T HE M ICRO F OUNDATIONS OF M ACRO S ORTING M ODELS Timothy L. Hamilton University of Richmond Daniel J. Phaneuf University of Wisconsin October 22, 2012
I NTRODUCTION – S ORTING M ODELS FOR N ON -M ARKET V ALUATION Households sort a la Tiebout to optimal residential location: Choice reveals tradeoffs between prices and attributes of locations Use to quantify preferences for local public goods Examples: Bayer et al. (2009) – particulate matter pollution Klaiber and Phaneuf (2010) – open space Tra et al. (2012) – school quality Tra (2012) – ozone pollution Many apparent advantages vis-à- vis first stage hedonic modeling…
A SSUMPTION H EAVY M ODELING E NVIRONMENT Need assertions on: Spatial extent of analysis → “macro” choice level vs. “micro” choice level → Bayer et al. ‘macro’ – country-wide choice → Klaiber and Phaneuf ‘micro’ – city-wide choice Definition of a choice element Functional form for utility and error distributions Nature/form of equilibrium conditions Important element of research agenda is examining extent to which advantages are assumption-driven …
C HOICE E LEMENTS AND S PATIAL S CALE Seems that most location choices are two- tiered… Choose region/city based on labor market, regional amenities, family roots… Choose neighborhoo d based on local amenities, schools, commute patterns… Choices are distinct – but interrelated? Complement/substitute relationship between regional and local public goods? e.g. does regional air quality have higher value if local landscape provides more outdoor opportunities?
R ESEARCH Q UESTIONS How do estimates of the non-market value of air quality depend on the interconnectedness between macro and micro sorting margins? → revisit Bayer et al. (2009) macro -sorting application to regionally varying air pollution → examine more general model that nests their specification while adding micro margin How can we tractably model the multiple sorting decision margins? → examine ‘two stage budgeting’ assumptions as applied to ‘two stage sorting’ → develop sequential estimation approach to accommodating both margins
F INDINGS /C ONTRIBUTIONS Consideration of micro sorting margin matters empirically: Elasticity of WTP with respect to air quality 0.31 (macro only) vs. 0.48 (macro/micro) Marginal WTP for air quality $232 vs. $371 Difference due to an implicit omitted variable in macro only model Operationalize sequential estimation of two stage budgeting/two stage sorting model Micro-level choices aggregated to a “quality adjusted price index” summarizing neighborhood level choice sets Connect practical use of nested logit model to two stage budgeting concept
O UTLINE OF T ALK 1) Introduction 2) Conceptual Basis 3) Empirical Basis 4) Application and Data 5) Estimation/Results 6) Conclusions We are working on finalizing paper for submission – what is still needed? Where should it go? Contribution well-framed?
C ONCEPTUAL B ASIS max exp( ) U C Y H X C Y H X ijm m jm jm m ijm (1) , C H . . s t C p H I jm im C : numeraire consumption H : consumption of ‘housing services’ Y m , m : regionally (MSA) varying public goods X jm , jm : neighborhood public goods (deviations from MSA averages) I im : income in MSA m ijm : idiosyncratic preference shock p jm : price of housing unit in neighborhood j , MSA m ln p jm = ln m + ln jm ↔ p jm = m × jm
Conditional indirect utility for person i , neighborhood j , MSA m : ln ln ln ln ln ln V I Y X ijm I im Y m X jm H m jm (2) , 1,..., 1,..., j J m M jm m ijm m Note: I = C + H Literature-standard additively separable form jm =1, X jm =1, J m =1, jm =0 → collapses to Bayer et al. model
T WO S TAGE B UDGETING A restriction on preferences implying: Consumer first determines expenditures on commodity groups – e.g. food, housing, clothing – conditional on income and commodity group price indices Consumer subsequently allocates commodity group expenditures among individual products – e.g. food expenditures spent on steak, beer, pizza, … Empirically convenient restriction often used in demand system estimation
P ROPOSITION ‘Macro’ stage sorting involves income allocation to broad non- housing ( C ) and housing ( Q ) consumption groups ‘Micro’ stage sorting involve s allocation of Q expenditures to house structure ( H ) and local public goods ( X ) Utility function (1) satisfies conditions for this division Proof in paper – relies on establishing ‘price aggregation’ and ‘decentralisability’ (Blackorby and Russell, 1997)
T WO S TAGE S ORTING M ODEL Consistency of (1) with two-stage budgeting allows us to write (2) as: i ln ln ln ln , 1,..., V I Y j M im I im Y m H m m m im where i max{ ln ln } X | m H jm X jm jm i j m j J m | ijm im ij m is a quality-adjust price ( or utility ) index for the second stage of i m sorting
E MPIRICAL B ASIS Start with k k ln ln ln ln ln ln V I Y X ijm I im Y m X jm H m jm jm m ijm 1,..., 1,..., j J m M m Assume GEV distribution for ,..., ,..., ,..., . 11 1, 21 2 1 ,..., i i iJ i iJ i M iJ M 1 2 M ‘Nested Logit’ s pecification: There are M ‘nests’ corresponding to MSAs There are J m alternatives in each nest corresponding to neighborhood within the MSA Household type specific heterogeneity ( k =1,…, K )
P ROPERTIES OF N ESTED L OGIT M ODEL Probability of observing ( m , j ) = Pr ijm =Pr ij | m × Pr im : k k exp ln ln ln I Y IV I im Y m H m m m Pr im M k k exp ln ln ln I Y IV I in Y n H n n n 1 n k k k k exp ln / X exp H jm X jm jm jm Pr , | ij m J J k k k k m m exp ln / exp X H jl X lm l m lm 1 1 l l J m k k i ln exp ( ) I V E m jm m 1 j k k k max{ ln ln } E X | H jm X jm jm ij m m j J m
T WO S TAGE B UDGETING /T WO -S TAGE SORTING /N ESTED LOGIT PUNCH L INE Literature-standard functional form provides useful structure for sequential estimation Use micro-sorting data to estimate inclusive value for lower nest ↔ (expectation of) price index in first stage budget allocation Estimate ‘dissimilarity’ coefficient k via macro-choice conditional logit model ↔ reflects degree of importance of micro-choice set in macro decisions Links upper and lower levels of nested logit to stages of budgeting (though two stage budgeting holds for any error distribution)
A PPLICATION AND D ATA Empirical objective follows Bayer et al (2009): Measure marginal WTP for regionally-varying air pollution (PM 10 ) Estimate a macro sorting model across 226 MSAs in continental US Data needs: Neighborhood level residential locations – Census Data Research Center (confidential) MSA level residential location – IPUMS (public use census micro data) PM 10 emissions – EPA National Emissions Inventory (converted to concentrations using source/receptor matrix) Other MSA level variables – various sources
C ENSUS D ATA Confidential micro data: 8.5 million people 1990 and 7.6 million 2000 Observe 23 to 40 year olds locating in 40,416 census tracts Divide out by household types Public use micro data (IPUMS): 39,058 1990 and 37,165 2000 23 – 40 year olds sorting across 226 MSAs Observe income, education, household makeup, etc. Use IPUMS data to predict MSA-level housing prices and (potential) household income at all M locations
H OUSEHOLD T YPES Type Definition (presence of children and education) Type 1 No children in household, No high school degree Type 2 No children in household, High school degree or some college Type 3 No children in household, Bachelor's degree Type 4 No children in household, Graduate or professional degree Type 5 Children in household, No high school degree Type 6 Children in household, High school degree or some college Type 7 Children in household, Bachelor's degree Type 8 Children in household, Graduate or professional degree
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