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The Value of Air Quality in Chinese Cities: Evidence from Labor and Property Market Outcomes

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Abstract

Using a dual-market sorting model of workers’ location decisions, this paper studies the capitalization of air pollution in wages and property prices across Chinese cities. To account for endogeneity of air pollution in the determination of wages and property prices, we exploit quasi-experimental variation in air quality induced by a policy subsidizing coal-based winter heating in northern China, and document a discontinuity in average air quality for cities located north and south of the policy boundary. Using data for all 288 Chinese cities in 2011, we estimate an equilibrium relationship between wages and house prices for the entire system of Chinese cities, and specify a regression discontinuity design to quantify how variation in air quality induced by the policy affects this relationship locally. Our preferred estimates of the elasticity of wages and house prices with respect to \(\text {PM}_{10}\) concentration are 0.53 and \({-}\) 0.71 respectively. At the average of our sample, the willingness to pay for a unit reduction in \(\text {PM}_{10}\) concentration is CNY 261.28 (\(\simeq \) USD 40.50), with a significant share reflected in labor market outcomes.

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Fig. 1

Source: NBSC (2012a)

Fig. 2

Source: MEP (2012)

Fig. 3
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Notes

  1. See World Health Organization (WHO 2006). \(\text {PM}_{10}\) represents the part of suspended particles with a diameter smaller than 10 \(\upmu \hbox {m}\). These particles can enter the lungs which, among other things, can cause an increase in the prevalence of cardiovascular diseases (e.g. D’Ippoliti et al. 2003; Tsai et al. 2003). More generally, empirical evidence has shown that air pollution, and in particular \(\text {PM}_{10}\), has significant welfare consequences, among which a negative impact on the overall level of public health (e.g. Chay and Greenstone 2003; Pope and Dockery 2006; Chen et al. 2013; Qiao et al. 2014). Growing evidence also suggests that air pollution affects wider economic outcomes such as worker productivity (Graff Zivin and Neidell 2012), labor supply (Hanna and Oliva 2015), as well as school attendance (Currie et al. 2009).

  2. In China’s administrative structure, a prefectural city is an administrative division ranking below a province and above a county/town. A prefectural city emerges if the administrative subdivision meets the following three criteria: (i) the non-agricultural population in the central urban area is over 250 thousand; (ii) the gross value of industrial output is more than CNY 200 million (around USD 31 million); (iii) tertiary industry’s share is higher than that of the primary industry, and accounts for over 35% of the gross regional production.

  3. See for example Black (1999), Epple and Sieg (1999), Davis (2004), Chay and Greenstone (2005), Linden and Rockoff (2008), and Pope (2008).

  4. In the present context, another benefit of using a regression discontinuity design is that it mitigates concerns about the quality of Chinese air pollution data. While we discuss this issue further below, it is important to note that our identification strategy essentially compares equilibrium market interactions near to the policy boundary, so that our results would be affected by data quality only insofar as cities included or not under the River Huai policy differ in how they report the data (Almond et al. 2009).

  5. Throughout the paper we use an average exchange rate for 2011 of CNY 1 \(\simeq \) USD 0.155.

  6. More specifically, OECD (2014) calculates that, in 2010, deaths attributed to ambient air pollution translate into 24.58 million years of life lost. Based on this, they estimate that the economic cost of outdoor air pollution and associated health impacts is about USD 1.4 trillion.

  7. As in Roback (1982), the use of a representative agent implicitly imposes that all individuals chose their location simultaneously, and that they are identical in tastes and skills.

  8. As suggested in the initial Roback (1982) paper, this approach can be used to construct an index-ranking of cities capturing variations in the quality of life. See for example Gyourko et al. (1999). In this paper we rather focus on estimating the implicit price of air pollution as we were not able to locate plausibly exogenous variations for the set of amenities that would make a city-ranking exercise meaningful.

  9. Starting in 1958, the Hukou policy classifies people into local and non-local residents as well as agricultural and non-agricultural status. This classification was used mainly to grant access to local public services (such as children’ access to public schools), and has thus restricted labor mobility for decades. Importantly however, in the year 2011 we consider the Hukou system did not impose significant restrictions for housing market transactions (see also Zheng et al. 2010).

