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Economic Valuation of Noise Pollution from the Suvarnabhumi Airport
        Using Home Value under Hedonic Pricing Method




                   Pisit Puapan and Pat Pattanarangsun
           National Institute of Development Administration (NIDA)
                                 May 2008




                For Submission to Professor Adis Israngkura
                    ECON 951 Environmental Valuation
CONTENT



1. Introduction                                   1
   1.1 Objectives of the Study                    1
   1.2 Benefits from the Study                    1


2. Theoretical Framework and Literature Reviews   2
   2.1 Hedonic Pricing Method (HPM)               2
   2.2 Literature Reviews                         2


3. Methodological Framework                       3
   3.1 Data                                       3
   3.2 Methodological and Model                   3
   3.3 Variables Descriptions                     5


4. Empirical Results                              6
   4.1 Descriptive Statistics                     6
   4.2 HPM Results                                7
   4.3 Marginal Prices                            9


5. Concluding Remark                              12
   5.1 Summary                                    12
   5.2 Suggestions                                12


References                                        13


Appendix                                          14
   Appendix A: Data                               15
   Appendix B: Full Model Estimation              16
   Appendix c: Reduced Model Estimation           18
1. INTRODUCTION


Since the opening of Suvarnabhumi Airport in September 2006, a major problem of this
Airport was created from the noise pollution affecting the surrounding communities from
hospitals, temples, schools, universities, and houses. It is possible to use the home and land
value to estimate the value of noise pollution under the presumption that it negatively affects
home and land value by using the Hedonic Pricing Method (HPM). We have conducted
survey of the home prices within the noise contour area as well as non-noise contour area
around the Airport.


1.1 Objectives of the study


     To study the value of noise pollution around the Airport using the home values around
     the Airport by comparing home prices in the noise contour and non-noise contour areas
     under the Hedonic Pricing Method
     To estimate the values of specific attributes and characteristics of homes and the
     environments that could not be valued with other approaches.


1.2 Benefits from the study


To know the value of the noise pollution created by the Airport and to use this information as
policy guideline for compensations for affected families/persons.




                                             -1-
2. THEORETICAL FRAMEWORK AND LITERATURE REVIEWS

2.1 Hedonic Pricing Method (HPM)


The hedonic pricing method is used to estimate economic values for ecosystem or
environmental services that directly affect market prices. It is most commonly applied to
variations in housing prices that reflect the value of local environmental attributes.
It can be used to estimate economic benefits or costs associated with:
       environmental quality, including air pollution, water pollution, or noise
       environmental amenities, such as aesthetic views or proximity to recreational sites

The basic premise of the hedonic pricing method is that the price of a marketed good is
related to its characteristics, or the services it provides. The hedonic pricing method is most
often used to value environmental amenities that affect the price of residential properties.


2.2 Literature Reviews


Leggett, C.G. and Bockstael, N.E. (2000) had conducted a study on the effect on house
prices of changes in nearby faecal coliform concentrations in Chesapeake Bay, Maryland to
estimate the water quality using the Hedonic Price Method. The authors estimate a single
stage OLS hedonic model to demonstrate the effect of changes in water quality on property
prices rather than using the characteristics of houses (rooms, bathrooms, etc.), Leggett and
Bockstael use the appraised value of houses. The study found that a change of 100 faecal
coliform counts per 100 mL is estimated to produce about a 1.5% change in property prices.
The study shows some specification problems that were identified (eg heteroscedasticity and
autocorrelation. However, the correction of these problems did not have substantial effects on
value estimates.


Rahmatian M. and Cockerill L. (2004) had done a study titled “Airport Noise and
Residential Housing Valuation in Southern California” using the Hedonic Pricing Method by
comparing Model 3 Functional Forms namely Linear, Semi-Log and Log-Linear to search
for the best estimate of the marginal implicit price of airport influence. The results indicate



                                              -2-
that individuals consider airport proximity and airport flight patterns in their housing
purchases. This shows that there exist two distinct measurable price gradients that distinguish
large airports from small airports. In addition, homes located under the flight path of a large
airport have a price gradient that is significantly larger than homes located under the flight
path of a small airport.


3. METHODOLOGICAL FRAMEWORK

3.1 Data


This paper obtains information to conduct the study from the following sources:
 1) Websites:
       - http://www.thaihomeonline.com
       - http://classified.sanook.com
       - http://www.ban4u.com
       - http://www.pantipmarket.com

 2) Books: Talad Ban (        F   ), Arkarn Lae Teedin ((              )

 3) Phone Interview


3.2 Methodology and Model


The methodology and model are as follows:


step 1: Data collection on home values with various attributes/characteristics such as prices,
       areas, utilized areas, number of restrooms, number of bedrooms, garage, distance
       from the Airport, number of stories, house types (town house, single home) and
       location with respect to Noise Contour.




                                             -3-
step 2: Estimate the relationship between the home prices and other related variables


        Dependent Variables
          - Prices of houses


        Independent Variables
        Categorized into 3 groups
          - Attributes such as number of floors, number of bedrooms
          - Environmental variables1 such as noise and air particle pollution
          - Community variables2 such as Crime Rate and average income of communities


step 3: Choose Functional Form of the Hedonic Pricing Model. The study chooses Semi-log
        (Log-Lin) with the following form ln(P) = α0 + ΣβiZi


step 4: Conduct 1st Stage Hedonic Pricing Model Estimation to estimate the coefficients of
        the model to estimate the home values with home located within and outside the noise

        contour. (Moreover, we can estimate the values of specific attributes that are in the

        model such as the value of garages).



step 5: Conduct the Ordinary Least Square (OLS) with the Eviews program and testing the
        following:
             Testing the CLRM assumptions such as Normality Test , Heteroskedasticity Test,
             Serial Correlation and Multicollinearity Problem
             Testing the Model such as Individual Significance, Sign and R2




1
  Due to data unavailability, the authors can not obtain certain environmental data such as Decibel and PM10,
therefore, the study uses dummy variables to represent home located within and outside the noise contour
2
  The study cannot obtain data on community and neighborhood, so these factors are not included in the model.



