Considering the above analysis throughout the cases and the negative factors influenced them, gives a hint for Chinese cities in the main research question. Therefore, the main hypothesis for this dissertation can be formulated based on their results.
H1: Lower air quality will lead to a decline on inbound tourism of Chinese cities.
Furthermore, the cases also showed there is a time period of recovery of more or less one year, leaving the necessity to detect if the recovery time also exist in the case of air pollution. Meanwhile, in line with the similar cases, it is also logical to postulate similar time lag as those cases. Therefore, the time-lagged effect will also be detected.
H1.1: Lower air quality in the previous year will result in a decline of inbound tourism of Chinese cities in the current year.
Moreover, it leaves a curiosity whether the negative publicity will have an impact on tourism as well, because it showed in the case of Singapore and Johannesburg a significant influence on tourism demand but not in the case of New Orleans. So it is necessary to confirm or dismiss this impact for air quality. In the sense that more media publicity available for the tourists, the more possible impact it will generate, and since air pollution itself is seen as a negative incident, the second hypothesis will be logically formulated as follows:
H2: More media publicity of air pollution will lead to a decline on inbound tourism of Chinese cities.
Similarly, since there might be a time-lagged impact of sulfur dioxide, it is also reasonable to make a hypothesis about media publicity.
H2.1: More media publicity of air pollution in the previous year would lead to a decline of tourism in the current year.
Furthermore, media publicity might be a moderating variable of air quality to enlarge influence on tourism demand. Therefore, it is going to be examined as well.
The model building up in Chapter 4 will assist to test the hypothesis formed above, in order to find out an answer to how the air quality will affect inbound tourism to Chinese cities. Thus, the next chapter will elaborate how the empirical model will be constructed and what variables will be selected.
Chapter 4 Empirical Models
From the previous chapters, the theoretical review has indicated that air pollution might have an impact on tourism demand, thus in order to test the hypothesis, a quantitative model will be constructed. The method used to analyze data will be introduced in Section 4.1, the necessity and benefit of applying certain method will be explained. The entire dataset will be used for the estimation will be described 4.2, in its sub section, the definition of all the variables and the reasons of inclusion or exclusion of each control variable will be elaborated. Finally, the empirical model for testing the main hypothesis is going to be formulated in 4.3.
4.1 Method
A time series data covering 31 Chinese cities from mainland of China and their annual statistics from 2005 to 2012 are collected into the database. Thus two dimensions are included in this panel data set – different cities and years. Regarding to the research question, the tourism demand changes over years in the same cities are going to be investigated, the within effect is meaningful for reaching the conclusion. Thus a fixed effect transmission is necessary in order to acquire within estimators, and an OLS regression will be specified in this panel dataset.
As mentioned previously, there are many factors influencing tourism of a city, and obviously they cannot be all included in the estimation. The important factors of making estimation in a panel dataset are what have (been) changed over the years during the observation. Meanwhile, a lot of characteristics of cities cannot be observed, which can be constant existing but also temporary appealing, probably also give an impact on international visitors, however, they are too complex to be exhausted exploring. A fixed effect estimation itself can partly eliminate these unobserved characteristics, meanwhile, time-demeaning variables can facilitate to control them, thus 9 year dummies will be added into this fixed effect estimation. Some variables explicitly keeping constant over time will be excluded.
Additionally, in order to support that the fixed effect estimation is the more preferable method for this panel dataset, a Hausman test will be conducted to seek for any significant difference it created between the fixed and random effect estimations.
All the estimation equations and inference tests in this dissertation will run in the software named STATA.
4.2 Data 4.2.1 Description
CEIC China premium database is the major source of data for this dissertation, and the Internet searching engine Bing.com is the other source used for data collection. As mentioned, the complete database included 31 Chinese cities and correspondent data in the city level. These cities are the capitals of the provinces of China mainland, which play leading roles in the international tourism market because of better accessibility and business opportunity. They are representatives of the other cities, and their successes or failures can be leading cases for the others to learn. Meanwhile, the time span of 2005 to 2012 is chosen, indicating that eight years of annual statistics will be used into the analysis.
Note that tourists from the Special Administration Regions – Hong Kong and Macau, and Taiwan Province current ruled by Kuomintang, are not included in this research, in order to avoid confusion and acquire more accurate estimated results for inbound tourism to Chinese cities. This group has to be distinguished from the other ‘pure’ international visitors. Travelling to China is easier for them than the other overseas tourists, because they have much stronger attachment (nationality, language, culture commitment, and etc.) with the mainland regions. Although statistical departments record them as international tourists, they are unique and they actually belong to neither domestic nor international category. To investigate the difference between this group and other overseas international tourists will be interesting as well, but unfortunately precise statistical numbers for SAR tourists in city level are missing, they are recorded only in Beijing, Shanghai and Guangzhou.