  10. According to the air quality guidelines from WHO (2006), the lowest level of annual average \(\text {PM}_{10}\) concentrations at which total, cardiopulmonary and lung cancer mortality have been shown to increase is 20 \(\upmu \hbox {g}/\hbox {m}^3\). There are also three intermediate targets of \(\text {PM}_{10}\). At 30 \(\upmu \hbox {g}/\hbox {m}^3\) the long-term risk of premature mortality increases by around three percent, at 50 \(\upmu \hbox {g}/\hbox {m}^3\) the risk increases by around 10 percent, and at 70 \(\upmu \hbox {g}/\hbox {m}^3\) the risk is around 15 percent higher.

  11. Because suspended particles move with wind, we have checked for any systematic wind patterns in cities located within 2 degrees’ latitude around the Huai River (the data source is lishi.tianqi.com). Among this subset of 55 cities, data indicate that 27 have no prevailing wind direction, 10 have east as their prevailing wind direction, 13 have southeast, 3 have south, 1 has west and 1 has northeast. This very heterogeneous pattern, with little evidence of systematic north/south dispersion, is in line with discontinuity in PM10 concentration reported in Almond et al. (2009) and Chen et al. (2013).

  12. All IV regressions are estimated with limited information maximum likelihood (LIML), as this approach is generally more reliable than two stage least square (TSLS). We report critical values of the Cragg–Donald statistics in the notes of the result tables. Note that TSLS estimates are, however, very similar to LIML estimates reported here.

  13. Table 3 again reports LIML estimates (with critical values for the Cragg–Donald test statistics reported in the notes), although as for the wage equations the TSLS estimates are very similar to LIML.

  14. According to the 1982 Constitution of China, land is publicly owned and private ownership is legitimately prohibited.

  15. As mentioned above, our regression discontinuity strategy generates a local estimate. It is therefore important to emphasize that we are extrapolating it assuming that the elasticity is constant across all cities in China.

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Authors and Affiliations

Authors

Corresponding author

Correspondence to Bruno Lanz.

Additional information

We would like to thank Souvik Datta, David Good, and Wei Hu, as well as participants at the 2015 EAERE meeting in Helsinki for useful comments and discussions. Funding from the China Scholarship Council is gratefully acknowledged. Any remaining errors are ours.

Appendices

Appendix A: Data Sources and Summary Statistics

Variable

Definition

Mean

SD

p10

p25

p50

p75

p90

Source

Wages

Average yearly wages (1000 CNY/Year)

35.96

8.24

27.02

30.48

34.62

39.81

47.05

NBSC (2012a)

Male

Share of population: male (%)

52.77

8.80

42.48

50.20

52.43

57.93

62.51

NBSC (2012b)

College

Share of population: college graduates (%)

8.10

4.85

3.93

5.02

6.73

8.98

15.07

NBSC (2010)

Unemployment

Unemployment rate (%)

3.30

0.74

2.20

2.80

3.50

3.90

4.20

NBSC (2012a)

Migrants

Share of population: immigration (%)

21.64

32.78

6.40

8.62

13.24

22.39

42.46

NBSC (2010)

House prices

Average house prices (1000 \(\hbox {CNY}/\hbox {m}^2\))

4.12

2.47

2.40

2.73

3.38

4.37

6.68

NBSC (2012a)

Variable

Definition

Mean

SD

p10

p25

p50

p75

p90

Source

Piped water

Share of houses with piped water (%)

63.25

21.46

35.00

45.00

61.50

83.00

93.00

NBSC (2010)

Fitted toilets

Share of houses with toilet (%)

70.68

16.50

49.00

58.00

73.00

84.00

90.00

NBSC (2010)

Fitted shower

Share of houses with shower (%)

51.19

22.79

18.00

32.50

52.00

67.50

81.00

NBSC (2010)

Density

Population density (1000 persons /\(\hbox {km}^2\))

0.47

0.54

0.08

0.18

0.34

0.62

0.87

NBSC (2012a)

Land supply

Traded land area (100 \(\hbox {km}^2\))

0.13

0.42

0.02

0.04

0.07

0.12

0.22

CLRA (2012)

Coastal

Indicator equal to 1 if city is on the coast

0.09

0.28

0.00

0.00

0.00

0.00

0.00

NGCC (2012)

Universities

Number of universities per 10,000 residents

0.01

0.01

0.00

0.01

0.01

0.01

0.02

NBSC (2012a)

