western Riverside County Multiple Species Habitat Conservation Plan. January 2003. 24 pp. 19. Allen MF. 2003. Report to the Coachella Valley Association of Governments. Unpublished report on a monitoring approach for the Coachella Valley Multiple Species Habitat Conservation Plan. March 2003. 23 pp. 20. Allendorf FW, R.F. Leary, P. Spruell, and J.K. Wenburg. 2001. “The Problem with Hybrids: Setting Conservation Guidelines.” Trends in Ecology and Evolution 16(11):613–22. 21. Alvarez-Castaneda ST, E. Rios, and A. Gutierrez-Ramos. 2001. “Noteworthy Records of the Little Pocket Mouse (Heteromyidae: Perognathus longimembris) on the Baja California Peninsula.” Southwestern Naturalist 46(2):243–5. 22. Ambuel B, and S.A. Temple. 1983. “Area-dependent Changes in the Bird Communities and Vegetation of Southern Wisconsin Forests.” Ecology 64(5):1057–68. 23. Amos W, and A. Balmford. 2001. “When Does Conservation Genetics Matter?” Heredity 87:257–65. 24. Andelman S, I. Ball, F. Davis, and D. Stoms. 1999. SITES V 1.0: An Analytical Toolbox for Designing Ecoregional Conservation Portfolios. A manual prepared for The Nature Conservancy by the Institute for Computational Earth System Science and Department of Geography, University of California Santa Barbara. 25. Andelman SJ, and W.F. Fagan. 2000. “Umbrellas and Flagships: Efficient Conservation Surrogates or Expensive Mistakes?” Proceedings of the National Academy of Sciences of the United States of America 97(11):5954–9. 26. Andersen MC, J.M. Watts, J.E. Freilich, S.R. Yool, G.I. Wakefield, J.F. McCauley, and P.B. Fahnestock. 2000. “Regression-tree Modeling of Desert Tortoise Habitat in the Central Mojave Desert.” Ecological Applications 10(3):890–900. 27. Anderson BW. 1995. “California Exotic Pest Plant Council: Salt Cedar, Revegetation and Riparian Ecosystems in the Southwest. 1995 CalEPPC Symposium Proceedings.” [Web Page]. Located at: http://www.caleppc.org/symposia/95symposium/anderson.html. Accessed 2002 Aug 10. 11-2 Proposed Major Amendment to the Coachella Valley MSHCP – March 2014 28. Anderson BW, and R.D. Ohmart. 1985. “Habitat Use by Clapper Rails in the Lower Colorado River Valley.” Condor 87:116–26. 29. Anderson DR, and K. P. Burnham. 1996. A Monitoring Program for the Desert Tortoise. Unpublished report. 15 pp. 30. Anderson DR, K.P. Burnham, B.C. Lubow, L. Thomas, P.S. Corn, P.A. Medica, and R.W. Marlow. 2001. “Field Trials of Line Transect Methods Applied to Estimation of Desert Tortoise Abundance.” Journal of Wildlife Management 65(3):583–97. 31. Anderson DR, K.P. Burnham, W.R. Gould, and S. Cherry. 2001. “Concerns About Finding Results That Are Actually Spurious.” Wildlife Society Bulletin 29:311–6. 32. Anderson J, and S. Yaffee. 1997. Balancing Public Trust and Private Interest: Public Participation in Habitat Conservation Planning, A Summary Report. Ann Arbor, Michigan: University of Michigan, School of Natural Resources and Environment. 33. Anderson JL. 1994. “Exclosures on the Beaver Dam Slope in Arizona and Utah.” Rangelands 16(5):184–8. 34. Ando A, J. Camm, S. Polasky, and A. Solow. 1998. “Species Distributions, Land Values, and Efficient Conservation.” Science 279:2126–8. 35. Andreassen HP, S. Halle, and R.A. Ims. 1996. “Optimal Width of Movement Corridors for Root Voles: Not Too Narrow and Not Too Wide.” Journal of Applied Ecology 33:63–70. 