4.2.2 The dependent variable
Tourist Arrival
Tourist arrivals will be used as the dependent variable to measure inbound tourism, in fact, in the researches recent years, it has been the most popular factor adopted of measuring the tourism demand (Song & Li, 2008). In the review study of Li, Song and Witt (2005), they discovered that in the majority of the previous studies of tourism demand, researchers frequently used tourism expenditure or tourist arrivals as the dependent variable, while a few other dependent variables were used in the minority, such as budget share of tourism expenditures, tourism imports and exports, numbers of nights.
Considering the database can be accessed, the tourist arrivals will be the most suitable dependent variable for this dissertation. While following the common sense that larger city are usually better known, the size of city may influence the tourist arrivals. Thus a correction should be applied. In each year, the city’s population will divide tourist arrivals, in order to eliminate the effect of city size. Population size is counted on per thousand basis.
4.2.3 The independent variables
Inclusion
The following variables listed will be included into the estimation equations going to be made, and the details of these variables will be illustrated one by one.
-
Sulfur dioxide
-
Media publicity
-
Foreign direct investment
-
Hotels
-
Mega events
-
Property Price
Sulfur Dioxide
This is the most important independent variable because it measures air quality, confronting the essence of the main research question.
In Chapter 2, it indicated that the concentration of PM 2.5 can measure air quality as well, and many countries (U.S. and western European countries) have adopted it as a measurement, called AQI (air quality index), measuring how microgram of PM 2.5 concentrated in the air per cubic meter on average. However, AQI had not accepted by the official department of China Environment Protection as an indicator of air quality before 2014. Meanwhile, PM 2.5 is a relatively new concept to Chinese public, most of websites provide real time statistics for each city, and historical data is rare. A Chinese website2 provides historical data from October 2013, but no data available from 2005 to 2012, indicating that there is not sufficient data to sustain a reliable result of estimation. Moreover, the official measurement of air quality in China was API, abbreviated for air pollution index; the difference between it and AQI is that API is measuring the concentration of PM 10. Some historical data of API can be pursuit in the website of Ministry of Environmental Protection of PRC3, but lack of completeness for the entire needed time span (2005 to 2012) will deteriorate the reliability of estimation, thus it is not adopted as well, unfortunately.
Finally, the annual emission of sulfur dioxide on thousand tons basis for each prefecture city was found in CEIC database, thus it is adopted in this empirical model as the indicator of air quality. Sulfate, mostly sulfur dioxide, which has been discussed in Section 2.5.1, is an important composition of air pollutant PM 2.5. It can be a proxy of measurement because they are in the same direction, more sulfur dioxide probably causes more PM 2.5 generation. Comparing with PM 2.5, this proxy might have less visible to the public, since it does not directly reported by media. It might lead the influence of media publicity is overestimated.
Still, the emission of sulfur dioxide is an appropriate proxy, since sulfur dioxide influences the air quality. It thus will also influence tourists’ behavior and decisions, since it is a threat to human’s health, e.g. increase the probability of CVD. Similarly to PM 2.5, WHO also set up guidelines for sulfur dioxide, which duration of exposing to sulfur dioxide more than 500 micro gram per cubic meter on average should not exceed 10 minutes (World Health Organization, 2006).
There is no need for city-size correction because it is not definite that bigger city will generate more sulfur dioxide based on the evidence found about PM 2.5, the cities in north are more polluted than the south, but both north and south have big cities.
In addition, since time lagged effect of air pollution is also going to be investigated, the one-year lagged value of sulfur dioxide will be also included as a independent variable.
Media publicity
Confronting with the second hypothesis, media publicity of air pollution has to be included. There is no definite way to measure this variable, or quantify it. In this research, it is assumed that more media publicity will generate more impact on tourists, so the number of information available would be an appropriate method for measurement. Therefore, certain terms were searched in the Internet searching engine Bing.com, and the total numbers of results found were recorded. The terms used to search were following the structure as “City name +’air pollution’ + year”, for example:
Beijing “air pollution” 2005
The result of this search includes all the webpages mentioned Beijing, air pollution and 2005, but also perfectly matched the order of the words “air pollution”. Likewise, Beijing can be replaced by Tianjin, Shanghai, or any other cities needed, and 2005 should be altered by 2006, 2007 till 2012.