                                                    -4-
3.3 Variables Descriptions
The descriptions of all variables are illustrated in Table 1


Table 1 Variables Descriptions

     Variables                       Definition                              Units               Expected Sign
        P                            Sale price                               Baht                      N/A
       LOT                        Total land area                         Square Wa                       +
      AREA                      Total living space                      Square Meters                     +
     FLOOR                      Number of floors                             floors                       +
      BATH                   Number of Bathrooms                             rooms                        +
       BED                    Number of Bedrooms                             rooms                        +
       CAR                         Garage space                               cars                        +
       DIS            Distance to Suvarnabhumi airport                    kilometers                    +/-3
      NOISE         1 if located in noise contour, 0 if not                    0/1                        -
    TOWNHOUSE          1 if townhouse, 0 if single house                       0/1                        -




3
  In the case of uncertain +/-, this is due to indeterminable effect of distance whether is positive or negative
since it is positive for transportation but negative for noise.



                                                        -5-
4. EMPIRICAL RESULTS

4.1 Descriptive Statistics


The empirical results are illustrated in Table 2


Table 2 Descriptive Statistics

                            Mean          Median          Max            Min          Std.Dev
         P                 4040909        3860000       12790000         820000       2784737.3
       LOT                   68.64           57            287             15              56.85
      AREA                  335.23           288           1148            50           240.05
     FLOOR                   1.977            2              3              1              0.46
      BATH                   2.114            2              4              1              0.75
       BED                   2.591            2              6              2              1.00
       CAR                   1.477            2              4              0              0.95
        DIS                 12.682           12             32              7              4.89
      NOISE               No.of “0” (outside contour) = 28 and No.of “1” (within contour) = 16
 TOWNHOUSE                No. of “0” (single house) = 30 and No. of “1” = 14 (townhouse)




                                                  -6-
4.2 HPM Results


The results from regression in a Full Model (inclusive of all variables) i.e.
                                                                                                  4
P = f(LOT,AREA,BATH,BED,FLOOR,CAR,DIS,NOISE,TOWNHOUSE) are as follows:


ln(P) = 13.6475 - 0.0017LOT + 0.0017AREA + 0.2378BATH - 0.0616BED
           (48.86)*       (-0.415)        (2.350)*             (2.071)*     (-0.727)

          + 0.1055FLOOR + 0.1974CAR + 0.0103DIS - 0.190 NOISE - 0.1379 TOWNHOUSE
                     (0.833)         (2.191)*        (1.149)        (-1.927)**         (-1.420)

Adj.R2 = 0.8839
F-Stat = 37.377
Note: “*” and “**” denote 5% and 10% level of significance respectively


From the empirical results and testing of the Full Model, it has the problem of
multicollinearity as shown in the correlation matrix in Appendix B.4 which cause most
variables to be insignificant despite high R2. Therefore, the authors exclude some of the
variables to test the following 6 models:


      1. Model excluding AREA, BED
      2. Model excluding AREA, CAR
      3. Model excluding LOT, CAR
      4. Model excluding AREA, CAR, DIS
      5. Model excluding AREA, BED, DIS
      6. Model excluding LOT, CAR, DIS




4
    See Appendix B



                                                 -7-
Table 3 comparison of the results from 6 Models

                                 #1          #2              #3       #4       #5       #6
LOT                                *              *                     *        *
AREA                                                           *                          *
FLOOR                              *              *                     *        *
BATH                                              *            *        *                 *
BED                                               *            *        *                **
CAR                                *                                             *
DIS
NOISE                              *              *            *        *        *        *
TOWNHOUSE                         **          **              **       **       **       **
# independent variables           7           7               7        6        6        6
  - sig at α = 5% (10%)         4 (5)       5 (6)           4 (5)     5(6)     4(5)     3(5)
  - sig & correct sign          4 (5)       4 (5)            3(4)     4(5)     4(5)     3(4)
Adjusted R-squared             0.8645      0.8632           0.8730   0.8647   0.8674   0.8721


Note: 1. “*” and “**” denote 5% and 10% level of significance respectively
      2. the variable with wrong sign is “BED” for all cases in which variable “BED” is
         significant




                                                      -8-
All Models have similar Adjusted R2. The authors choose Model number                       4 which has the
most significant variables as follows:


ln(P) = 13.8262 + 0.0087LOT + 0.3071FLOOR + 0.2697BATH 0.1825BED
         (53.568)*       (5.157)*             (3.135)*           (2.376)*        (-2.527)*5

          – 0.2731NOISE – 0.1878TOWNHOUSE
                  (-2.891)*                  (-1.819)**

Adj. R2 = 0.8647
F-Stat = 46.805
Note: “*” and “**” denote 5% and 10% level of significance respectively


This is the Model that can explain home prices from the attributes/characteristics using the
Hedonic Pricing Model as follows:
ln(P) = 13.826 + 0.0087LOT + 0.307FLOOR + 0.2707BATH - 0.183BED - 0.190NOISE - 0.138TOWNHOUSE



4.3 Marginal Prices

    4.3.1    Formula for semi-log model

        ln(P) = α0 + ΣβiZi
        (1/P)⋅(∂P/∂Zi) = βi
        (∂P/P)/∂Zi = βi

        Therefore marginal price of Zi = P(Zi) = ∂P/∂Zi = βiP




5
  BED or number of bedrooms shows opposite sign from our expectation, but the authors retain the variable in
the Model since the study aims to value noise pollution and this attribute may be due to consumers’ behaviors
which may need further study.