36. Andren H. 1992. “Corvid Density and Nest Predation in Relation to Forest Fragmentation: A Landscape Perspective.” Ecology 73(3):794–804. 37. Andren H, and P. Angelstam. 1988. “Elevated Predation Rates as an Edge Effect in Habitat Islands: Experimental Evidence.” Ecology 69:544–7. 38. Andrew NG, V.C. Bleich, A.D. Morrison, L.M. Lesicka, and P.J. Cooley. 2001. “Wildlife Mortalities Associated With Artificial Water Sources.” Wildlife Society Bulletin 29(1):275–80. 39. Andrew NG, V.C. Bleich, P.V. August, and S.G. Torres. 1997. “Demography of Mountain Sheep in the East Chocolate Mountains, California.” California Fish and Game 83(2):68–77. 40. Andrews FG, A.R. Hardy, and D. Giuliani. 1979. The Coleopterous Fauna of Selected California Sand Dunes. Sacramento, California: Bureau of Land Management, report # CA-960- 1285-1225-DEOO. 41. Armstrong WP. 1998 Jan. “The Life & Love of Sand Dunes: Part 1, Phenomena of the Wind!” [Web Page]. Located at: http://www.desertusa.com/magjan98/dunes/jan_dune1.html. Accessed 2002 Aug 10. 42. Armstrong WP. 1998 Feb. “The Life & Love of Sand Dunes: Part 2, Life on the Dunes.” [Web Page]. Located at: http://www.desertusa.com/magfeb98/dunes/jan_dune2.html. Accessed 2002 Aug 10. 11-3 Proposed Major Amendment to the Coachella Valley MSHCP – March 2014 43. Arnold C. 1990. “Wildlife Corridors. California Coast and Ocean.” Summer: 10-21. 44. Arrowood PC, C.A. Finley, and B.C. Thompson. 2001. “Analyses of Burrowing Owl Populations in New Mexico.” Journal of Raptor Research 35(4):362–70. 45. As S. 1999. “Invasion of Matrix Species in Small Habitat Patches.” Conservation Ecology 3(1). 46. Aubrey KB. no date. A Key for Identifying Mammal Tracks on Sooted Aluminum Tracking Stations. Unpublished report. 11 pp. 47. Auffenberg W, and R. Franz. 1978. Gopherus agassizii. Catalog. Amer. Amphib. Rept 212:1–2. 48. Averett DE, and K.R. Neisess. 1993. Salvia. In: J.C. Hickman, ed. The Jepson Manual: Higher Plants of California. Berkeley, California: University of California Press. p. 725–9, 733. 49. Avery H. 1998. Nutritional Ecology of the Desert Tortoise (Gopherus agassizii) in Relation to Cattle Grazing in the Mojave Desert. Ph.D. dissertation, University of California Los Angeles. 50. Avise JC, B.W. Bowen, T. Lamb, A.B. Meylan, and E. Bermingham. 1992. “Mitochondrial DNA Evolution at a Turtle's Pace: Evidence for Low Genetic Variability and Reduced Microevolutionary Rate in Testudines.” Molecular Biology and Evolution 9(3):457–73. 51. Bachelet D, R.P. Neilson, J.M. Lenihan, and R.J. Drapek. 2001. “Climate Change Effects on Vegetation Distribution and Carbon Budget in the United States.” Ecosystems 4:164–85. 52. Bagley M. 1989. Sensitive Plant Species Survey on a Portion of the Proposed Fort Irwin NTC Expansion Area, San Bernardino County, California. Prepared for U.S. Army Corps of Engineers, Los Angeles, California. 53. Bailey SJ, C.R. Schwalbe, and C.H. Lowe. 1995. “Hibernaculum Use by a Population of Desert Tortoises (Gopherus agassizii) in the Sonoran Desert.” Journal of Herpetology 29(3):361–9. 54. Bainbridge DA, and R.A. Virginia. 1990. “Restoration in the Sonoran Desert of California.” Restoration & Management 8(1):3–14. 55. Baker RJ, J.C. Patton, H.H.
