| Literature DB >> 31861055 |
Abstract
This paper describes a study of the relationship between undesired road traffic externalities and residential price values in the Spanish city of Madrid. A large database was gathered, including the price and characteristics of 21,634 flats and road traffic intensity at 3904 different points across the city. The results obtained by a hedonic model suggest that both distance from the traffic measurement point and average daily traffic are significantly related to the price of residential properties, even after controlling for structural and neighbourhood variables. Distance to traffic areas has a positive impact on dwelling prices, whilst these are negatively related to traffic intensity.Entities:
Keywords: hedonic model; residential price; road traffic; traffic externalities
Mesh:
Year: 2019 PMID: 31861055 PMCID: PMC6950656 DOI: 10.3390/ijerph16245149
Source DB: PubMed Journal: Int J Environ Res Public Health ISSN: 1660-4601 Impact factor: 3.390
Summary of papers that investigate external costs of traffic.
| Paper | Quantitative Measurement | Methodology | Database Size | City | Key Results |
|---|---|---|---|---|---|
| Wilhelmsson [ | Noise level, visual exposure to a road | OLS | 292 housing transactions | Stockholm (Sweden) | A single-family house located near a road with loud traffic could lose 30% of its value |
| Kawamura and Mahajan [ | Daily volume, max hourly volume, and total night volume for trucks and all vehicles | Spatial lag and 2SLS | 685 single-family houses | Chicago (USA) | Traffic characteristics have modest but statistically significant impact on property values; truck traffic characteristics are not statistically significant |
| Day et al. [ | Road, rail, and aircraft noise | Partially linear model with spatial smoothing | 10,848 residential properties | Birmingham (UK) | A 1-dB increase in road traffic noise reduces the selling price of a property by between 0.18% and 0.55% |
| Kim et al. [ | Traffic noise level, distance to different types of roads | OLS | 328 zones | Seoul (South Korea) | A 1% increase in traffic noise is associated with a 1.3% decline in land price |
| Andersson et al. [ | Road and rail noise | OLS | 1738 houses | Lerum (Sweden) | Road noise has a larger negative impact on the property prices than railway noise |
| Blanco and Flindell [ | Road and rail noise | OLS | Flats in London (407), Birmingham (226) and Sutton Coldfield (86) | London, Birmingham, Sutton Coldfield (UK) | Noise decreases property values in London, raises in Sutton Coldfield, and no significant impacts in Birmingham |
| Brandt and Maennig [ | Road, rail, and aircraft noise on a micro-level grid | Spatial lag | 4832 condominiums | Hamburg (Germany) | A 1-dB(A) increase in noise reduces the value of a condominium by 0.23% |
| Larsen [ | Daily traffic count | OLS | 9680 single-family house transactions | Kettering (USA) | Parcels fronting or adjacent to a high-traffic sell at an 8.1% discount |
| Li and Saphores [ | Freeway average daily traffic, percentage of trucks in freeway | OLS | 4715 single-family houses | Los Angeles (USA) | A 1% increase in total traffic would reduce by only $24 the value of a $420,000 house located within 100 m of a freeway. A 1% increase in truck traffic would decrease the value of a $420,000 house located between 100 and 400 m from the nearest freeway by $2000 to $2750 |
| Del Giudice and De Paola [ | Noise level | OLS | 31 residential properties | Naples (Italy) | A 1-dB increase in noise level reduces the selling price of a property by between 0.30% (diurnal emissions) and 0.33% (nocturnal emissions) |
| Larsen and Blair [ | Daily traffic count | OLS | 9680 single-family house transactions and 455 multi-unit rental properties | Kettering (USA) | Houses located adjacent to an arterial street sold at a 7.8% discount |
| owicki and Piotrowska [ | Noise level, distance to roads | OLS | 56 residential properties | Poznan (Poland) | Plots located in the zone with noise exceedance at night were about 57% cheaper than those located outside this zone |
| Szczepańska et al. [ | Noise level | Correlation analysis | 118 apartments | Olsztyn (Poland) | Correlation between apartment prices and noise level in the range [0.61, 0.51] |
| Swoboda et al. [ | Traffic noise | LWR (locally weighted regression) | 42,083 single-family properties | St Paul, Minnesota (USA) | Marginal effect of traffic noise varies over space and time |
| Le Boennec and Salladarré [ | Air and noise pollution | OLS | 2969 houses | Nantes (France) | Air pollution has no significant impact on the price; noise pollution does have an impact |
| Gallo [ | Average daily frequency | OLS | 60 zones | Naples (Italy) | High-frequency metro lines have appreciable effects on real estate values |
Figure 1Evolution of vehicles in the region of Madrid. Source: National Department of Traffic, www.dgt.es.