Note that using different searching engine like “Google” and “Bing” will get different results. The results from google.com were not adopted because they sometimes were not comparable, and bing.com gave more stable results. Besides, searching in a different time and different PC will also lead to a distort result. To clarify, the data used in this dissertation was collected on 14th August 2014, in a laptop with a Chinese PC system.
This proxy of measuring media publicity is rough, and has several limitations need to be pointed out. First, it included every webpage mentioning these terms, but not the actual number of people’s hits. There might be some webpages never get a hit, which indeed have no impact on tourists, but are still counted into the result. Google Trends gives the comparable trend over years based on the number of hits, but for some cities which are cleaner in common sense, are rarely generate hits, and therefore cannot produce enough data to be used as a variable. Another database named LexisNexis was also used to attempt to get news published in certain years, but it was found the same problem as Google Trends.
Second, using the year “2005…2012” directly does not show the webpage reported air pollution in 2005. Instead, every webpage mentioned 2005 will be included, but people cannot reach a webpage published in 2008 but mentioned 2005 before 2008. Furthermore, there will be increasing number of webpages mentioning terms like 2005, because people are keeping publishing, but they are not available for previous searching as well. Since the actual number of webpages published in a certain time period is not shown in both Google and Bing, as a result, the data collected is more than actual webpages existed at that year.
Third, the Internet is just one of the mass media channels, other information sources, such as the local newspapers, are excluded from the results. However, newspapers is much more reachable for aged people than the Internet.
Fourth, this result might have excluded the information sources for non-English speakers. Even though major components of international tourists understand English, niche markets cannot be neglected, for example, Urumqi receives a lot of visitors from middle Asia countries, and they communicate by Uyghur language. Together with the third limitation, the data collected is less than the actual information available.
Additionally, most of webpages mentioned air pollution discussed about PM 2.5, but annual emission of sulfur dioxide will be used as the independent variable in the following analysis. It created a slight inconsistency, because most tourists probably search terms like “air pollution” “PM 2.5” or “air pollutant”, but not “sulfur dioxide emission” when they want to prepare for their travels. But as stated above, it is a pity that the data of PM 2.5 is not sufficient to be adopted in the estimation.
Combining all the limitations above, it is difficult to judge the number in the database is larger or smaller than what can be reached in reality, but it is an indication of the intensity of media publicity, since more information published the more probable people will be influenced.
Foreign Direct Investment
It is an indicator referring to market ties. In the previous context we measured it by GDP. FDI and GDP are all economic indicators, which can be used as proxy of market ties. Figure 6 depicts GDP (in billion Chinese Yuan) and FDI (in million US dollar) for all Chinese prefecture level cities from 2005 to 2012. It is clear that they are positively correlated, which suggests that only one of these two indicators can be included in the estimation model.
Figure 6: GDP and FDI for all prefecture level cities in China from 2005 to 2012
Source: CEIC China Premium Database (2014)
FDI is chosen instead of GDP in the sense that more FDI in the city, more business visits would generate. GDP can be seen as a potential of more business opportunities, but FDI is the business has already done, which have a stronger connection with the actual business trips of international visitors took place in that time period.
The data of FDI for each city from 2005 to 2012 comes from CEIC China Premium Database. The total capital utilized for each year is recorded and counted in million US dollar. Additionally, it is also corrected by the city size (population).
Hotels
Accommodation is always important of travelling arrangement. It has been discussed that international visitors prefer qualified hotels, which indicates that 4-star or 5-stars hotel should be taken into account by measuring international tourism demand. However when looking for the data of 4 and 5-star hotels, there are still some values missing. In CEIC China Premium Database, the number of all registered hotel in the city is found, thus it is adopted as a proxy of qualified accommodation. It is also corrected by the city size (population).
Mega Event
As stated in Section 2.2.3, China started to participate holding mega events. To control the impact of mega event on tourism demand, this is set up as a dummy variable. If the city held a mega event in the year, then its value equal to 1, otherwise equal to 0. There are two mega eents took place in Chinese cities in time span from 2005 to 2012, which are Beijing Olympics 2008 and Shanghai Expo 2010. Value for Beijing in the year of 2008 and Shanghai in the year of 2010 equal to 1, all the rest cities in the rest years equal to 0.
Property Price
Price level of the destination also has impact on tourism demand, because the basis of demand and supply relationship suggests a higher price leads to a lower quantity. An expensive destination, to some extent, probably will keep tourists away, and vice versa.
