KRISTY CAMPBELL WINTER ECOLOGY,SPRING 2014 Mountain Research Station, University of Colorado, Boulder The Effect of Elevation on Mammal Behavior and Abundance.

Slides:



Advertisements
Similar presentations
Winter Invertebrate Composition as a Function of Elevation How does invertebrate richness, diversity, and abundance change throughout an elevational gradient?
Advertisements

The effect of trees on snowpack: live versus dead lodgepole pines in subalpine forest Dylan Brown Winter Ecology Spring 2014 Mountain Research Station,
Mountain Research Station – University of Colorado, Boulder.
Varying snow depths and the effect on moose Movement Alyssa Countway Winter Ecology Spring 2014 Mountain Research Station, University of Colorado, Boulder.
Matt Guyerson Winter Ecology Spring 2014 Mountain Research Station, University of Colorado, Boulder.
INTRODUCTION  Many areas within the subalpine area of the San Juan Mountains are commonly used for human recreational activities such as backcountry skiing,
How do snowpack depth and proximity to trees affect subnivean plant growth Robin Reibold Winter Ecology: Spring 2014 Mountain Research Station, University.
Bivariate Statistics GTECH 201 Lecture 17. Overview of Today’s Topic Two-Sample Difference of Means Test Matched Pairs (Dependent Sample) Tests Chi-Square.
You would not go and count every single flower
Diversity and Distribution of Species
Plant diversity and land use under organic and conventional agriculture: a whole- farm approach Paper by: R. H. GIBSON, S. PEARCE, R. J. MORRIS, W. O.
Introduction Subalpine meadows play a crucial role in species diversity, supporting many endangered species of plant and wildlife. Subalpine meadows play.
 Vegetation Density and Snow Accumulation Evan Esfahani Winter Ecology 2014 Mountain Research Station.
Elevation Distribution of Vaccinium Myrtillus in Spruce-Fir and Lodge Pole Forests. By: Nicholas Condello Schwinger 7/ 17/2013.
+ Trail Disturbance in the Alpine Meadow on Arapaho Pass and Mount Yale Marieta Bialek Vegetation Ecology 2013 Mountain Research Station University of.
Impact of Aspect on Stand Density and Species Frequency in Gordon Gulch Brian Owens II University of Colorado, Boulder.
Copyright © Cengage Learning. All rights reserved. 11 Applications of Chi-Square.
Supranivean travel of snowshoe hares on Niwot Ridge Marieta Bialek EBIO 4100 Winter Ecology Spring 2012.
Habitat Use of the Snowshoe Hare Melissa Pacheco Winter Ecology Spring 2010 Mountain Research Station, University of Colorado, Boulder.
World Biomes Boreal forest or Taiga. Climate Long, cold winters, and short, mild, wet summers are typical of this region. In the winter, chilly winds.
Colorado Life Zones Alpine Prairie 2. Foothills 3. Montane 4.
Impact of Recreational Snow Compaction on Small Mammals in the Subnivean Space Derek Sweeney EBIO 4120 Spring 2008 Mountain Research Station University.
Animal Activity and Tree Well Width Erin Kinney Winter Ecology 2011 Mountain Research Station, University of Colorado, Boulder Erin Kinney Winter Ecology.
Vulnerability of moose and roe deer to wolf predation in Scandinavia - does habitat matter? Contact Lisette Fritzon
Mammal activity in the sub-alpine urban- interface in relation to distance from settlement boundary. Kyle Poos-Benson Winter Ecology 2014 Mountain Research.
PCB 3043L - General Ecology Data Analysis. OUTLINE Organizing an ecological study Basic sampling terminology Statistical analysis of data –Why use statistics?
Birds on the Edge Forest edge effects on bird assemblage size and composition in the Chuckanut Mountains Drew Schwitters Department of Environmental Sciences,
 Comparing Vegetation in a Riparian Zone to an Upland Area in a Colorado Montane Forest By: Abby Branson Vegetation Ecology, Summer 2013 Mountain Research.
By Michael R. McHugh Winter Ecology Spring 2010 Mountain Research Station – University of Colorado, Boulder.
Rachel Jones Winter Ecology Spring 2013 Mountain Research Station, University of Colorado, Boulder Photo by Yellow Wood Guiding.