Figure 2Location of traffic flow measurement points across Madrid.
Figure 3Location of flats in the analysis.
Figure 4Average price of flats per square metre by census section.
Summary statistics for the variables included in the dataset.
| Variable | Description | Min | Median | Mean | Max | Sd. Deviation |
|---|---|---|---|---|---|---|
| Structural variables | ||||||
| Price | Bid price (€) | 99,500 | 258,860 | 377,273 | 3,600,000 | 335,569.80 |
| Area | Square metres of the dwelling | 30 | 87 | 100.30 | 300 | 51.65 |
| Bedrooms | Number of bedrooms | 1 | 3 | 2.62 | 8 | 1.15 |
| Bathrooms | Number of bathrooms | 1 | 1 | 1.62 | 5 | 0.08 |
| Lift | Lift facility in building (0/1) | 0 | 1 | 0.76 | 1 | 0.43 |
| Garden | Garden (0/1) | 0 | 0 | 0.20 | 1 | 0.41 |
| Renovated | Is the dwelling renovated? (0/1) | 0 | 0 | 0.24 | 1 | 0.43 |
| Views | Dwelling with views (0/1) | 0 | 0 | 0.14 | 1 | 0.35 |
| Luxury | Luxury dwelling (0/1) | 0 | 0 | 0.04 | 1 | 0.20 |
| Open kitchen | Open kitchen (0/1) | 0 | 0 | 0.07 | 1 | 0.26 |
| Wooden floor | Wooden floor / laminate flooring (0/1) | 0 | 0 | 0.27 | 1 | 0.45 |
| Neighborhood variable | ||||||
| Avg. family income | Average family income in the section (€) | 10,027 | 34,161 | 39,626 | 89,015 | 5508.44 |
| Road traffic variables | ||||||
| Distance | Distance from the nearest TMP (km) | 0.0003 | 0.1159 | 0.1983 | 4.047 | 0.36 |
| ADT | Average daily traffic in the nearest TMP | 0.5 | 19,800.9 | 31,783.6 | 345,239.4 | 37,471.69 |
Regression results.
| Variable | Estimate | Std. Error | t Value | Pr(>|t|) | VIF |
|---|---|---|---|---|---|
| (Intercept) | 11.2820040 | 0.0040825 | 2763.48 | 0.0000 *** | |
| Area | 0.0103689 | 0.0000416 | 249.14 | 0.0000 *** | 4.6157 |
| Bedrooms |
| 0.0012373 |
| 0.2826 | 2.0577 |
| Bathrooms | 0.0239193 | 0.0021622 | 11.06 | 0.0000 *** | 2.8575 |
| Lift | 0.0429986 | 0.0025190 | 17.07 | 0.0000 *** | 1.2008 |
| Avg. family income | 0.0000133 | 0.0000002 | 57.26 | 0.0000 *** | 1.6408 |
| Renovated | 0.0110624 | 0.0023904 | 4.63 | 0.0000 *** | 1.0520 |
| Views | 0.0121576 | 0.0029353 | 4.14 | 0.0000 *** | 1.0474 |
| Luxury | 0.0029306 | 0.0052594 | 0.56 | 0.5774 | 1.0814 |
| Open kitchen |
| 0.0039775 |
| 0.0002 *** | 1.0987 |
| Wooden floor | 0.0066911 | 0.0022680 | 2.95 | 0.0032 ** | 1.0326 |
| Distance | 0.0076939 | 0.0027497 | 2.80 | 0.0051 ** | 1.0058 |
| ADT |
| 0.0000000 |
| 0.0422 * | 1.0059 |
Significant codes: 0.001 ***, 0.01 **, 0.05 *; Residual standard error: 0.1472 on 21621 degrees of freedom; Multiple : 0.9437; Adjusted : 0.9437; F-statistic: 3.022 × 10 on 12 and 21621 DF, p-value: < 2.2 × 10.