                                                     -9-
4.3.2     Marginal price calculation6

      From the formula in 43.1, the marginal prices of attributes can be calculated as follows:
         1. P(LOT)                   = 0.0087*4040909.09                        = 35220.56
         2. P(FLOOR)                 = 0.3071*4040909.09                        = 1241003.59
         3. P(BATH)                  = 0.2697*4040909.09                        = 1089631.14
         4. P(BED)                   = -0.1825*4040909.09                       = -737328.52
         5. P(NOISE)                 = -0.2731*4040909.09                       = -1103370.23
         6. P(TOWNHOUSE)             = -0.1878*4040909.09                       = -758878.69

      4.3.3     Interpretation of marginal prices

      The interpretation of the marginal prices can be done from the variables as follows:
         Inside and outside noise contour (NOISE)
         (= 1 if inside, = 0 if outside)

            from P(NOISE) =          -1103370.23
           ∴ the price of house which is outside noise contour is 1103370 baht higher than the
              one which is inside noise contour

              ln(Pout) - ln(Pin) = 0.273050        ln(Pout / Pin) = 0.273050
                                                   Pout / Pin = e0.27305 = 1.314
           ∴ the price of house which is outside noise contour is 1.314 (or 31.4% greater than)
               times the one which is inside noise contour
         Townhouse and Single house (TOWNHOUSE)
         (= 1 if townhouse, = 0 if single house)

            from P(TOWNHOUSE) = -758878.69
           ∴ the price of single house is 758879 baht higher than the price of a townhouse

            ln(Psingle) - ln(Ptown) = 0.187799             ln(Psingle / Ptown) = 0.187799
                                                           Psingle / Ptown = e0.187799 = 1.207


6
    Average P = 4040909.09 has been used in the estimation of marginal prices



                                                     - 10 -
∴ the price of a single house is 1.207 times (or 20.7% greater than) the price of a
    townhouse

Lot size (LOT)

  from P(LOT) = 35220.56
 ∴ the value of lot size is about 35220.56 baht per 1 square Wa

  (∂P/P)/∂LOT = βi = 0.008716
 ∴ when lot size increases 1 square Wa, the price of a house will increase by 0.8716%

No.of floors (FLOOR)

  from P(FLOOR) = 1241003.59
 ∴ the value of one additional floor is about 1241003.59 baht

  (∂P/P)/∂FLOOR = βi = 0.307110
 ∴ when there is one additional floor, the price of a house will increase by 30.71%

No.of bathrooms (BATH)

  from P(BATH) = 1089631.14
 ∴ the value of a bathroom is about 1089631.14 baht

  (∂P/P)/∂BATH = βi = 0.269650
 ∴ when there is an additional bathroom, the price of a house will increase by 26.97%

No.of bedrooms (BED)

  from P(BED) = -737328.52
 ∴ the value of a bedroom is about -737328.52 baht

  (∂P/P)/∂BED = βi = -0.187799
 ∴ when there is an additional bathroom, the price of a house will decrease by 18.78%




                                      - 11 -
5. CONCLUDING REMARK

5.1 Summary

Noise problem from Suvarnabhumi airport can be reflected from a difference between prices
of houses which are in and out of noise contour ≈ 1,103,370 Baht. Furthermore, other
attributes which may not be valued directly or easily can be determined by the calculation of
marginal prices from hedonic price function in the 1st stage.

5.2 Suggestions

   5.2.1 Recommendations for further study

             Collecting more observations to make the results more reliability.
             Add more independent variables to capture other effects to home value and be
             able to focus on the values of specific attributes
             - Pollution level e.g. dB(A), PM10
             - Community and neighborhood variables e.g. crime, income
             Adjusting the Model such as

             - Changing the Functional Form e.g. linear Boxcox
             - Including the Interaction Term or Slope Dummy into the Model
             Estimate demand (2nd Stage Hedonic) to measure welfare (in case of non-
             marginal change)


   5.2.2 Policy Recommendation

             The concerned authorities should consider compensating the people affected by
             the noise pollution within and outside the noise contour by 1.1 million Baht.
             Consideration should be made for the timeline of residence such as the new
             residents (after the Airport’s opening) have already benefited from lower home
             prices, and should not be compensated for noise pollution. On the other hand,
             old residents (living prior to the Airport’s opening) should be compensated
             accordingly.


                                             - 12 -
REFERENCES


Adair, A.S., Berry, J. N& McGreal, W. S. (1996). Hedonic modeling, housing submarkets
       and residential valuation, Journal of Property Research, vol. 13, pp. 67-83.

Clark, D. E. & Herrin, W. E. (2000). The Impact of public school attributes on home sale
       price in California, Growth and Change, vol. 31, pp. 385-407.

Espey, M. & Lopez, H. (2000). The impact of airport noise and proximity on residential
       property values, Growth and Change, vol. 31, pp. 408-419.

Garrod G. and Keneth G. Willis. (2003). “A Primer on Non market Valuation”. 1st ed.
       Edward Elgar Publishing Limited.

Leggett, C. G. & Bockstael, N. E. (2000). Evidence of the effects of water quality on
       residential land prices, Journal of Economics and Management, vol. 39, pp.121-144.

Patricia A. Champ, Kevin J. Boyle and Thomas C. Brown. (1999). “Economic Valuation of
       the Environment: Methods and Case Studies”. 1st ed. Kluwer Academic Publisher.

Rahmatian M. and Cockerill L. (2004) “Airport Noise and Residential Housing Valuation in
       Southern California”. International Journal of Environmental Science & Technology.
       vol.1, No.1, pp.17-25.