Load more

Recommended publications
  • UMNP Mountains Manual 2017
    Mountain Adventures Manual utahmasternaturalist.org June 2017 UMN/Manual/2017-03pr Welcome to Utah Master Naturalist! Utah Master Naturalist was developed to help you initiate or continue your own personal journey to increase your understanding of, and appreciation for, Utah’s amazing natural world. We will explore and learn aBout the major ecosystems of Utah, the plant and animal communities that depend upon those systems, and our role in shaping our past, in determining our future, and as stewards of the land. Utah Master Naturalist is a certification program developed By Utah State University Extension with the partnership of more than 25 other organizations in Utah. The mission of Utah Master Naturalist is to develop well-informed volunteers and professionals who provide education, outreach, and service promoting stewardship of natural resources within their communities. Our goal, then, is to assist you in assisting others to develop a greater appreciation and respect for Utah’s Beautiful natural world. “When we see the land as a community to which we belong, we may begin to use it with love and respect.” - Aldo Leopold Participating in a Utah Master Naturalist course provides each of us opportunities to learn not only from the instructors and guest speaKers, But also from each other. We each arrive at a Utah Master Naturalist course with our own rich collection of knowledge and experiences, and we have a unique opportunity to share that Knowledge with each other. This helps us learn and grow not just as individuals, but together as a group with the understanding that there is always more to learn, and more to share.
    [Show full text]
  • Overwintering in Tegu Lizards
    Overwintering in Tegu Lizards DENIS V. ANDRADE,1 COLIN SANDERS,1, 2 WILLIAM K. MILSOM,2 AND AUGUSTO S. ABE1 1 Departamento de Zoologia, Universidade Estadual Paulista, Rio Claro, SP, Brasil 2 Department of Zoology, University of British Columbia, Vancouver, BC, Canada Abstract. The tegu, Tupinambis merianae, is a large South American teiid lizard, which is active only during part of the year (hot summer months), spending the cold winter months sheltered in burrows in the ground. This pattern of activity is accompanied by seasonal changes in preferred body temperature, metabolism, and cardiorespiratory function. In the summer months these changes are quite large, but during dormancy, the circadian changes in body temperature observed during the active season are abandoned and the tegus stay in the burrow and al- low body temperature to conform to the ambient thermal profile of the shelter. Metabolism is significantly depressed during dormancy and relatively insensitive to alterations in body temperature. As metabolism is lowered, ventilation, gas exchange, and heart rate are adjusted to match the level of metabolic demand, with concomitant changes in blood gases, blood oxygen transport capacity, and acid-base equilibrium. Seasonality and the Tegu Life Cycle As with any other ectothermic organism, the tegu lizard, Tupinambis merianae, depends on external heat sources to regulate body temperature. Although this type of thermoregulatory strategy conserves energy by avoiding the use of me- tabolism for heat production (Pough, 1983), it requires that the animal inhabit a suitable thermal environment to sustain activity. When the environment does not provide the range of temperatures that enables the animal to be active year round, many species of ectothermic vertebrates become seasonally inactive (Gregory, 1982).
