Abstract
We estimate a hedonic-pricing model using geo-coded farmland-transaction data from the Campine region, situated in the north-east of Belgium. Unlike previous hedonic studies, we use the method of unconditional quantile regression (Firpo et al., in Econometrica 77(3):953–973, 2009). An important advantage of this new method over the traditional conditional quantile regression (Koenker and Bassett, in Econometrica 46(1):33–50, 1978) is that it allows for the estimation of potentially heterogeneous effects of cadmium pollution along the entire (unconditional) distribution of farmland prices. Using a threshold specification of the hedonic-pricing model, we find evidence of a U-shaped valuation pattern, where cadmium pollution of the soil has a negative and significant impact on prices only in the middle range of the distribution, insofar as cadmium concentrations are above the regulatory standard of 2 parts per million for agricultural land. Results obtained from a probit model to classify land plots into different price segments further suggest that the heterogeneous impact of soil pollution on price can be directly related to the variety of amenities that farmland provides.
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Notes
Synthesized information (in Dutch) on the Cadmium Action Plan and the BeNeKempen project is online available at http://www.milieurapport.be/Upload/main/miradata/MIRA-T/02_themas/02_15/Synthesetekst_MiraT2006-08Def.pdf (MIRA, Milieurapport Vlaanderen/Flanders Environmental Report).
Cadmium has been identified as the trace element with the highest bio-accumulation index in green plants, causing severe health risks (e.g., kidney damage, bone decalcification, and cancer). As a result of that, farmers are not allowed to grow crops/vegetables for human consumption on heavily contaminated land.
To verify if farmers are compliant with existing food regulations, the Federal Agency for the Safety of the Food Chain (FASFC), an executive body with jurisdiction over the entire Belgian territory, collects a large number of food samplings and performs different kinds of controls and inspections. To enforce compliance with the law, non-compliance is penalized, and transgressors even risk legal prosecution. OVAM takes action only in the case of land that is directly in danger; i.e., land that is potentially hazardous due to former polluting activities on-site.
The average (Google-Maps) distances between the 14 municipalities in our study area and the cities of Brussels and Antwerp are 94.7 km (min = 68.1, max = 117.0) and 71.5 km (min = 56.0, max = 90.9), respectively.
CQR has been well documented elsewhere (Koenker and Bassett 1978; Koenker and Hallock 2001). Therefore, it will not be further discussed here. An example of the application of CQR to the hedonic valuation of farmland characteristics is Uematsu et al. (2013). Their study is closely linked to ours through its focus on the contribution of natural-amenity attributes to the price of farmland.
This property does not hold for CQR, for the simple reason that observations, say, at the top of a conditional distribution may be at the bottom of the unconditional distribution.
In the present study, sales transactions are only those transfers of farmland where a landowner sells a plot of land to a buyer at an agreed price. Transactions in the rental market have been excluded from our analysis, since rental prices are regulated by the Flemish government; that is, they are not allowed to exceed a legal maximum level, where the latter is below the market price. Moreover, there is legislation to protect the tenant (e.g., in the form of long-term contracts), and the tenant has a pre-emptive right to buy the tenanted land if it is for sale.
The GIS files are polygons of plot boundaries. Given the generally small size of the farmland plots in our sample (see summary statistics in Table 1 below), our geo-referenced variables are expected to be quite robust.
In Sect. 5.3 we compare the performance of the baseline model specification with some other, more commonly-used specifications.
These covariates have been included as control variables, and are primarily aimed at helping the identification of the Cd parameter of interest. So the coefficients on the former do not necessarily have a “causal” interpretation.
Evidently, built structures vary tremendously in quality, size, age, etc. Unfortunately, our data set contains only information about the presence or otherwise of built structures.
One could, of course, argue that the choice of the 1-km distance is arbitrary, but we consider this radius as reasonable, given the “peculiar” landscape features of our study area. If we had chosen, say, a larger distance, the local nature of the urban-development pressure might have been lost. Also, the use of distance-buffer variables is not uncommon in the literature. For instance, Alberini (2007) used a variable defined as the percentage of land slated for residential use within 1500 m of the parcel.
Specifically, we found that the correlation between the time-series variation of the average real prices of developable land (averaged over the 14 municipalities of the study area) and the estimated year dummies in our baseline hedonic-pricing model is equal to 0.96.