                                            - 13 -
APPENDIX




  - 14 -
Appendix A:
                                                                           Data

Obs   AREA   LOT   BATH   BED   CAR    DIS     NOISE   TOWNHOUSE   FLOOR    PRICE

 1     379    79    2      2     2      8        1         0         2      4510000
 2     300    54    3      4     1     15        0         1         3      4750000
 3     518   130    3      3     3      7        1         0         2      6480000
 4     576    80    2      3     2     10        0         0         3      5880000
 5     614   151    3      4     3     26        0         0         2      8500000
 6     404   101    3      3     3      9        0         0         2      4970000
 7     403    84    2      2     2     13        0         0         2      4730000
 8     612    85    2      2     2      8        0         0         3      6410000
 9     144    60    2      2     2     15        0         0         1      2810000
10     612    98    2      2     2     13        0         0         2     6810000
11     179    28    2      2     1     10        1         0         2     1730000
12     360    75    2      2     2     10        0         0         2     3950000
13     132    50    2      3     2     13        0         0         2     3900000
14     760   190    4      4     2     11        0         0         2     9150000
15     228    36    2      2     1     12        0         0         2     2330000
16     322    67    2      2     2      9        1         1         2      4100000
17     288    60    2      2     2     15        0         0         2     3900000
18     122    38    2      2     1      8        1         1         1      1590000
19     67    17     1      2     0      9        1         1         1      820000
20     128    20    2      3     1     11        1         1         2      960000
21     160    42    2      4     0     12        1         0         1     2000000
22     648   110    2      3     2      7        0         0         2     8150000
23     50    16     1      2     1     14        0         1         2     1230000
24     310    62    2      3     1     32        0         0         2     4300000
25     288    45    2      2     1     16        0         1         2     3680000
26     288    45    2      2     1     20        0         0         2     3940000
27     120    15    1      2     0     12        1         0         2     1460000
28     134    17    1      2     0      9        1         0         2      1060000
29     188    29    2      2     1     12        1         1         2     2230000
30     195    31    2      2     1     13        0         0         2     2010000
31     620   155    3      5     2     11        0         0         2     6790000
32     173    27    2      2     1     15        0         1         2     1810000
33     760   190    4      5     3     14        0         0         2     9250000
34    1148   287    4      6     4     18        1         0         2     12790000
35     128    16    1      2     0     14        0         1         2     1400000
36     120    15    1      2     0      8        1         0         2      1000000
37     154    24    2      2     1     10        1         1         2     1840000
38     120    15    1      2     0     13        0         1         2     1240000
39     175    47    2      2     1     10        1         1         2     2340000
40     73    23     2      2     1      7        1         1         1     1120000
41     678   113    3      3     2     11        0         0         3     8320000
42     324    68    2      2     2     21        0         0         2     3940000
43     446    62    2      2     2     14        0         0         2     3800000
44     302    63    2      2     2     13        0         0         2     3820000



                                      - 15 -
Appendix B:
                                                                               Full Model Estimation

B.1 Result

             Dependent Variable: LOG(P)
             Method: Least Squares
             Date: 05/09/08 Time: 21:40
             Sample: 1 44
             Included observations: 44

                   Variable          Coefficient         Std. Error   t-Statistic     Prob.

                     LOT             -0.001696           0.004084     -0.415317       0.6805
                    AREA              0.001724           0.000734      2.349958       0.0247
                   FLOOR              0.105486           0.126646      0.832913       0.4107
                    BATH              0.237765           0.114812      2.070914       0.0460
                     BED             -0.061554           0.084634     -0.727302       0.4720
                    CAR               0.197407           0.090087      2.191293       0.0354
                     DIS              0.010303           0.008971      1.148534       0.2588
                   NOISE             -0.190268           0.098735     -1.927064       0.0624
                 TOWNHOUSE           -0.137883           0.097099     -1.420024       0.1647
                      C               13.64753           0.279308      48.86199       0.0000

             R-squared                0.908205       Mean dependent var             14.96983
             Adjusted R-squared       0.883906       S.D. dependent var             0.728276
             S.E. of regression       0.248142       Akaike info criterion          0.247087
             Sum squared resid        2.093534       Schwarz criterion              0.652584
             Log likelihood           4.564094       F-statistic                    37.37663
             Durbin-Watson stat       2.072298       Prob(F-statistic)              0.000000




B.2 Normality Test
             8
                                                                      Series: Residuals
             7                                                        Sample 1 44
                                                                      Observations 44
             6
                                                                      Mean          -7.36e-16
             5
                                                                      Median        -0.016962
             4                                                        Maximum        0.414774
                                                                      Minimum       -0.543988
             3                                                        Std. Dev.      0.220651
                                                                      Skewness      -0.019328
             2                                                        Kurtosis       2.545039

             1                                                        Jarque-Bera    0.382220
                                                                      Probability    0.826042
             0
                    -0.4      -0.2     -0.0        0.2         0.4




                                               - 16 -
B.3 White Hetero Skcedasticity test




B.4 Correlation Matrix




                                      - 17 -
Appendix C:
                                                                          Reduced Model Estimation

C.1 Result

             Dependent Variable: LOG(P)
             Method: Least Squares
             Date: 05/09/08 Time: 21:48
             Sample: 1 44
             Included observations: 44

                   Variable        Coefficient         Std. Error      t-Statistic      Prob.

                    LOT             0.008716           0.001690        5.157246        0.0000
                  FLOOR             0.307110           0.097960        3.135064        0.0034
                   BATH             0.269650           0.113476        2.376263        0.0228
                   BED             -0.182466           0.072202       -2.527166        0.0159
                  NOISE            -0.273050           0.094436       -2.891384        0.0064
                TOWNHOUSE          -0.187799           0.103229       -1.819250        0.0770
                     C              13.82623           0.258109        53.56752        0.0000

             R-squared              0.883585      Mean dependent var                 14.96983
             Adjusted R-squared     0.864707      S.D. dependent var                 0.728276
             S.E. of regression     0.267876      Akaike info criterion              0.348323
             Sum squared resid      2.655023      Schwarz criterion                  0.632171
             Log likelihood        -0.663100      F-statistic                        46.80482
             Durbin-Watson stat     2.022406      Prob(F-statistic)                  0.000000



C.2 Normality Test
  6
                                                                    Series: Residuals
                                                                    Sample 1 44
  5
                                                                    Observations 44

  4                                                                 Mean             -1.93e-15
                                                                    Median            0.002960
  3                                                                 Maximum           0.522445
                                                                    Minimum          -0.415909
                                                                    Std. Dev.         0.248485
  2                                                                 Skewness          0.200434
                                                                    Kurtosis          2.281225
  1
                                                                    Jarque-Bera      1.241778
                                                                    Probability      0.537466
  0
      -0.4       -0.2     -0.0      0.2          0.4




                                             - 18 -
C.3 White Hetero Skedasticity test




                                     - 19 -

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Noise pollution suvarnabhumi airport

