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USING RESOURCE UTILIZATION FUNCTIONS (RUFs) TO ASSESS WILDLIFE-HABITAT RELATIONSHIPS
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Transcript of USING RESOURCE UTILIZATION FUNCTIONS (RUFs) TO ASSESS WILDLIFE-HABITAT RELATIONSHIPS
USING RESOURCE UTILIZATION FUNCTIONS (RUFs) TO ASSESS
WILDLIFE-HABITAT RELATIONSHIPS
Y = β0 + β1x1+ β2x2 + β3x3 + βnxn ……
Brian KertsonWildlife Science GroupSFR/WACFWRU
HABITAT IS THE KEY FOR WILDLIFE
• Understanding relationships is critical-Food-Reproduction-Survivorship-Predator-prey dynamics-Behavior and ecology
• Management and conservation
KEY TERMINOLOGY
• Use: how much, how often – metric matters • Selection/Avoidance: animal uses resource more
or less than available• Preference: animal selects between 2 equally
available resources
WILDLIFE-HABITAT METHODS
• Many analytical procedures available• Common techniques:
-Compositional Analysis-Resource Selection Functions (RSFs)-Resource Selection Probability Functions (RSPFs)
• Varying degrees of rigor, each has advantages and disadvantages
COMMON PROBLEMS
• Lack of independence of observations
• Incorrect sampling unit• Habitat data and scale
-Use of remote sensing• Unit-sum constraint• Discrete use• Failure to connect with
behavior (i.e., fitness)
USED VS. UNUSED LIMIATIONS
• Logistic regression• Contamination:
-Classified as unused when it was used-GPS -Snow tracking-Critter cams
PROBLEMS DEFINING AVAILABILITY
• Can we know how animals perceive their environment?
• Do we actually know what is available?
• NO!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!• Arbitrary • Home range simulations:
-Rigorous: potentially-Biologically meaningless
You know
nothing!!
Stupid hairless
monkeys.
ADDITIONAL AVAILABILITY ISSUES
Kertson and Marzluff, in press
Resource Utilization Functions
• Marzluff et al. 2004 (Ecology)• Continuous:
-High vs. low use (relative comparison) • Multivariate:
-Multiple regression• Individual is sampling unit:
-Quantify individual variation• No measure of availability
HOW THE RUF WORKS
Animal relocations99% Utilization Distribution
(Use values) Sampling grid
Use and habitat covariates
Ruf.fit
KEY TOOLS
• ArcMap 9.x• Hawth’s Tools:
http://www.spatialecology.com/htools/index.php
-Bivariate kernel• Excel or Notepad• R statistical computing
-Ruf.fit packagehttp://csde.washington.edu/~handcock/ruf/
MEASURING USE
• Individual = sampling unit• Sampling design critical
-Individuals-Monitoring
• Increase monitoring, more refined UD
• VHF vs. GPS:-Increased resolution-Increased accuracy-Not perfect
Kertson and Marzluff, in press
UTILIZATION DISTRIBUTION (UD)
• Animal use is not random-Gradient of use
• Probability Density Function (pdf)-Sums to 1
• Use = height (volume) of UD
UD ESTIMATION
• Fixed kernel • Min. of 30 relocations
-Preferably n ≥ 50• Resolution (grid size):
-25 or 30 m common• Bandwidth smoothing (h)
-Most critical component
SELECTION OF h • Selection: data • Over vs. under-smoothing• Univariate vs. bivariate• Lots of options:
-Reference (HREF)-Least-squares cross-validation (LSCV)-Plug in (PI)-Solve the equation (STE)-Biased cross validation (BCV)
• Each has +/-
EFFECTS OF h ON UD
Kertson and Marzluff, in press
Kertson and Marzluff, in press
ESTIMATING h
• Animal Movements Extension (ArcView 3.3)• ArcMap 9.x:
-Home Range Tools (HRT)*LSCV, BCV, HREF
• R statistical computing:-KernSmooth package-KS package *PI values from both (bivariate)
UD CHALLENGES
• UD size can push the limits of software:-Male cougar UDs can exceed 2.0 million points
• Over-smoothing:-Lakes, rivers, major highways, and other unsuitable/unusable habitat
• Under-smoothing:-Donut holes and disconnect cores
• Solutions:-Clip UD (over-smoothing) -Adjust h (try different bandwidth method)-Little bit of black magic here
LANDSCAPE COVARIATES
• Covariate types:-Categorical -Continuous
• Resolution:-As fine as possible-Landscape configuration-Remote sensing
• Transformations:-Can improve model performance
Distance to Water
Percent Conifer Forest
CATEGORICAL COVARIATES
• Common categorical covariates:-Landcover-Aspect
• Classes for each variable are not independent• Must be recoded 0,1
-No. of columns = no. of classes
CATEGORICAL COVARIATES
LC_5 Conifer Forest
Mixed Forest
Riparian High Elevation
Urban
1 1 0 0 0 04 0 0 0 1 03 0 0 1 0 05 0 0 0 0 12 0 1 0 0 0
RUF.FIT• Developed by Dr. Mark Handcock (UW-CSSS)• Multiple regression:
Y = β0 + β1x1+ β2x2 + β3x3 + βnxn ……
• Code:Cat1<- ruf.fit(USE ~ COV1 + COV2 + COV3 + COV4, space= ~ X + Y, data=data_file, theta=hval, name=“whatever_you_want", standardized=F)
• Corrects for spatial dependence in UD• Unstandardized and standardized
coefficients
MODEL COEFFICIENTS• Average for sample• Coefficient signs:
-Increase use (+); decrease use (-)• Unstandardized:
-Mapping predicted occurrence• Standardized:
-Statistical significance of individual covariates-Differences between covariates-Relative importance-Proportion of sample +/- influence
RUF.FIT OUTPUT> summary(CAT1)
Standardized Coefficients for name: Misska
Matern Log-Lik = -9195.395 LS Log-Lik = -9331.533
Change in Log-Lik 136.1377 p-value = < 1e-04
MLE s.e. LS estimate LS s.e.range 149.277454 5.437344 NA NAsmoothness 1.500000 NA NA NA(Intercept) 30.387746 0.117809 16.851820 0.107699PCCREG 7.008595 0.223041 0.265138 0.001150PCF 8.226134 0.283357 0.221347 0.000960PFOREST -0.371450 0.191588 -0.018902 0.001464DWATER -2.234107 0.161222 -0.011138 0.000153DISTEDGE 3.158826 0.178807 0.053626 0.000406DISTROAD -0.565676 0.120716 -0.004882 0.000147DRESD -6.581544 0.225750 -0.004287 0.000025RESDENS1KM 0.854841 0.095044 0.005812 0.000373PAR -1.252951 0.599006 -0.078281 0.001941SLOPE 0.272329 0.308374 0.004249 0.001152DEM 5.641831 0.406940 0.002025 0.000015
β and associated SE
HOW DOES LANDSCAPE INFLUENCE COUGAR-HUMAN INTERACTION?
• Apex predator with a large home range• Largest geographic distribution of any
terrestrial mammal in western hemisphere-Tremendous habitat diversity
• Key landscape resources:-Ungulate prey-Cover
• High levels of interaction with people
METHODOLOGY
• Captured 32 cougars in western WA, outfitted with GPS collars
• Investigated interaction reports• Focused on landscape metrics I suspect
correlate with prey and cover• Modeled with RUF• Quantified individual variation
UNSTANDARDIZED COEFFICIENTS
COUGAR PREDICTED USE
STANDARDIZED COEFFICIENTS
CONSERVATION AND MANAGEMENT IMPLICATIONS
• Identify key resources to manage and conserve• Identify high quality habitats• Develop proactive management strategies
-71.5% of confirmed interactions occurred in high and med-high use habitats-Management hotspots
• Space use and interactions with people highly individualized-Population approaches may not work
REGIONAL APPLICATIONS
ADDITIONAL APPROACHES
• Sex and age specific RUFS:-Male vs. female-Adult vs. subadult
• Behavior specific:-Movement rates-Relates habitat use to different aspects of fitness
Traveling Resting/Feeding
HuntingNursing
RUF CHALLENGES
• The more RAM the better• Capable of running full data set, may need to sub-
sample• Processing time can be significant• Model comparisons (e.g., model parsimony)
difficult-RUF outputs log-likelihoods (ΔAIC)
RUF LIMITATIONS
• Models are tools, not absolute truth• Results are only as good as the data used
-Limitations and accuracy of remotely-sensed data• Do the results pass the laugh test?• Subject to same assumptions as normal multiple
regression• No alternatives for correcting spatial dependence
in UD
NEED DIRECTIONS?