Our choice of the length of the time period is partly motivated by the modest size of our data set. We choose a 12-month time window, which implies that we lose the first 64 observations (11 % of the original sample). If we had chosen 24 months, we would have already lost 160 observations (27 % of the original sample).
The Euclidian distances (in km) between the farmland plots in our sample (the elements in the distance matrix D) have been calculated on the basis of the so-called Lambert (x, y) coordinates. The mean (median) distance between the farmland plots is 15.3 km (14.3 km). The minimum distance is only 9 m, while the maximum distance is 49.6 km. The largest minimum distance is 4.1 km (i.e., there is one plot that is located at 4.1 km from its nearest neighbor), while the smallest maximum distance is 25.7 km (i.e., there is one plot that is located within a 25.7 km distance of every other plot).
It should be noted, in passing, that the UQR estimate (for the median of the price distribution) is two and four times larger in absolute size than its CQR (for the median) and OLS (for the mean) counterparts, respectively.
To obtain the full covariance matrix of the estimated coefficients, necessary to implement the Wald-type F test, we had to perform a prior bootstrap estimation (based on 500 replications).
For example, although the quantile estimate at the 80th percentile \((\hat{\beta }_{{0.80}} =-{0.236})\) lies outside the 9. 5 % CI of the estimate at the median \((\hat{\beta }_{0.50} =-{1.381})\), as can be seen from Fig. 3, the null hypothesis of their equality could not be rejected at conventional levels of significance \(\left( \hbox {F}_{\hat{\beta }_{{0.80}} -\hat{\beta }_{{0.50}}} =1.38,~p={0.241}\right) \).
It is important to note that a probit analysis as conducted here is meaningful only in the context of UQR (thus not for CQR), as it provides useful information on the observable association between the characteristics of the land plots in the sample population and their position in the unconditional price distribution.
While being an intriguing issue, any further investigation of it to make stronger claims is beyond the scope of the present paper, as our data set contains no information on the buyers’ identity and/or personal characteristics and preferences as, for example, in Kostov (2010) and Curtiss et al. (2013).
The OLS estimate of the coefficient on the public-sales dummy is 0.209 (see column 1 of Table 2). This means that, on average, the public-sales price is estimated to be about 23.2 % \(=\left( {e^{0.209}-1}\right) \times 100\) higher than the private-sales price, or the price stated to the government (net of the side payment) in the case of private sales is, on average, about 18.8 % lower than the actual (full) transaction price. This percentage is very close to the 20 % mentioned in Ciaian et al. (2012, p. 8).
It should be noted that the quantile effect of public sales rebounds to a high level of 0.83 % at the 95th quantile (not shown in panel a of Fig. 4) after the unexpectedly low value of 0.21 % at the 90th percentile of the price distribution.
Municipal-level data on average prices of developable land and areas of cultivated land were available from the Flemish portal of local statistics, http://aps.vlaanderen.be/lokaal/lokale_statistieken.htm.
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Acknowledgments
The authors thank the co-editor, Phoebe Koundouri, and two anonymous reviewers of this journal for their valuable comments and suggestions on earlier versions of the paper. The first author is also grateful to Yves Surry for sharing his views on issues related to quantile regression at an early stage of the paper.
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Appendices
Appendix 1: Differences Between CQR and UQR—Illustrative Simulation Example
This appendix presents a simple simulation example (borrowed with some modifications) from McMillen (2013) to illustrate the differences between traditional CQR and new UQR, and to point to potential problems that may arise when interpreting the estimates returned by CQR.
Consider a single explanatory variable, X, which is limited to take integer values from 1 to 10. Each integer value occurs 200 times in the simulated data set, leading to a total of 2000 observations. The regression equation is specified as \({Y}=10-{0.5X}+\varepsilon .\) To ensure an \(R^{2}\) of approximately 0.8 for the OLS (mean) regression, we specify \(\varepsilon \sim \hbox {N}\left[ {0,\sigma _\varepsilon \left( {X}\right) } \right] ,\) where \(\upsigma _{\varepsilon }^{2}\left( {X}\right) = \frac{0.2\sigma _{X}^{2}}{{X}}.\) This variance function for \(\varepsilon \) implies that the quantiles of the conditional distribution of Y given X converge; that is, the dispersion (variance) of the conditional distribution of Y decreases with higher values of X.
The results from OLS, CQR, and UQR are summarized in Table 6. Selected CQR regression lines, representing the 10th, 50th, and 90th percentiles of the conditional distribution of Y given X, are shown in Fig. 6. The OLS regression line represents the conditional mean of Y.
The points a and b in Fig. 6 show why standard CQR results may be misinterpreted. Point a is associated with a high value of X on the 90th-percentile regression line, whereas point b represents a low value of X on the 10th-percentile regression line. The value of the dependent variable Y at point a is lower than its value at point b, where the former is positioned at the bottom end of the unconditional distribution of Y. Therefore, it is not the case that an increase in X leads to a greater decline in Y whenever Y is unconditionally high. The steeper slope at the 90th percentile merely indicates that an increasing X leads to greater declines in Y along the 90th percentile of Y than at its 10th percentile, conditional on the values of X.
Another way to illustrate the differences between the estimated effects of X on Y using either CQR or UQR is to look at the quantile plots presented in Fig. 7. Specifically, they show the CQR and UQR estimates (along with their 95 % confidence bands) of the effects of X at nine different quantiles (from the 10th to 90th percentile). It can immediately be seen that the estimated effect obtained using UQR is highly non-monotonic, exhibiting a pronounced U-shaped pattern, whereas the effect obtained using standard CQR declines monotonically. It is interesting to see that the pattern displayed by the quantile coefficients obtained using UQR is close to a “mirror image” of the inverse U-shaped pattern shown in FFL (2009, their Fig. 1, p. 965).
The quantile coefficients obtained using CQR are the estimated slopes of the regression lines in Fig. 6, which show how the quantiles of the conditional distribution of Y given X are affected by a 1-unit change in X. Thus, CQR and UQR estimate two different things, where CQR focuses on the unobserved heterogeneity of Y reflected by the distribution of Y for a given value of X, \(\hbox {F(Y|X)}=\hbox {F}\left( \varepsilon \right) \), while UQR centers on the observed distribution of Y for the entire population, \(\hbox {F}\left( {Y}\right) \). Yet it is curious to see that in many empirical applications of CQR, results are often erroneously interpreted as if they were UQR results.
Appendix 2: Within- and Between-Municipality Covariances among Farmland Prices
This appendix provides simple descriptive measures of the covariance (or correlation) patterns among observed prices as a function of the distances between the farmland plots.
Following Barrios et al. (2012), we calculated the within- and between-municipality covariances for pairs of prices of farmland plots whose (straight-line) distance in km is within some bandwidth h of a given distance d; that is,
and
where \(\tilde{p}_{i}\), \(\tilde{p}_{j}\) are the “demeaned” sales prices (measured as deviations from the overall sample mean). The symbols \(m_{i}\) and \(m_{j}\) denote the municipalities in which the plots i and j are located. Specifically, \(m_{i}=m_{j}\) \((m_{i}\ne m_{j})\) means that farmland plots i and j are (not) located in the same municipality. Note that all farmland plots have been ordered, and the condition \(i<j\) just takes account of the symmetry of the variance-covariance matrix.
The panels in Fig. 8 show the covariance functions for bandwidth h going from 1 to 4 or the within- and between-municipality covariances. For example, with bandwidth \(h=1\), we look at the prices of all plots j located at a distance between 0 and 2 km from plot i for \(d=1\), between 1 and 3 km for \(d=2\), between 2 and 4 km for \(d=3\), and so on.
The main conclusions from the graphs presented in Fig. 8 are that the covariances decrease with distance, and that the between-municipality covariances are of a magnitude much smaller than the within-municipality covariances. Therefore, the results provide some empirical support for (i) the importance of using simple inverse distances, and (ii) the land-market segmentation along municipal boundaries. In a certain way, the latter can be interpreted as a manifestation of “home biases” along municipal boundaries, due to higher transaction or information-search costs associated with the prices prevailing “on the other side of the fence”. Admittedly, this is just our conjecture, which has not been further tested here. Based on the findings from the covariance analysis, our empirical application in the main text uses only the within-municipality prices of farmland in constructing the spatiotemporal lag of the dependent price variable.
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Peeters, L., Schreurs, E. & Van Passel, S. Heterogeneous Impact of Soil Contamination on Farmland Prices in the Belgian Campine Region: Evidence from Unconditional Quantile Regressions. Environ Resource Econ 66, 135–168 (2017). https://doi.org/10.1007/s10640-015-9945-6
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DOI: https://doi.org/10.1007/s10640-015-9945-6