  • 1. Economic Valuation of Noise Pollution from the Suvarnabhumi Airport Using Home Value under Hedonic Pricing Method Pisit Puapan and Pat Pattanarangsun National Institute of Development Administration (NIDA) May 2008 For Submission to Professor Adis Israngkura ECON 951 Environmental Valuation
  • 2. CONTENT 1. Introduction 1 1.1 Objectives of the Study 1 1.2 Benefits from the Study 1 2. Theoretical Framework and Literature Reviews 2 2.1 Hedonic Pricing Method (HPM) 2 2.2 Literature Reviews 2 3. Methodological Framework 3 3.1 Data 3 3.2 Methodological and Model 3 3.3 Variables Descriptions 5 4. Empirical Results 6 4.1 Descriptive Statistics 6 4.2 HPM Results 7 4.3 Marginal Prices 9 5. Concluding Remark 12 5.1 Summary 12 5.2 Suggestions 12 References 13 Appendix 14 Appendix A: Data 15 Appendix B: Full Model Estimation 16 Appendix c: Reduced Model Estimation 18
  • 3. 1. INTRODUCTION Since the opening of Suvarnabhumi Airport in September 2006, a major problem of this Airport was created from the noise pollution affecting the surrounding communities from hospitals, temples, schools, universities, and houses. It is possible to use the home and land value to estimate the value of noise pollution under the presumption that it negatively affects home and land value by using the Hedonic Pricing Method (HPM). We have conducted survey of the home prices within the noise contour area as well as non-noise contour area around the Airport. 1.1 Objectives of the study To study the value of noise pollution around the Airport using the home values around the Airport by comparing home prices in the noise contour and non-noise contour areas under the Hedonic Pricing Method To estimate the values of specific attributes and characteristics of homes and the environments that could not be valued with other approaches. 1.2 Benefits from the study To know the value of the noise pollution created by the Airport and to use this information as policy guideline for compensations for affected families/persons. -1-
  • 4. 2. THEORETICAL FRAMEWORK AND LITERATURE REVIEWS 2.1 Hedonic Pricing Method (HPM) The hedonic pricing method is used to estimate economic values for ecosystem or environmental services that directly affect market prices. It is most commonly applied to variations in housing prices that reflect the value of local environmental attributes. It can be used to estimate economic benefits or costs associated with: environmental quality, including air pollution, water pollution, or noise environmental amenities, such as aesthetic views or proximity to recreational sites The basic premise of the hedonic pricing method is that the price of a marketed good is related to its characteristics, or the services it provides. The hedonic pricing method is most often used to value environmental amenities that affect the price of residential properties. 2.2 Literature Reviews Leggett, C.G. and Bockstael, N.E. (2000) had conducted a study on the effect on house prices of changes in nearby faecal coliform concentrations in Chesapeake Bay, Maryland to estimate the water quality using the Hedonic Price Method. The authors estimate a single stage OLS hedonic model to demonstrate the effect of changes in water quality on property prices rather than using the characteristics of houses (rooms, bathrooms, etc.), Leggett and Bockstael use the appraised value of houses. The study found that a change of 100 faecal coliform counts per 100 mL is estimated to produce about a 1.5% change in property prices. The study shows some specification problems that were identified (eg heteroscedasticity and autocorrelation. However, the correction of these problems did not have substantial effects on value estimates. Rahmatian M. and Cockerill L. (2004) had done a study titled “Airport Noise and Residential Housing Valuation in Southern California” using the Hedonic Pricing Method by comparing Model 3 Functional Forms namely Linear, Semi-Log and Log-Linear to search for the best estimate of the marginal implicit price of airport influence. The results indicate -2-
  • 5. that individuals consider airport proximity and airport flight patterns in their housing purchases. This shows that there exist two distinct measurable price gradients that distinguish large airports from small airports. In addition, homes located under the flight path of a large airport have a price gradient that is significantly larger than homes located under the flight path of a small airport. 3. METHODOLOGICAL FRAMEWORK 3.1 Data This paper obtains information to conduct the study from the following sources: 1) Websites: - http://www.thaihomeonline.com - http://classified.sanook.com - http://www.ban4u.com - http://www.pantipmarket.com 2) Books: Talad Ban ( F ), Arkarn Lae Teedin (( ) 3) Phone Interview 3.2 Methodology and Model The methodology and model are as follows: step 1: Data collection on home values with various attributes/characteristics such as prices, areas, utilized areas, number of restrooms, number of bedrooms, garage, distance from the Airport, number of stories, house types (town house, single home) and location with respect to Noise Contour. -3-
  • 6. step 2: Estimate the relationship between the home prices and other related variables Dependent Variables - Prices of houses Independent Variables Categorized into 3 groups - Attributes such as number of floors, number of bedrooms - Environmental variables1 such as noise and air particle pollution - Community variables2 such as Crime Rate and average income of communities step 3: Choose Functional Form of the Hedonic Pricing Model. The study chooses Semi-log (Log-Lin) with the following form ln(P) = α0 + ΣβiZi step 4: Conduct 1st Stage Hedonic Pricing Model Estimation to estimate the coefficients of the model to estimate the home values with home located within and outside the noise contour. (Moreover, we can estimate the values of specific attributes that are in the model such as the value of garages). step 5: Conduct the Ordinary Least Square (OLS) with the Eviews program and testing the following: Testing the CLRM assumptions such as Normality Test , Heteroskedasticity Test, Serial Correlation and Multicollinearity Problem Testing the Model such as Individual Significance, Sign and R2 1 Due to data unavailability, the authors can not obtain certain environmental data such as Decibel and PM10, therefore, the study uses dummy variables to represent home located within and outside the noise contour 2 The study cannot obtain data on community and neighborhood, so these factors are not included in the model. -4-
  • 7. 3.3 Variables Descriptions The descriptions of all variables are illustrated in Table 1 Table 1 Variables Descriptions Variables Definition Units Expected Sign P Sale price Baht N/A LOT Total land area Square Wa + AREA Total living space Square Meters + FLOOR Number of floors floors + BATH Number of Bathrooms rooms + BED Number of Bedrooms rooms + CAR Garage space cars + DIS Distance to Suvarnabhumi airport kilometers +/-3 NOISE 1 if located in noise contour, 0 if not 0/1 - TOWNHOUSE 1 if townhouse, 0 if single house 0/1 - 3 In the case of uncertain +/-, this is due to indeterminable effect of distance whether is positive or negative since it is positive for transportation but negative for noise. -5-
  • 8. 4. EMPIRICAL RESULTS 4.1 Descriptive Statistics The empirical results are illustrated in Table 2 Table 2 Descriptive Statistics Mean Median Max Min Std.Dev P 4040909 3860000 12790000 820000 2784737.3 LOT 68.64 57 287 15 56.85 AREA 335.23 288 1148 50 240.05 FLOOR 1.977 2 3 1 0.46 BATH 2.114 2 4 1 0.75 BED 2.591 2 6 2 1.00 CAR 1.477 2 4 0 0.95 DIS 12.682 12 32 7 4.89 NOISE No.of “0” (outside contour) = 28 and No.of “1” (within contour) = 16 TOWNHOUSE No. of “0” (single house) = 30 and No. of “1” = 14 (townhouse) -6-
  • 9. 4.2 HPM Results The results from regression in a Full Model (inclusive of all variables) i.e. 4 P = f(LOT,AREA,BATH,BED,FLOOR,CAR,DIS,NOISE,TOWNHOUSE) are as follows: ln(P) = 13.6475 - 0.0017LOT + 0.0017AREA + 0.2378BATH - 0.0616BED (48.86)* (-0.415) (2.350)* (2.071)* (-0.727) + 0.1055FLOOR + 0.1974CAR + 0.0103DIS - 0.190 NOISE - 0.1379 TOWNHOUSE (0.833) (2.191)* (1.149) (-1.927)** (-1.420) Adj.R2 = 0.8839 F-Stat = 37.377 Note: “*” and “**” denote 5% and 10% level of significance respectively From the empirical results and testing of the Full Model, it has the problem of multicollinearity as shown in the correlation matrix in Appendix B.4 which cause most variables to be insignificant despite high R2. Therefore, the authors exclude some of the variables to test the following 6 models: 1. Model excluding AREA, BED 2. Model excluding AREA, CAR 3. Model excluding LOT, CAR 4. Model excluding AREA, CAR, DIS 5. Model excluding AREA, BED, DIS 6. Model excluding LOT, CAR, DIS 4 See Appendix B -7-
  • 10. Table 3 comparison of the results from 6 Models #1 #2 #3 #4 #5 #6 LOT * * * * AREA * * FLOOR * * * * BATH * * * * BED * * * ** CAR * * DIS NOISE * * * * * * TOWNHOUSE ** ** ** ** ** ** # independent variables 7 7 7 6 6 6 - sig at α = 5% (10%) 4 (5) 5 (6) 4 (5) 5(6) 4(5) 3(5) - sig & correct sign 4 (5) 4 (5) 3(4) 4(5) 4(5) 3(4) Adjusted R-squared 0.8645 0.8632 0.8730 0.8647 0.8674 0.8721 Note: 1. “*” and “**” denote 5% and 10% level of significance respectively 2. the variable with wrong sign is “BED” for all cases in which variable “BED” is significant -8-
  • 11. All Models have similar Adjusted R2. The authors choose Model number 4 which has the most significant variables as follows: ln(P) = 13.8262 + 0.0087LOT + 0.3071FLOOR + 0.2697BATH 0.1825BED (53.568)* (5.157)* (3.135)* (2.376)* (-2.527)*5 – 0.2731NOISE – 0.1878TOWNHOUSE (-2.891)* (-1.819)** Adj. R2 = 0.8647 F-Stat = 46.805 Note: “*” and “**” denote 5% and 10% level of significance respectively This is the Model that can explain home prices from the attributes/characteristics using the Hedonic Pricing Model as follows: ln(P) = 13.826 + 0.0087LOT + 0.307FLOOR + 0.2707BATH - 0.183BED - 0.190NOISE - 0.138TOWNHOUSE 4.3 Marginal Prices 4.3.1 Formula for semi-log model ln(P) = α0 + ΣβiZi (1/P)⋅(∂P/∂Zi) = βi (∂P/P)/∂Zi = βi Therefore marginal price of Zi = P(Zi) = ∂P/∂Zi = βiP 5 BED or number of bedrooms shows opposite sign from our expectation, but the authors retain the variable in the Model since the study aims to value noise pollution and this attribute may be due to consumers’ behaviors which may need further study. -9-
  • 12. 4.3.2 Marginal price calculation6 From the formula in 43.1, the marginal prices of attributes can be calculated as follows: 1. P(LOT) = 0.0087*4040909.09 = 35220.56 2. P(FLOOR) = 0.3071*4040909.09 = 1241003.59 3. P(BATH) = 0.2697*4040909.09 = 1089631.14 4. P(BED) = -0.1825*4040909.09 = -737328.52 5. P(NOISE) = -0.2731*4040909.09 = -1103370.23 6. P(TOWNHOUSE) = -0.1878*4040909.09 = -758878.69 4.3.3 Interpretation of marginal prices The interpretation of the marginal prices can be done from the variables as follows: Inside and outside noise contour (NOISE) (= 1 if inside, = 0 if outside) from P(NOISE) = -1103370.23 ∴ the price of house which is outside noise contour is 1103370 baht higher than the one which is inside noise contour ln(Pout) - ln(Pin) = 0.273050 ln(Pout / Pin) = 0.273050 Pout / Pin = e0.27305 = 1.314 ∴ the price of house which is outside noise contour is 1.314 (or 31.4% greater than) times the one which is inside noise contour Townhouse and Single house (TOWNHOUSE) (= 1 if townhouse, = 0 if single house) from P(TOWNHOUSE) = -758878.69 ∴ the price of single house is 758879 baht higher than the price of a townhouse ln(Psingle) - ln(Ptown) = 0.187799 ln(Psingle / Ptown) = 0.187799 Psingle / Ptown = e0.187799 = 1.207 6 Average P = 4040909.09 has been used in the estimation of marginal prices - 10 -
  • 13. ∴ the price of a single house is 1.207 times (or 20.7% greater than) the price of a townhouse Lot size (LOT) from P(LOT) = 35220.56 ∴ the value of lot size is about 35220.56 baht per 1 square Wa (∂P/P)/∂LOT = βi = 0.008716 ∴ when lot size increases 1 square Wa, the price of a house will increase by 0.8716% No.of floors (FLOOR) from P(FLOOR) = 1241003.59 ∴ the value of one additional floor is about 1241003.59 baht (∂P/P)/∂FLOOR = βi = 0.307110 ∴ when there is one additional floor, the price of a house will increase by 30.71% No.of bathrooms (BATH) from P(BATH) = 1089631.14 ∴ the value of a bathroom is about 1089631.14 baht (∂P/P)/∂BATH = βi = 0.269650 ∴ when there is an additional bathroom, the price of a house will increase by 26.97% No.of bedrooms (BED) from P(BED) = -737328.52 ∴ the value of a bedroom is about -737328.52 baht (∂P/P)/∂BED = βi = -0.187799 ∴ when there is an additional bathroom, the price of a house will decrease by 18.78% - 11 -
  • 14. 5. CONCLUDING REMARK 5.1 Summary Noise problem from Suvarnabhumi airport can be reflected from a difference between prices of houses which are in and out of noise contour ≈ 1,103,370 Baht. Furthermore, other attributes which may not be valued directly or easily can be determined by the calculation of marginal prices from hedonic price function in the 1st stage. 5.2 Suggestions 5.2.1 Recommendations for further study Collecting more observations to make the results more reliability. Add more independent variables to capture other effects to home value and be able to focus on the values of specific attributes - Pollution level e.g. dB(A), PM10 - Community and neighborhood variables e.g. crime, income Adjusting the Model such as - Changing the Functional Form e.g. linear Boxcox - Including the Interaction Term or Slope Dummy into the Model Estimate demand (2nd Stage Hedonic) to measure welfare (in case of non- marginal change) 5.2.2 Policy Recommendation The concerned authorities should consider compensating the people affected by the noise pollution within and outside the noise contour by 1.1 million Baht. Consideration should be made for the timeline of residence such as the new residents (after the Airport’s opening) have already benefited from lower home prices, and should not be compensated for noise pollution. On the other hand, old residents (living prior to the Airport’s opening) should be compensated accordingly. - 12 -
  • 15. REFERENCES Adair, A.S., Berry, J. N& McGreal, W. S. (1996). Hedonic modeling, housing submarkets and residential valuation, Journal of Property Research, vol. 13, pp. 67-83. Clark, D. E. & Herrin, W. E. (2000). The Impact of public school attributes on home sale price in California, Growth and Change, vol. 31, pp. 385-407. Espey, M. & Lopez, H. (2000). The impact of airport noise and proximity on residential property values, Growth and Change, vol. 31, pp. 408-419. Garrod G. and Keneth G. Willis. (2003). “A Primer on Non market Valuation”. 1st ed. Edward Elgar Publishing Limited. Leggett, C. G. & Bockstael, N. E. (2000). Evidence of the effects of water quality on residential land prices, Journal of Economics and Management, vol. 39, pp.121-144. Patricia A. Champ, Kevin J. Boyle and Thomas C. Brown. (1999). “Economic Valuation of the Environment: Methods and Case Studies”. 1st ed. Kluwer Academic Publisher. Rahmatian M. and Cockerill L. (2004) “Airport Noise and Residential Housing Valuation in Southern California”. International Journal of Environmental Science & Technology. vol.1, No.1, pp.17-25. - 13 -
  • 16. APPENDIX - 14 -
  • 17. Appendix A: Data Obs AREA LOT BATH BED CAR DIS NOISE TOWNHOUSE FLOOR PRICE 1 379 79 2 2 2 8 1 0 2 4510000 2 300 54 3 4 1 15 0 1 3 4750000 3 518 130 3 3 3 7 1 0 2 6480000 4 576 80 2 3 2 10 0 0 3 5880000 5 614 151 3 4 3 26 0 0 2 8500000 6 404 101 3 3 3 9 0 0 2 4970000 7 403 84 2 2 2 13 0 0 2 4730000 8 612 85 2 2 2 8 0 0 3 6410000 9 144 60 2 2 2 15 0 0 1 2810000 10 612 98 2 2 2 13 0 0 2 6810000 11 179 28 2 2 1 10 1 0 2 1730000 12 360 75 2 2 2 10 0 0 2 3950000 13 132 50 2 3 2 13 0 0 2 3900000 14 760 190 4 4 2 11 0 0 2 9150000 15 228 36 2 2 1 12 0 0 2 2330000 16 322 67 2 2 2 9 1 1 2 4100000 17 288 60 2 2 2 15 0 0 2 3900000 18 122 38 2 2 1 8 1 1 1 1590000 19 67 17 1 2 0 9 1 1 1 820000 20 128 20 2 3 1 11 1 1 2 960000 21 160 42 2 4 0 12 1 0 1 2000000 22 648 110 2 3 2 7 0 0 2 8150000 23 50 16 1 2 1 14 0 1 2 1230000 24 310 62 2 3 1 32 0 0 2 4300000 25 288 45 2 2 1 16 0 1 2 3680000 26 288 45 2 2 1 20 0 0 2 3940000 27 120 15 1 2 0 12 1 0 2 1460000 28 134 17 1 2 0 9 1 0 2 1060000 29 188 29 2 2 1 12 1 1 2 2230000 30 195 31 2 2 1 13 0 0 2 2010000 31 620 155 3 5 2 11 0 0 2 6790000 32 173 27 2 2 1 15 0 1 2 1810000 33 760 190 4 5 3 14 0 0 2 9250000 34 1148 287 4 6 4 18 1 0 2 12790000 35 128 16 1 2 0 14 0 1 2 1400000 36 120 15 1 2 0 8 1 0 2 1000000 37 154 24 2 2 1 10 1 1 2 1840000 38 120 15 1 2 0 13 0 1 2 1240000 39 175 47 2 2 1 10 1 1 2 2340000 40 73 23 2 2 1 7 1 1 1 1120000 41 678 113 3 3 2 11 0 0 3 8320000 42 324 68 2 2 2 21 0 0 2 3940000 43 446 62 2 2 2 14 0 0 2 3800000 44 302 63 2 2 2 13 0 0 2 3820000 - 15 -
  • 18. Appendix B: Full Model Estimation B.1 Result Dependent Variable: LOG(P) Method: Least Squares Date: 05/09/08 Time: 21:40 Sample: 1 44 Included observations: 44 Variable Coefficient Std. Error t-Statistic Prob. LOT -0.001696 0.004084 -0.415317 0.6805 AREA 0.001724 0.000734 2.349958 0.0247 FLOOR 0.105486 0.126646 0.832913 0.4107 BATH 0.237765 0.114812 2.070914 0.0460 BED -0.061554 0.084634 -0.727302 0.4720 CAR 0.197407 0.090087 2.191293 0.0354 DIS 0.010303 0.008971 1.148534 0.2588 NOISE -0.190268 0.098735 -1.927064 0.0624 TOWNHOUSE -0.137883 0.097099 -1.420024 0.1647 C 13.64753 0.279308 48.86199 0.0000 R-squared 0.908205 Mean dependent var 14.96983 Adjusted R-squared 0.883906 S.D. dependent var 0.728276 S.E. of regression 0.248142 Akaike info criterion 0.247087 Sum squared resid 2.093534 Schwarz criterion 0.652584 Log likelihood 4.564094 F-statistic 37.37663 Durbin-Watson stat 2.072298 Prob(F-statistic) 0.000000 B.2 Normality Test 8 Series: Residuals 7 Sample 1 44 Observations 44 6 Mean -7.36e-16 5 Median -0.016962 4 Maximum 0.414774 Minimum -0.543988 3 Std. Dev. 0.220651 Skewness -0.019328 2 Kurtosis 2.545039 1 Jarque-Bera 0.382220 Probability 0.826042 0 -0.4 -0.2 -0.0 0.2 0.4 - 16 -
  • 19. B.3 White Hetero Skcedasticity test B.4 Correlation Matrix - 17 -
  • 20. Appendix C: Reduced Model Estimation C.1 Result Dependent Variable: LOG(P) Method: Least Squares Date: 05/09/08 Time: 21:48 Sample: 1 44 Included observations: 44 Variable Coefficient Std. Error t-Statistic Prob. LOT 0.008716 0.001690 5.157246 0.0000 FLOOR 0.307110 0.097960 3.135064 0.0034 BATH 0.269650 0.113476 2.376263 0.0228 BED -0.182466 0.072202 -2.527166 0.0159 NOISE -0.273050 0.094436 -2.891384 0.0064 TOWNHOUSE -0.187799 0.103229 -1.819250 0.0770 C 13.82623 0.258109 53.56752 0.0000 R-squared 0.883585 Mean dependent var 14.96983 Adjusted R-squared 0.864707 S.D. dependent var 0.728276 S.E. of regression 0.267876 Akaike info criterion 0.348323 Sum squared resid 2.655023 Schwarz criterion 0.632171 Log likelihood -0.663100 F-statistic 46.80482 Durbin-Watson stat 2.022406 Prob(F-statistic) 0.000000 C.2 Normality Test 6 Series: Residuals Sample 1 44 5 Observations 44 4 Mean -1.93e-15 Median 0.002960 3 Maximum 0.522445 Minimum -0.415909 Std. Dev. 0.248485 2 Skewness 0.200434 Kurtosis 2.281225 1 Jarque-Bera 1.241778 Probability 0.537466 0 -0.4 -0.2 -0.0 0.2 0.4 - 18 -
  • 21. C.3 White Hetero Skedasticity test - 19 -