“MODELLING THE EFFECT OF HEALTH RISK PERCEPTION ON
PREFERENCES AND CHOICE SET FORMATION OVER TIME:
RECREATIONAL HUNTING SITE CHOICE AND CHRONIC
WASTING DISEASE
THUY TRUONG
VIC ADAMOWICZ
PETER BOXALL
Resource and Environmental Economics
University of Alberta
OUTLINE
What is Chronic Wasting Disease?
Random Utility Models and Choice Set
Formation
Empirical Approach
Data and Some Descriptive Statistics
Model Results, Welfare Measures
Extensions and Limitations
Conclusions
THE PROBLEM: WHAT IS THE ECONOMIC
WELFARE IMPACT OF CWD?
Chronic Wasting Disease (CWD): prion disease
that affects deer, elk and other cervid wildlife
species
Neurodegenerative disease
BSE, Scrapie, CWD, Creutzfeldt Jakob Disease (vCJD)
No known link between the consumption of CWD
affected meat and human health, but
Cautions were provided to hunters
CWD might affect a recreational hunter’s:
choice sets
site choice
…and these effects might change over time
Source: "Chronic Wasting Disease Alliance (www.cwd-info.org)"
ECONOMIC IMPACTS OF CWD IN ALBERTA
Hunting
Cervid Farming Sector
Resident Hunters - Recreational Hunting
Aboriginal People – Traditional Use
Elk Farms
“Passive Use Values”
General Public View of CWD and Resource
Allocation
Risk to Threatened Species
Landowners
Wildlife Viewing / Recreation
Consumers / Food
Non-Resident Hunters
Source: Alberta SRD
http://srd.alberta.ca/BioDiversityStewardship/WildlifeDiseases/
documents/CWD-PositiveMap-Jan-21-2009.pdf
MANAGEMENT OF CWD
Government initiated CWD
control programs
Testing of deer heads
Provide extra tags/licenses
Allow more deer to be harvested by
hunters
Culling of deer
Only way to find disease
“experts” find deer, remove them, and
test for CWD
CWD may be perceived as a
health risk, or a nuisance, or
both, or neither!
CHOICE AND CHOICE SET FORMATION
Random Utility Theory
U jn = β ′X jn + ε jn
Pjn = Pr{U jn > U j 'n , ∀j '∈ Cn , j ' ≠ j} = Pr{U jn > max(U j 'n ), ∀j '∈ Cn , j ' ≠ j}
exp( µV jn )
exp( µβ ′X jn )
∴ Pjn =
=
∑ exp(µVkn ) ∑ exp(µβ ′X kn )
k∈Cn
k∈Cn
A More General Approach (Swait et al)
i ← ∆n
*
n
j∈C n
{
(
~
U = V ( X , Z n ; β ) + ε X , Z n ;θ
)}
OBJECTIVES OF THE STUDY
Identify whether changes in potential health
risks (CWD) result in
change in utility of a recreation site
change in its availability in the choice set (choice
set formation)
Analysis of effects over time
Examine if there are scale differences over time
and data generating mechanism
Examine specifications of choice set formation
models
Examine if approximations to choice set
formation provide similar results to a fully
endogenous choice set formation model
LITERATURE REVIEW – CHOICE SETS
Exogenously determined choice sets
Define choice set using survey responses:
spatial boundaries, distance, familiarity
Explicit modeling
Modeling choice sets (endogenous choice sets)
Haab and Hicks’ (1997)
Manski’s approach (Swait 1984, Swait and Ben-Akiva 1987a
and Ben-Akiva and Boccara 1995)
GenL model (Swait 2001)
Hicks and Schnier (2010)
Implicit modeling
Cascetta and Papola (2001)
Martinez et al (2009)
Bierlaire et al (2010)
Kuriyama et al (2003)
EXPLICIT MODELING OF CHOICE SET
Haab and Hicks’ model:
p=
j
∑ P( j | j ∈C ) P( j ∈C )
Ck ⊆ Cm
k
Manski’s two stage decision process:
pj =
k
Disadvantage:
∑ P ( j | C ) Q (C )
Ck ⊆ Cm
k
k
Large number of possible choice sets (2J -1)
Intractable for large choice problems
Site choice utility
Choice set
INDEPENDENT AVAILABILITY MODEL
Swait (1984)
Probability of Ck being the ”true” choice set
Q ( Ck ) =
∏ A ∏ (1 − A )
j∈Ck
j
l∉Ck
l
1 − ∏ (1 − Ah )
h∈Cm
1
Aj =
− γ Zij
1+ e
IMPLICIT MODELING OF CHOICE SET
Implicit Availability and Perception model
(Cascetta and Papola 2001)
pij =
Availability function:
Aj e
µVij
J
µVik
A
e
∑ k
k =1
1
Aij =
−α Z
1+ e
IMPLICATIONS
Long history of concern over choice set
misspecification, but little done...