Subnivean Access in Forests of Varying Density Patrick Ellsworth Winter Ecology, Spring 2013 Mountain Research Station.
The effect of tree density and height on tree-flagging of Lodgepole Pines in Niwot’s sub-alpine forest Michael D. Schuster Winter Ecology – Spring 2010.
WINTERTIME MAMMAL ACTIVITY – SPECIFIC ENVIRONMENTAL CONTROLS Brian Inglis EBIO Winter Ecology Mountain Research Station Spring ’12 CU Boulder.
Biomes. What is a biome?  Biomes refer to a large region or area characterized by the following: 1. A particular pattern of the annual temperature and.
PCB 3043L - General Ecology Data Analysis.
Inference for Tables Catapult Discovery Question: –How does a cat land (feet, side, nose/face)? –Write your predictions in percent. Collect data for.
Winter Controls on the Distribution of Arboreal Hair Lichens in the Niwot Ridge Biosphere Reserve Keli Baker Winter Ecology Spring 2013 Mountain Research.
381 Goodness of Fit Tests QSCI 381 – Lecture 40 (Larson and Farber, Sect 10.1)
Are the Snowpack Structures Different Between the Riparian and Upland Environments? Allie B. Cunningham Winter Ecology Spring 2015 CU Mountain Research.
Genesis Machek Winter Ecology, Spring 2010 Mountain Research Station - University of Colorado at Boulder.
Soil & Herbaceous Composition Among Differing Strata Phil Mortellaro Vegetation Ecology Summer ‘13 Mountain Research Station, University of Colorado Boulder.
A snowpack comparison between a limber pine site and a spruce site within a spruce forest Sam Sartwell, Winter Ecology, EBIO 4100, Spring 2014, CU Mountain.
Kate Lonner Winter Ecology Spring 2015 Mountain Research Station, University of Colorado, Boulder.
MICROBE ACTIVITY COMPARISON BETWEEN NORTH AND SOUTH FACING SLOPES Jake DePompolo CU Mountain Research Station 2015.
Wolverines are known for scavenging dead animals like caribou or moose but are also very capable of killing their own meal, including ground squirrels.
Kirill Langer Vegetation Ecology Summer Semester July 2013 University of Colorado Mountain Research Station Plant Species Diversity in the Subalpine Elk.
TREE WELLS: COMPARISON OF CONIFEROUS AND DECIDUOUS TREES Magali Weissgerber, Winter Ecology, Spring 2015, CU Mountain research Station.
Aquatic Macroinvertebrate Composition Over an Elevation Gradient
The Effects of Topography on Forest Cover in Subalpine Forest
Charles J. Krebs, Jeffery R. Werner, and Rudy Boonstra
PCB 3043L - General Ecology Data Analysis.
Canada’s Natural Regions
Distribution of Arboreal Lichens Relative to Snowpack
Vegetation Composition in Niwot’s Riparian Tundra
Trail Effects on Squirrel and Snow Shoe Hare Density
Snow Compaction Variation Across a Subalpine Transect
Snowshoe hare behavior in different environments
Species Diversity Comparison North and South Slopes
A Comparison of Riparian Vegetation Structures
Pressure Chapter 3.3.
Statistical Analysis Chi-Square.
SEASONAL DISTRIBUTION PATTERNS OF DEER.
Landscape Features Affecting Squirrel Cache Density and Location
Aspen Tree Well Influence on Microbial Respiration
Questions Do fish species differ in relative abundance as a function of zone (shallow, deep) This should be in the context of a specific set of predictions.
Influence of canopy cover on behavioral traits of snowshoe hare
Tina Nguyen Vegetation Ecology Summer 2018
The effects of Canopy Cover on Herbaceous Vegetation
Presentation transcript:

KRISTY CAMPBELL WINTER ECOLOGY,SPRING 2014 Mountain Research Station, University of Colorado, Boulder The Effect of Elevation on Mammal Behavior and Abundance in Winter

Introduction Morphological and physiological adaptations allow mammals to survive the winter in Colorado. Behavioral Adaptation – Some mammals utilize the insulative properties of snow. Physical Adaptation – The Snowshoe Hare has large feet that allow it to easily walk across the snow (like snowhoes)

Introduction Because of the deeper snowpack at higher elevations, larger mammals such as moose and deer are found more often at lower elevations (Poole & Stuart-Smith 2006).

