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Estimating the Economic Value of Beach Nourishment

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Convergent Validity of Revealed and Stated Recreation Behavior with Quality ... Experimental WTP: List and Gallet, ERE, 2001. Experimental WTP: Murphy et al. ERE, 2005 ... – PowerPoint PPT presentation

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Title: Estimating the Economic Value of Beach Nourishment


1
Estimating the Economic Value of Beach Nourishment
  • John Whitehead, ASU Dan Phaneuf, NCSU Chris
    Dumas, UNCW Jim Herstine, UNCW Jeff Hill, UNCW
    Bob Beurger, UNCW

2
Convergent Validity of Revealed and Stated
Recreation Behavior with Quality Change A
Comparison of Multiple and Single Site Demands
  • John Whitehead, ASU Dan Phaneuf, NCSU Chris
    Dumas, UNCW Jim Herstine, UNCW Jeff Hill, UNCW
    Bob Beurger, UNCW

3
Beach Nourishment
4
(No Transcript)
5
NC Beach Nourishment 1961-2006
  • Annual costs 4.37 million (2004 )
  • Annual cost of nourishing all 138 miles 831
    million
  • The number of NC beaches annually nourished
    ranges from one to seven (a small fraction of
    total beaches)

6
Market for Beach Width?
Price
S
D
Beach Width
7
Implicit Market Travel cost method
Travel cost
D
D
Trips
8
Construct Validity
  • The degree to which inferences can be made from
    the measures of a theoretical construct to the
    theoretical construct

9
Construct validity tests
  • Length of stay Loomis, ERE, 1993
  • Site selection Grijalva, Berrens, Bohara and
    Shaw, AJAE, 2002
  • Hurricane evacuation Whitehead, ERE, 2005

10
Convergent validity
  • The degree to which a measure is similar to other
    measures for which it should also be similar.

Revealed Preference
Stated Preference
11
Convergent validity tests
  • WTP and implicit market values Carson et al.,
    Land Econ, 1996
  • RP and SP number of trips Jeon and Herriges,
    working paper, 2005

12
Hypothetical bias
  • Experimental WTP List and Gallet, ERE, 2001
  • Experimental WTP Murphy et al. ERE, 2005
  • Whitehead et al., JES, forthcoming

13
A comparison of three TCM models over ?CS and ?x
  • Single-site RP and SP model
  • Linked multiple-site RP site-selection and trip
    frequency model
  • Kuhn-Tucker RP seasonal demand system

14
Issues
  • Single-site models are less capable of
    incorporating substitutes
  • RP data may not be able to forecast accurately
    beyond the range of historical experience
  • SP data is subject to hypothetical bias

15
Current Application NC Beaches
16
Model 1 Single Site Model
Travel cost
D RP, SP D SP
D
D
Trips X Sxj
17
Model 1 Welfare
  • lnµit b0 b1p b2p b3y b4q
  • b5SP ui eit
  • CS per trip SP0 -x(q) x(qo)/b1
  • CS CS per trip X DX

18
Model 2 Linked Model
  • Step 1 Discrete choice site selection model

19
Step 1 Nested Logit
20
Nested Logit details
21
Step 2 Linked Model
  • Negative binomial trip frequency model

X(IV,y,z)
IV(q)
Trips X Sxi
22
Linked Model Welfare
  • WTP per trip -IV(q) IV(qo)/d
  • WTP WTP per trip X DX

23
Model 3 Kuhn-Tucker Model
Travel costj
Dj RP Dj RP
Dj
Dj
Trips xj
24
via Maximum Likelihood
25
Kuhn-Tucker Model Welfare
  • Welfare analysis and demand prediction in the KT
    model relies on Monte Carlo integration in which
    the unobserved heterogeneity (error) terms are
    drawn conditionally so that behavior at baseline
    travel cost and site conditions is replicated in
    the simulated outcomes. Given multiple simulated
    error vectors for each person compensating
    surplus is calculated for each error draw, and
    the average over people and draws provides an
    estimate of E(CS)
  • See appendix and references for details

26
Data
  • 2003 Survey
  • n 1000 beach goers
  • n 800 with complete RP data
  • n 600 with complete SP data
  • n 351 with X Sxj
  • Single and multi-day trips

27
Sxj -X
Probit for sample selection Probit for sample selection
Variable t-value
Intercept 0.25
house 0.34
children 0.84
married 1.28
male 0.35
white -0.94
age 1.28
educ -0.12
income2 -0.98
  • Mean 2.24 (n 535)
  • STD 21.52
  • Quantiles
  • 100 260
  • 95 10
  • 90 3
  • 10 -1
  • 5 -3
  • 0 -98

28
Single Site Trips
RP last year 10.06
SP status quo 11.93
SP trips with improved access 15.41
SP trips with increased width 12.85
29
Multiple-Site Data
Beach Trips () Width Access Park Length
Fort Macon 4.56 90 2 602 1.40
Atlantic Beach 21.08 135 19 662 4.90
Pine Knoll Shores 0.85 110 6 195 4.80
Indian Beach / S.P. 1.14 90 2 131 2.50
Emerald Isle 11.11 130 69 550 11.50
North Topsail Beach 3.42 82 42 929 9.70
Surf City 5.7 90 36 272 5.10
Topsail Beach 1.99 110 37 234 4.00
Wrightsville Beach 24.22 160 45 1479 4.50
Carolina Beach 7.98 185 26 452 2.00
Kure Beach 2.56 130 20 223 2.80
Fort Fisher 1.14 400 2 240 1.90
Caswell Beach 0.28 80 12 103 2.80
Oak Island 2.28 120 66 821 7.50
Holden Beach 3.7 90 21 200 6.80
Ocean Isle Beach 6.55 85 28 341 5.30
Sunset Beach 1.42 115 34 260 1.20
30
Travel cost
  • Single Site minimum distance TC 94
  • Outer banks TC 203
  • Mean multiple site TC 125 (n 17 351
    5967)

31
Single Site Models
SP Random Effects Poisson SP Random Effects Poisson RP-SP Random Effects Poisson RP-SP Random Effects Poisson
Coeff. t-ratio Coeff. t-ratio
Constant 2.278 14.09 2.077 13.37
Own travel cost -0.011 -11.28 -0.011 -11.07
Substitute travel cost 0.004 4.13 0.004 4.14
Income 0.010 4.10 0.011 4.40
Married -0.549 -4.61 -0.526 -4.40
Stated preference 0.171 8.87
Access improvement 0.256 16.69 0.256 15.97
Increase in beach width 0.074 2.58 0.074 2.56
a 0.986 10.48 0.952 10.396
Cases 351 351 351 351
Periods 3 3 4 4
32
Linked Model
Nested Logit Site Selection Nested Logit Site Selection Nested Logit Site Selection Negative Binomial Trip Frequency Negative Binomial Trip Frequency Negative Binomial Trip Frequency
Coeff. t-ratio Coeff. t-ratio
Travel cost -0.100 -25.91 Constant 2.321 16.90
Beach width 0.003 8.35 Income 0.019 6.60
Access areas 0.003 1.94 Married -0.424 -2.82
Parking spaces 0.001 17.85 Log sum 0.117 10.02
Beach length 0.020 1.94 Alpha 1.053 13.20
Inclusive Value 0.673 21.34
Sample size 5967 351
33
Kuhn-Tucker Model
Model 1 Model 1 Model 2 Model 2 Model 3 Model 3
Coeff. t-ratio Coeff. t-ratio Coeff. t-ratio
Intercept -2.720 -1.17 Fixed Effects Fixed Effects Fixed Effects Fixed Effects
Married -0.028 -0.13 -0.033 -0.14 -0.034 -0.14
Translating 2.087 16.00 1.442 6.48 1.599 8.05
Access -0.004 -1.48 -0.002 -0.33 -0.007 -2.21
Length 0.011 0.71 -0.040 -1.19
Parking 0.001 10.52 0.000 1.38 0.000 1.98
Beach Width 0.001 1.55 0.002 2.06 0.003 2.71
Income -0.609 -1.52 -0.611 -1.41 -0.609 -1.40
ln(u) -0.284 -5.18 -0.195 -3.32 -0.194 -3.30
Fixed effects NO NO YES YES YES YES
34
Convergent Validity
Multiple Site Multiple Site Single Site Single Site
Linked K-T SP RP-SP
?X 1.03 1.10 1.08 1.08
WTP, CS per trip 2.93 14.44 6.59 6.53
X 11.09 11.16 11.14 11.14
X WTP, CS per trip 32.49 164.65 73.41 72.74
35
Policy Implications Benefits
  • 1.58m households in the study region
  • 64 participants
  • Aggregate benefit 772 million
  • The annual recreation benefit of increased width
    60 million

36
Policy Implications Costs
  • The annual cost to replace one foot of eroded
    beach 32,000 per mile
  • 60 miles
  • 100 feet
  • Every 4 years
  • Annual cost 48,000,000

37
Net benefits
  • NB 60m 48m
  • NB lt 0 in linked model
  • Property benefits are not included
  • Environmental costs are not included

38
Conclusions
  • Single-site and multi-site models are
    statistically convergent valid for quality change
    not economically convergent valid
  • Hypothetical bias can be adjusted with SP 0
  • Joint estimation of RP and SP is not needed in
    this application
  • RP data is able to forecast beyond the range of
    historical experience

39
Additional Research
  • Compare CS and WTP per trip
  • Is it hypothetical bias?
  • Consider those with mismatched trips
  • Consider sample selection effects
  • Compare with other multiple site models (e.g.,
    participation model)
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