Applies to a large class of models / applications
Transportation
Food Choices (health risks?)
Housing Demand
Stated Preference Data Sets
SP Data with multiple alternatives, etc.
Marketing
Little theory or understanding of the impact of
misspecifed choice sets
Behavioral Econ – ”too much choice”?
DATA AND ESTIMATION
Data:
2 years, stated and revealed preference data
Attributes: cwd prevalence, tags, culling and travel
cost
11 sites (wildlife management units )
Demographics
Estimation
Utility function: alternative specific constants,
attributes and relevant interactions
Scale function: dummy for SP/RP data, time dummy
in exponential function
Availability function: cwd and its interaction with
time dummy, age, urban and hunting years
ESTIMATION CONTINUED
Examine probability of site choice, and choice set
formation, in random utility framework
Evaluate impact of CWD (and other features)
over time
Differences in utility, choice set formation, and scale
Examine welfare measures
Contribution from utility function
Contribution from choice set formation
MODELS
MNL model (utility function only)
MNL model with scale function
MNL model with scale and availability (CP)
RPL (random parameter logit) versions of the
models above
IAL model (fully endogenous choice set
formation) with scale
MNL model using a ”thresholds” specification of
the availability function
EXAMPLE OF CONTINGENT BEHAVIOUR / SP QUESTION
Do you feel CWD is a threat to human
health?
Do you feel CWD is a threat to wildlife?
I no longer consume deer meat
because of CWD
CWD has affected my enjoyment of
hunting deer
I eat or give away deer meat before I get
testing results back from Fish and Wildlife
RESULTS: ESTIMATED MODELS
Fixed parameter
models
Model
Random parameter
models
Loglikelihood
Rhosquared
Loglikelihood
Rhosquared
Base MNL
-7,583.41
0.275
-5,067.19
0.516
With scale
-7,500.26
0.283
-4,960.53
0.526
With scale
and
availability
-7,375.68
0.295
-4,937.84
0.528
RESULTS: FIXED PARAMETER MODEL
Utility function
Availability function
Travel cost
-23.2 (1.08)
CWD
0.627 (0.087) CWD
Tags
0.572 (0.105) CWD x year 2 -0.116 (0.054) Year2 x SP
Cull
-0.961 (0.129) Age
Tc x urban
11.1 (0.776)
Tags x urban
-0.265 (0.136) Hunting years
CWD x urban
-0.655 (0.083)
Cull x hunt
years
0.014 (0.005)
CWD x year 2 -0.054 (0.027)
Constant
Urban
4.59 (0.594)
Scale function
Year 2
-0.768 (0.062) SP
-0.305 (0.068)
-0.468 (0.045)
0.3 (0.09)
-0.077 (0.015)
10 (2.31)
0.12 (0.012)
Loglikelihood
Rho-square
-7,375.68
0.295
WELFARE CHANGE OF MOVING TO THE
WORST SCENARIO – CWD SPREAD
MNL
Base MNL
MNL with
scale
Year 1
Year 2
Rural
Urban
Rural
Urban
15.37
(3.75)
-4.24
(4.38)
-11.23
(3.66)
-40.67
(4.74)
15.00
(5.18)
-18.35
(4.73)
-23.07
(6.28)
-49.93
(15.78)
CP MNL
Year 1
Year 2
Rural
Urban
Rural
Urban
Utility function
248.49
(30.51)
-7.26
(3.41)
248.98
(0.63)
-28.45
(8.39)
Availability
factor
-81.41
(32.7)
-0.35
(1.03)
-116.05
(3.4)
-0.69
(2.82)
Total
68.33
(21.17)
-7.69
(2.71)
-38.36
(1.98)
-29.04
(8.52)
COMPARISON WITH THE IAL MODEL
(ENDOGENOUS CHOICE SETS)
Scale components similar
Utility components similar
But CWD has a negative effect for all hunters, in all
years.
Availability component – somewhat different
Urban residents do not consider all sites available
(although they still have high probabilities relative to
rural individuals)
CWD effect positive in year 1, negative year 2
interaction.
Welfare measures: TBD
RESULTS: IAL MODEL
Utility function
Availability function
Scale function
Travel cost
-59.608 (4.909) Constant
-0.068 (0.267) Year 2
-1.377 (0.074)
CWD
-0.148 (0.053) CWD
1.176 (0.364) SP
-0.782 (0.104)
Tags
1.929 (0.282) CWD x year 2
-0.747 (0.254) Year2 x SP
0.676 (0.113)
Cull
-2.48 (0.260) Age
-0.001 (0.008)
Tc x urban
26.472 (2.855) Urban
0.356 (0.186)
Tags x urban
-1.676 (0.345) Hunting years
-0.004 (0.007)
CWD x urban
-0.203 (0.110)
Cull x hunt
years
0.0455 (0.012)
CWD x year 2 -0.164 (0.066)
Loglikelihood
Rho-square
-7402.643
0.292
IAL MODEL
Implied Probabilities of Choice Set Size
# alternatives
Q (probability)
1 alt
0.00
2 alts
0.00
3 alts
0.01
4 alts
0.03
5 alts
0.08
6 alts
0.15
7 alts
0.21
8 alts
0.22
9 alts
0.18
10 alts
0.10
11 alts
0.03
MODEL 3: A ”THRESHOLDS” MODEL
Many suggestions surrounding specification of
choice formation
Hauser 2010 summary – ”thresholds” / heuristics
We now model availability as a function of
CWD threshold (presence / absence)
Travel cost threshold (above / below average)
Availability function
Constant
28.750 (17.228)
CWD Threshold
-27.949 (17.227)
CWD RP x year 2
-1.342 (0.366)
Travel Cost Threshold
-2.012
CWD SP x year 2
18.474
Utility function
CWD
0.139
Tags
0.779
Cull
-0.882
Travel Cost (TC)
-21.851
TC x urban
9.846
Tags x urban
-0.662
CWD x urban
-0.155
Cull x hunt years
0.020
CWD x year 2
-0.174
Scale function
-0.587
SP
-0.220
Year 2
0.187
Year 2 x SP
(0.264)
(13.537)
(0.027)
(0.117)
(0.139)
(0.993)
(0.747)
(0.137)
(0.023)
(0.005)
(0.033)
PARAMETERS OF A
MNL MODEL
EMPLOYING
“THRESHOLDS” IN
AVAILABILITY
(0.042)
(0.068)
(0.080)
Note: coefficients in italics are NOT significant at 10%. Standard errors are in parentheses.
Welfare Measures – from the “Thresholds”
Model (with availability and scale)
Year 1
Utility
Availability
Total
Year 2
Rural
Urban
Rural
Urban
46.82
(9.86)
-1.76
(5.73)
-27.5
(3.52)
-60.27
(22.24)
-8.38
(4.06)
-24.51
(4.00)
-32.85
(7.19)
-83.45
(13.75)
39.96
(12.92)
-25.07
(7.67)
-40.07
(3.64)
-163.62
(18.87)
Note: Welfare change $/trip of moving to the worst case scenario. Standard deviations are in parentheses.
CONCLUSION
Using the CP model, CWD is found to have an
effect on choice set formation
The negative effect of CWD on choice set
formation increases over time
Time and habit effects? (similar to BSE research)
However, the impact of results are sensitive to
specification and model type
Is the CP approach a tractable choice set
formation model?
LIMITATIONS AND EXTENSIONS
Limitations:
Complex behaviors, observed and unobserved
heterogeneity
Small sample with possible selection bias
Next Steps
Checks on robustness of IAL model
Endogeneity of CWD?
Simulation analysis
Extensions / Future Research:
A Theory for Choice Sets?
Kreps – “options” (1978) or Sarver – “regret” (2008)
Choice sets versus “cutoffs”?
Welfare analysis?
FUNDING SOURCES
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