Introduction Studies have shown that species diversity and abundance of small mammals in riparian zones is greater than in upland areas (Doyle 1990). These mammals may be drawn to the riparian zones for water, abundance of vegetation, or abundance of other prey mammals. For these reasons, I focused my study on riparian zones at different elevations.

Introduction Hypothesis – The proportion of smaller to larger mammals increases with elevation in the winter. Prediction - Tracks from smaller mammals (such as squirrels and Snowshoe Hares) will be more abundant at higher elevations than at lower elevations. Tracks from larger mammals (such as ungulates), will be more abundant at lower elevations.

Methods 2 elevations along Como Creek 50 m transect through the riparian area Observed animal tracks at 10 random points along the transect 10 m Riparian zone

Methods 3020 m 2857 m

Methods Measured Snow depth and type of vegetation at both sites. Analyzed differences in species frequency and density at both elevations using a Chi-Square Test. Site m site m

Site 1 Site 2 Snow Depth – 90 cm Vegetation:  Willows  Lodegpole Pine  Spruce  Aspen Slope – flat area ( 4◦) Snow Depth – 60 cm Vegetation:  Willows  Lodgepole Pine  Spruce  Aspen Slope – flat area ( 6◦) Results

Results: Density of Tracks Density of track found at site 1 (high elevation) and site 2 (low elevation) Site 1Site 2 Chi-Square Test of Independence H 0 = The density at each site is not different from a random distribution. P = 0.56 There was no significant difference from random. The null hypothesis could not be rejected.

Results: Relative Frequency of Tracks Chi- Square Goodness of Fit Test H o – The frequency distributions are the same. P = 0.90 There was no significant difference in relative frequency of tracks found between site 1 and site 2. The null hypothesis could not be rejected. Relative Frequency of tracks found at site 1 (high elevation) and site 2 (low elevation)

Results: Absolute Frequency of Tracks Chi- Square Goodness of Fit Test H o – The frequency distributions are the same. P = 0.95 There was no significant difference in absolute frequency of tracks found between site 1 and site 2. The null hypothesis could not be rejected. Absolute Frequency of tracks found at site 1 (high elevation) and site 2 (low elevation)

Discussion The frequency and density of different mammal tracks found at both sites tested were statistically identical to each other. Vegetation at both sites was the same. Elevation was not as different as planned. Snow depth was different, but the top layer of snow was firm. The coyote tracks found at the high elevation did not penetrate deep into the snow.

Discussion My hypothesis was not supported. However, due to the constraints of my study, I think that further research could be done: More replicates need to be done at each site. There needs to be a larger difference in elevation. At least one more lower elevation needs to be studied. Perhaps asking permission of private land owners to study animal tracks near the creek.

3200 m 2857 m 2469 m

Discussion Not all methods could be carried out as planned: I planned to begin collecting data at 3200 m (the top of Komo Creek), but I could not find the creek. I began instead at 3020 m. I planned to collect my final set of data at an elevation of 2469 m, but I could not access the sampling area because it was on private land.

References Doyle, A. T Use of Riparian and Upland Habitats by Small Mammals. Journal of Mammalogy. Vol 71. No. 1: Gillis, E. A., Hilk, D.S., Boonstra R., Karels, T.J., and Krebs, C.J Being High is Better: Effects of Elevation and Habitat on Arctic Ground Squirrel Demography. OIKOS 108: Poole, K.G., and Stuart-Smith Winter Habitat Selection by Female Moose in Western Interior Montane Forests. Canadian Journal of Zoology. Vol 84: