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Multilevel (Hierarchical) Modeling: What It Can and Cannot Do

Multilevel (Hierarchical) modeling : What It Can and Cannot Do Andrew G ELMAN. Department of Statistics and Department of Political Science Columbia University New York, NY 10027. ). Multilevel (hierarchical) modeling is a generalization of linear and generalized linear modeling in which regression coefficients are themselves given a model, whose parameters are also estimated from data. We illustrate the strengths and limitations of Multilevel modeling through an example of the prediction of home radon levels in counties. The Multilevel model is highly effective for predictions at both levels of the model, but could easily be misinterpreted for causal inference.

Multilevel (hierarchical) modeling is a generalization of linear and generalized linear modeling in which regression coefÞcients are themselves given a model, whose parameters are also estimated from data. We illustrate the strengths and limitations of multilevel modeling through an example of the prediction of home radon levels in U.S. counties.

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Transcription of Multilevel (Hierarchical) Modeling: What It Can and Cannot Do

1 Multilevel (Hierarchical) modeling : What It Can and Cannot Do Andrew G ELMAN. Department of Statistics and Department of Political Science Columbia University New York, NY 10027. ). Multilevel (hierarchical) modeling is a generalization of linear and generalized linear modeling in which regression coefficients are themselves given a model, whose parameters are also estimated from data. We illustrate the strengths and limitations of Multilevel modeling through an example of the prediction of home radon levels in counties. The Multilevel model is highly effective for predictions at both levels of the model, but could easily be misinterpreted for causal inference.

2 KEY WORDS: Contextual effects; Hierarchical model; Multilevel regression. 1. INTRODUCTION comes from underground and can enter more easily when a house is built into the ground.) We also had an important Multilevel modeling is a generalization of regression meth- county-level predictor a measurement of soil uranium that ods, and as such can be used for a variety of purposes, including was available at the county level. We fit a model of the form prediction, data reduction, and causal inference from experi- ments and observational studies (for recent reviews, see Kreft yij N( j + xij , y2 ), for i = 1.

3 , nj , j = 1, .. , J, and De Leeuw 1998; Snijders and Bosker 1999; Raudenbush (1). and Bryk 2002; Hox 2002). Compared with classical regres- j N( 0 + 1 uj , 2 ), for j = 1, .. , J, sion, Multilevel modeling is almost always an improvement, but to varying degrees; for prediction Multilevel modeling can where yij is the logarithm of the radon measurement in house i be essential, for data reduction it can be useful, and for causal within county j, xij is an indicator for whether the measure- inference it can be helpful. ment was taken in a basement, and uj is the log uranium level We illustrate the strengths and limitations of Multilevel mod- in county j.

4 The errors with variance y2 in the first line of (1). eling through an example of the prediction of home radon levels represent within-county variation, which in this case includes in counties. measurement error, natural variation in radon levels within a house over time, and variation between houses (beyond what 2. Multilevel modeling FOR ESTIMATING is explained by the basement indicator). The errors with vari- HOME RADON LEVELS ance 2 in the second line represent variation between counties beyond what is explained by the county-level uranium predic- Background and Model tor.

5 The hierarchical model allows us to fit a regression model Radon is a carcinogen a naturally occurring radioactive gas to the individual measurements while accounting for systematic whose decay products are also radioactive known to cause unexplained variation among the 3,000 counties. lung cancer in high concentrations and estimated to cause Equivalently, the model can be written as a single-level re- several thousand lung cancer deaths per year in the United gression with correlated errors States. The distribution of radon levels in homes varies greatly, with some houses having dangerously high concentra- y N( 0 1 + 1 Gu + x, y2 I + 2 GGT ), tions.

6 To identify areas of high radon exposure, the Environ- where G is the n J matrix of county indicators. mental Protection Agency coordinated radon measurements in The model can be expanded in many ways, most naturally a random sample of more than 80,000 houses throughout the by adding more predictors at the individual and county lev- country. els and by allowing the slope and the intercept to vary To simplify the problem somewhat, our goal in analyzing by county. For the purposes of this article, however, model these data was to estimate the distribution of radon levels in each of the approximately 3,000 counties, so that home- (1) is general enough.

7 We further simplify by focusing on a owners could make decisions about measuring or remediating subset of our data the 919 houses from the state radon sur- the radon in their houses based on the best available knowledge vey of the 85 counties of Minnesota (Price, Nero, and Gelman of local conditions. For the purpose of this analysis, the data 1996). We fit the model using hierarchical Bayes methods ( , were structured hierarchically: houses within counties. (If we Gelman, Carlin, Stern, and Rubin 2003). The posterior density were to analyze multiple measurements within houses, then there would be a three-level hierarchy of measurements, houses, 2006 American Statistical Association and and counties.)

8 The American Society for Quality In performing the analysis, we had an important predictor TECHNOMETRICS, AUGUST 2006, VOL. 48, NO. 3. whether the measurement was taken in a basement. (Radon DOI 432. Multilevel (HIERARCHICAL) modeling 433. is simply, p( , , , y , |y, x, u). nj . J . J. N( yij | j + xij , j2 ) N( j | 0 + 1 uj , 2 ), (2). j=1 i=1 j=1. where N( |M, S2 ) represents the normal density function with mean M and standard deviation S and assuming a uniform prior distribution on , y , and , which is reasonable given that the number of counties, J, is large (Gelman 2006).)

9 Data Reduction: Estimating Associations Figure 1 displays the estimated Multilevel model for a selec- Figure 2. Estimated County Coefficients j ( 1 standard error) Plot- tion of 8 of the 85 counties in Minnesota, along with the com- ted versus County-Level Log Uranium Measurement uj , Along With the pletely pooled and unpooled regression line for each county. Estimated Multilevel Regression Line = 0 + 1 u. The county coef- ficients roughly follow the line but not exactly; the deviation of the co- (The completely pooled line is y = + x, with a common line efficients from the line is captured in , the standard deviation of the for all counties, and the unpooled lines are y = j + x, with errors in the county-level regression.)

10 The 85 j 's estimated by least squares.). Compared with the two classical estimates (no pooling and complete pooling), the inferences from the Multilevel models to estimate this second-level relation using classical regression, are more reasonable. At one extreme, the complete-pooling first fitting the no-pooling model to estimate the j 's and then method gives identical estimates for all counties, which is par- fitting county-level regression to the j 's. The Multilevel model ticularly inappropriate for this application, whose goal is to has the appeal of fitting the two levels together and actually can identify the locations in which residents are at high risk of be implemented using a Gibbs sampler alternating between the radon.


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