    [Show full text]
  • Molecular Characterization of Adult Diapause in the Northern House Mosquito, Culex Pipiens
    MOLECULAR CHARACTERIZATION OF ADULT DIAPAUSE IN THE NORTHERN HOUSE MOSQUITO, CULEX PIPIENS DISSERTATION Presented in Partial Fulfillment of the Requirements for the Degree Doctor of Philosophy in the Graduate School of The Ohio State University By Rebecca M. Robich, M.S. ***** The Ohio State University 2005 Dissertation Committee: Professor David L. Denlinger, Advisor Approved by Professor Donald H. Dean ________________________ Professor Glen R. Needham Advisor Graduate Program in Entomology Professor Brian H. Smith ABSTRACT In the northern United States, Culex pipiens (L.), a major avian vector of several arthropod-borne viruses, spends a good portion of the year in a state of developmental arrest (diapause). Although the physiological and hormonal aspects of Cx. pipiens diapause have been well-documented, there is little known on the molecular aspects of this important stage. Using suppressive subtractive hybridization (SSH), 40 genes differentially expressed in diapause were identified and their expression profiles were probed by northern blot hybridization. These genes have been classified into 8 distinct groupings: regulatory function, food utilization, stress response, metabolic function, cytoskeletal, ribosomal, transposable elements, and genes with unknown functions. Among 32 genes confirmed by northern blot hybridization, 6 are upregulated specifically in early diapause, 17 are upregulated in late diapause, and 2 are upregulated throughout diapause. In addition, 2 genes are diapause downregulated and 5 remained unchanged during diapause. Two regulatory genes upregulated in late diapause, ribosomal protein (rp) S3A and rpS6, are of particular interest for their potential involvement in developmental arrest. In other mosquito species, these genes are upregulated prior to oogenesis, and their suppression leads to a disruption in ovarian development.
    [Show full text]
  • Department of the Interior
    Vol. 80 Thursday, No. 63 April 2, 2015 Part V Department of the Interior Fish and Wildlife Service 50 CFR Part 17 Endangered and Threatened Wildlife and Plants; Threatened Species Status for the Northern Long-Eared Bat With 4(d) Rule; Final Rule and Interim Rule VerDate Sep<11>2014 21:11 Apr 01, 2015 Jkt 235001 PO 00000 Frm 00001 Fmt 4717 Sfmt 4717 E:\FR\FM\02APR3.SGM 02APR3 tkelley on DSK3SPTVN1PROD with RULES3 17974 Federal Register / Vol. 80, No. 63 / Thursday, April 2, 2015 / Rules and Regulations DEPARTMENT OF THE INTERIOR midwest/Endangered. Comments and northern long-eared bat (Myotis materials we received, as well as septentrionalis) as a threatened species. Fish and Wildlife Service supporting documentation we used in The basis for our action: Under the preparing the final listing rule, are Endangered Species Act, we can 50 CFR Part 17 available for public inspection at http:// determine that a species is an endangered or threatened species based [Docket No. FWS–R5–ES–2011–0024; www.regulations.gov, and by 4500030113] appointment, during normal business on any of five factors: (A) The present hours at: U.S. Fish and Wildlife Service, or threatened destruction, modification, RIN 1018–AY98 Twin Cities Ecological Services Office, or curtailment of its habitat or range; (B) overutilization for commercial, Endangered and Threatened Wildlife 4101 American Blvd. East, Bloomington, MN 55425; telephone (612) 725–3548, recreational, scientific, or educational and Plants; Threatened Species Status purposes; (C) disease or predation; (D) for the Northern Long-Eared Bat With ext. 2201; or facsimile (612) 725–3609.
    [Show full text]
  • Minimal Overwintering Temperatures of Red-Sided Garter Snakes (Thamnophis Sirtalis Parietalis): a Possible Cue for Emergence?
    771 NOTE / NOTE Minimal overwintering temperatures of red-sided garter snakes (Thamnophis sirtalis parietalis): a possible cue for emergence? Deborah I. Lutterschmidt, Michael P. LeMaster, and Robert T. Mason Abstract: Red-sided garter snakes (Thamnophis sirtalis parietalis (Say in James, 1823)) in Manitoba, Canada, undergo 8 months of continuous winter dormancy prior to spring emergence. As in other ectothermic species, increases in ground temperature may be the cue for emergence from winter dormancy in these populations. To test this hypothesis, we meas- ured body temperatures during winter dormancy by surgically implanting small temperature loggers into 32 female red- sided garter snakes before they entered their native hibernaculum. The following spring, we recaptured seven of the snakes implanted with temperature loggers. Body temperature declined gradually from mid-September (14.7 ± 0.24 8C, mean ± SE) to early April (1.1 ± 0.16 8C, mean ± SE) during winter dormancy, reaching minimal values approximately 1 month prior to spring emergence. Body temperatures of emerging snakes ranged from 0.5 8C during early spring to 6.3 8C during late spring (3.4 ± 0.84 8C, mean ± SE). These results do not support the hypothesis that an increase in ground temperature (and hence body temperature) is necessary for emergence from winter dormancy. We suggest that critically low tempera- tures (i.e., 0.5–1 8C) are a Zeitgeber entraining an endogenous circannual cycle that regulates snake emergence. These re- sults offer new insight into the mechanisms regulating seasonal emergence from winter dormancy. Re´sume´ : Les couleuvres raye´es a` flancs rouges (Thamnophis sirtalis parietalis (Say in James, 1823)) du Manitoba, Can- ada, comple`tent 8 mois continus de dormance d’hiver avant leur e´mergence au printemps.
    [Show full text]
  • 12. Kootenay Boundary Field Guide
    Wildlife Habitat Features Field Guide (Kootenay Boundary Region) 12. A Bat Hibernaculum 1) Definition A bat hibernaculum (plural: hibernacula) means a site where one or more bats hibernate in winter. Figure 43 shows the entrance to a cave hibernaculum. Figure 43. Townsend’s Big-Eared Bat hibernaculum located in a cave. (Photo: Anna Roberts) 2) Importance of a Bat Hibernaculum A bat hibernaculum is a site where bats hibernate over the winter. A specific hibernaculum may only be used for part of the winter and may or may not be used every year. The lack of use in a given year does not mean that the hibernaculum has been abandoned. Hibernacula occur most often in caves (Figure 43), rock or cliff crevices (Figure 44), or abandoned mines. Note: Only naturally occurring bat hibernacula are considered wildlife habitat features. Hibernacula provide cold, constant temperatures and protection from weather and predators. Rock features with suitable characteristics for hibernation by bats are relatively scarce across the landscape and therefore are typically used by several species of bats at once. The cool, moist microclimate of a hibernaculum allows bats to enter a torpid state where breathing rate, metabolic rate and heart rate are significantly decreased from active levels and body temperatures drop to match the air temperature. Bats naturally awaken infrequently over the winter from this torpid state. Recent work on wintering bats in British Columbia has revealed that bats are far more active in winter than previously assumed. Movements appear to occur during warmer periods in winter. During these periods’ bats may move to different roosting areas within the hibernation site or move outside the underground feature to roost in adjacent large roost trees 77 Wildlife Habitat Features Field Guide (Kootenay Boundary Region) within 500 m of a hibernaculum opening.
    [Show full text]
  • Reptile Dispersal from a Hibernaculum in an Agricultural Landscape in Western France
    Reptile dispersal from a hibernaculum in an agricultural landscape in Western France ROGER MEEK 7 rue Georges Clemenceau, Chasnais, France 85400 [email protected] ABSTRACT – Observations have been made on post hibernation movements in four species of reptile, , Natrix natrix, Vipera aspis and Lacerta bilineata, around a hibernaculum in west- ern France. Movement around the hibernaculum was observed between late March and late May with most sightings in April. Sightings gradually declined as April progressed with no reptiles seen after May 28. INTRODUCTION Situated in the northern end of a hedgerow Winter temperatures are a key factor in the system surrounding what had previously been a survivorship of temperate reptiles and hence drainage ditch, the den area consisted of a selection of an appropriate winter hibernaculum discontinuous series of drainage pipe remnants is a crucial life history attribute (e.g. Vipera of approximately 1 m diameter. European ash berus: Viitanen, 1967; Presst, 1971; Thamnophis (Fraxinus excelsior) formed the canopy with a sirtalis: Gregory, 1977; V. aspis: Altweg et al,. dense understory of bramble growth (Rubus 2005). The biology of hibernacula has been fruticosus). A combination of autumn leaf fall, fairly well-studied in some North American drifting soil from agricultural land and lack of reptiles (e.g. Macartney, et al., 1989; Brent maintenance resulted in debris entering the Charland, 1989, Harvey & Weatherhead, 2006; pipes, leaving only limited openings of less than Gregory, 2011) but less information is available 15 cm at the top of the pipes for entry. The exact on species from Europe (Viitanen, 1967; Presst, and full extent of the chamber was difficult to 1971; Whiting & Booth, 2012).
    [Show full text]
  • Thermal Ecology of the Garter Snakes Thamnophis Sirtalis Concinnus (Hallowell) And
    AN ABSTRACT OF THE THESIS OF GLENN R. STEWART for the Ph. D. in Zoology (Name) (Degree) (Major) Date thesis is presented > /4 Title THERMAL ECOLOGY OF THE GARTER SNAKES THAMNOPHIS SIRTALIS CONCINNUS (HALLOWELL) AND THAMNOPHIS ORDINOIDES (BAIRD & GIRARD), Abstract approved In recent years, studies dealing with temperature regulation, temperature sensitivity, and physiological responses to temperature in lizards and other reptiles have increased tremendously. It is notable that snakes have been largely ignored in such studies. This no doubt is due to their less direct relationship to ancestral endo- therms. However, problems in the ecology of snakes themselves may be elucidated by studies of this kind. The present study deals with two species of garter snakes ( Thamnophis sirtalis concinnus and Thamnophis ordinoides) which are abundant in Oregon's Willamette Valley. The species sirtalis is the most wide ranging snake in the United States. It is commonly found near permanent water, though occasionally it is encountered in rather dry situations. In contrast to sirtalis, the monotypic species ordinoides is a strictly terrestrial northern Pacific Coast form, which typically is associated with areas of dense vegetation. T. s. concinnus is often seen basking on mild days of the coldest winter months (November- February) while T. ordinoides rarely emerges during these months. The distinct differences in habitat preference and winter behavior exhibited by these snakes suggest differences in thermal preferences and critical levels. To examine this possibility, and the responses of the snakes to thermal acclimation, comparative data on the following variables have been sought: 1) Body temperature of snakes in the field and its relationship to environmental temperatures; 2) body temperature of snakes in a thermal gradient box; 3) critical thermal maximum and minimum; 4) metabolic rate; 5) the effect of thermal acclimation on items two, three, and four.
    [Show full text]
  • Wildlife Habitat Suitability Models
    Benga Mining Limited Grassy Mountain Coal Project July 2016 APPENDIX C: WILDLIFE HABITAT SUITABILITY MODELS Benga Mining Limited Grassy Mountain Coal Project July 2016 Table of Contents 1.0 APPROACH ........................................................................................................................................ C-5 1.1 General Overview ........................................................................................................................... C-5 1.2 Habitat Suitability Ratings ............................................................................................................ C-6 1.3 Model Adjustments ...................................................................................................................... C-16 1.4 Specific Methodology ................................................................................................................... C-16 2.0 VALUED COMPONENT SPECIES ACCOUNTS AND MODELS ........................................ C-21 2.1 Columbia Spotted Frog ................................................................................................................ C-21 2.1.1 Distribution and Abundance .............................................................................................. C-21 2.1.2 Ecology and Key Habitat Requirements ........................................................................... C-21 2.1.3 Response to Disturbance ..................................................................................................... C-23 2.1.4
    [Show full text]
  • The University of Notre Dame
    The University of Notre Dame Ecology of Cave Use by the Frog, Rana palustris Author(s): William J. Resetarits, Jr. Source: American Midland Naturalist, Vol. 116, No. 2 (Oct., 1986), pp. 256-266 Published by: The University of Notre Dame Stable URL: http://www.jstor.org/stable/2425733 . Accessed: 25/01/2011 16:41 Your use of the JSTOR archive indicates your acceptance of JSTOR's Terms and Conditions of Use, available at . http://www.jstor.org/page/info/about/policies/terms.jsp. JSTOR's Terms and Conditions of Use provides, in part, that unless you have obtained prior permission, you may not download an entire issue of a journal or multiple copies of articles, and you may use content in the JSTOR archive only for your personal, non-commercial use. Please contact the publisher regarding any further use of this work. Publisher contact information may be obtained at . http://www.jstor.org/action/showPublisher?publisherCode=notredame. Each copy of any part of a JSTOR transmission must contain the same copyright notice that appears on the screen or printed page of such transmission. JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact [email protected]. The University of Notre Dame is collaborating with JSTOR to digitize, preserve and extend access to American Midland Naturalist. http://www.jstor.org Ecologyof Cave Use by the Frog,Rana palustris WILLIAM J.
    [Show full text]
  • Metabolic Flexibility: Hibernation, Torpor, and Estivation
    Metabolic Flexibility: Hibernation, Torpor, and Estivation James F. Staples*1 ABSTRACT Many environmental conditions can constrain the ability of animals to obtain sufficient food en- ergy, or transform that food energy into useful chemical forms. To survive extended periods un- der such conditions animals must suppress metabolic rate to conserve energy, water, or oxygen. Amongst small endotherms, this metabolic suppression is accompanied by and, in some cases, fa- cilitated by a decrease in core body temperature—hibernation or daily torpor—though significant metabolic suppression can be achieved even with only modest cooling. Within some ectotherms, winter metabolic suppression exceeds the passive effects of cooling. During dry seasons, estivating ectotherms can reduce metabolism without changes in body temperature, conserving energy re- serves, and reducing gas exchange and its inevitable loss of water vapor. This overview explores the similarities and differences of metabolic suppression among these states within adult animals (excluding developmental diapause), and integrates levels of organization from the whole animal to the genome, where possible. Several similarities among these states are highlighted, including patterns and regulation of metabolic balance, fuel use, and mitochondrial metabolism. Differences among models are also apparent, particularly in whether the metabolic suppression is intrinsic to the tissue or depends on the whole-animal response. While in these hypometabolic states, tis- sues from many animals are tolerant of hypoxia/anoxia, ischemia/reperfusion, and disuse. These natural models may, therefore, serve as valuable and instructive models for biomedical research. © 2016 American Physiological Society. Compr Physiol 6:737-771, 2016. Introduction the gas exchange required to support aerobic metabolism is associated with some inevitable loss of water vapor from gas Metabolic energy is required for animal development, exchange surfaces.
    [Show full text]
  • Hibernation and Aestivation in Gastropod Molluscs
    HIBERNATION AND AESTIVATION IN GASTROPOD MOLLUSCS. ON THE HABITS OF A SLUG FROM DALHOUSIE (WESTERN HIMALAYAS), 'VITH REMARKS ON CERTAIN OTHER SPECIES OF GASTROPOD MOLLUSCS. By SUNDER LAL HORA, D.Bc., F.L.B., F.Z.B., Zoological Survey of India, Calcutta. CONTENTS. PAGE. Habits of the Dalhousie Slug 357 Tree-climbing habits of certain snails and their biological significance 361 The' Hibernaculum ' of Oremnockonchus sylw,dre1UJi8 Blanford 365 The Epiphragm : its form and function 365 Awakening after torpidity 369 Conclusions 371 Literature 372 HABITS OF THE DALHOUSIE SLUG. I was spending the summer of 1927 at Dalhousie, altitude about 7,000 feet above sea level, in the Western Himalayas and in the course of my daily walks I noticed the peculiar habits of the common slug, .A.nadenus dalhousiensis Bhatia.! The months of May and June are generally very hot and dry in this part of the country, but fortunately during my stay the weather remained pleasant on account of occasional rain storms. These storms are rather unusual for this time of the year. There was a regular alternation of hot and dry weather for a fortnight or so follo,ved by cloudy weather with rain for three or four days. During these wet days a number of slugs were always noticed crawling about on the roads and rocks at the side, but on the approach of the dry weather they gradually became scarce and ultimately disappeared altogether even from shady places. After observing this behaviour of the slug on three or four occasions I became interested to learn what happened to these animals during the dry weather.
    [Show full text]