\(\text {PM}_{10}\)

Average \(\text {PM}_{10}\) concentration (\(\upmu \hbox {g}/\hbox {m}^3\))

77.44

19.11

53.00

64.00

78.00

91.00

100.00

MEP (2012)

\(\hbox {Polluted days}^{\mathrm{a}}\)

Number of days with API \(\ge \) 100

21.94

21.59

0.00

4.50

17.00

34.00

48.00

NBSC (2012a)

Huai policy

Indicator equal to 1 if city is included in the River Huai policy

0.43

0.50

0.00

0.00

0.00

1.00

1.00

NGCC (2012)

Latitude

Distance to latitude \(33^{\circ }\) (degree \(^{\circ }\))

\(-\) 0.06

6.67

\(-\) 9.27

\(-\) 5.17

\(-\) 0.56

4.71

8.80

NGCC (2012)

Temp mean summer

Mean temperature in summer (\(^{\circ }\mathrm {C}\))

26.10

2.87

22.24

23.66

26.85

28.32

29.37

CMA (2012)

Temp mean winter

Mean temperature in winter (\(^{\circ }\mathrm {C}\))

1.91

8.34

\(-\) 9.62

\(-\) 3.04

3.27

6.83

13.16

CMA (2012)

  1. 288 observations
  2. \(^{\mathrm{a}}\)Definition of API is in Appendix B. Exchange rate for 2011: CNY 1 \(\simeq \) USD 0.155

Appendix B: Definition of the Air Pollution Index (API)

The conversion method from pollutant concentrations to API values is available from the website of China’s Ministry of Environmental Protection. First, average concentration of air pollutants are reported from the monitoring stations in each city (cities with a population of over 3 million people are required to use at least eight monitoring stations to measure urban air quality). Specifically, concentrations of \(\text {PM}_{10}\), \(\hbox {SO}_{2}\) and \(\hbox {NO}_{2}\) are measured with daily averages.

The API is then constructed from piecewise linear indexes computed for each pollutant. Conversion of concentrations into pollutant-specific indexes is as follows:

$$\begin{aligned} I_k= \frac{I_{{ high}} - I_{{ low}}}{C_{{ high}} - C_{{ low}} }\left( C_k -C_{{ low}}\right) + I_{{ low}} \end{aligned}$$
(B1)

where \(I_k\) is the pollution index of pollutant k, \(C_k\) is pollutant k’s concentration, \(C_{{ low}}\) is the concentration threshold below \(C_k\) (defined in Table 4), \(C_{{ high}}\) is the concentration threshold above \(C_k\), \(I_{{ low}}\) is the index threshold corresponding to \(C_{{ low}}\), and \(I_{{ high}}\) is the index threshold corresponding to \(C_{{ high}}\). The API then represents the highest value of those indexes:

$$\begin{aligned} \hbox {API} = \hbox {max} \left( I_{PM_{10}},I_{SO_2} ,I_{NO_2}\right) \end{aligned}$$
(B2)

Note that the scale for each pollutant is non-linear, as is the final API value. An implication is that an API of 100 is not equivalent to a doubling of air pollution associated with an API of 50.

Table 4 Air pollution index (API).

As shown in Table 4, an API of 100 is regarded as the threshold of air pollution that can lead to non-negligible health consequences. Thus days with an API under 100 are defined as a “Blue Sky” days (i.e. days in which air pollution poses little or no risk to human health). When the API is between 101 and 200, air pollution may generate slight irritations to breathing and lead to heart diseases. When API is between 201 and 300, air pollution will aggravate the symptoms of patients with cardiac and lung diseases, even healthy people will be noticeably affected. When API is above 300 air is severely polluted and may cause irritations and other symptoms. People are advised to avoid outdoor activities.

Appendix C: First Stage Regression Results

Table 5 First stage results for pollution in the wages equation (Table 2)
Table 6 First stage results for house prices in the wages equation (Table 2)
Table 7 First stage results for pollution in the house prices equation (Table 3)
Table 8 First stage results for wages in the house prices equation (Table 3)

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Huang, X., Lanz, B. The Value of Air Quality in Chinese Cities: Evidence from Labor and Property Market Outcomes. Environ Resource Econ 71, 849–874 (2018). https://doi.org/10.1007/s10640-017-0186-8

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