The best variable for the price level of tourism is Consumer Price Index (CPI), because tourism activities covers a wide range of consumer products, and CPI is the one that comprehensively evaluated the price level in a certain place. It is a surprise that a comprehensive CPI is difficult to find. CEIC provides retail prices for agricultural, food, industrial, consumer goods, and service charges in very details (e.g. daily price of eggs per kilo), but they are average values in the country level. The only prefectural level data is only available for property price, so it is taken as a proxy of consumer price level. It is counted based on Chinese Yuan per square meter.
Property price can be relevant to tourists’ expenditure, because hotel price is largely influenced since they are both related to real estate sector. Accommodation expenditure also has great proportion in total travel expenses, so property price can partly represent how expensive a destination is. The limitation of this proxy is obvious, it ignores the prices of other tourist products. However it is still difficult to include every product the tourists might consume, so another two representatives are picked up. The retail price of egg is an indicator of normal food expense, and the price of taxi per kilometer is an indicator of service/transportation expense. Figure 7 illustrates the changes of price level for property, egg and taxi in Chinese cities from 2005 to 2012(price in Jan 2008 equals to 1). It shows that property price has a greater increase than the other two products, and taxi price almost remains stable over years. Thus taking property price as a proxy of price level may lead to overestimation of the impact of price level on tourism demand.
Figure 7: Price changes of property, egg and taxi over years
Source: CEIC China Premium Database (2014)
The above-mentioned variables are all needed for building up the estimation model for this dissertation. Table 8 presents all the variables and their units, when model is being specified in Section 4.3, for simplicity, they will be mentioned by their abbreviated name.
Table 8: List of selected variables
Function
|
Name
|
Abbreviation
|
Unit
|
Remarks
|
Dependent variable
|
Tourist arrivals
|
TA
|
Thousand people
|
Corrected by city size
|
Independent variable
|
Sulfur dioxide
|
SD
|
Thousand tons
|
|
1-year lagged sulfur dioxide
|
SD_1
|
Thousand tons
|
|
Media publicity
|
MP
|
Thousand results
|
|
1-year lagged media publicity
|
MP_1
|
Thousand results
|
|
Foreign direct investment
|
FDI
|
Million US Dollar
|
Corrected by city size
|
Hotels
|
Hotel
|
Unit
|
Corrected by city size
|
Mega Event
|
ME
|
N/A
|
Dummy variable
|
Property price
|
PP
|
Thousand Chinese Yuan / square meter
|
|
Source: own elaboration
Exclusion
Likewise, the following variables are excluded from this research; the reasons will also be explained for each of them.
-
Trade-weighted effective exchange rate index (BIS)
-
Number of heritages
-
Transportation cost
-
Airport ranking
-
Income of tourists from origins
Trade-weighted effective exchange rate index (BIS)
BIS is an overall exchange rate index that complies weighted average of exchange rate of home currency against foreign currencies with the weight of each foreign country equal to its share in trade. Exchange rate between Chinese Yuan and other currencies is another determinants of how expensive for travelling in Chinese cities, which can be seen as a composition of price level, indicating an impact on tourism demand.
In fact, the exchange rate has changes quite an extent in these years, due to the financial crisis in western countries and strong performance of Chinese economy. Table 8 illustrated the changes of BIS over years, which can be found a trend of appreciation of Chinese Yuan.
Table 9: BIS of Chinese Yuan from 2005 to 2012 (2010=100)
Year
|
2005
|
2006
|
2007
|
2008
|
2009
|
2010
|
2011
|
2012
|
BIS
|
87.2467
|
89.24
|
90.38197
|
96.37333
|
102.0108
|
100
|
100.0833
|
105.6792
|
Source: CEIC China Premium Database (2014)
The reason of dropping it is that BIS is an universal number for every city. Although it changes over years, but in this sense it can only explain the changes in the number of visitors in different years, which occurs in all cities. Meanwhile, as time-demeaned variables are added, which already have caught characteristic differs over the years but remains the same for every city; BIS as such a variable is not necessarily to be added into the model.
Number of heritages
Cultural and natural heritages are important attractions for international tourists. It is not picked into the model because the number of heritages keeps constant over time, because they cannot be created. In panel data estimation, this type of effect is automatically omitted because the impact does not change.
Transportation cost
Lower transport cost leads to an expansion of tourism – it might be true for short distance international travelling, like a city break travel in European countries. For example, the introduction of low-cost airline in Alghero significantly boosted the number of tourists, because of reduction of transportation cost resulted from greater accessibility (Pulina & Cortes-Jimenez, 2010). However, it is inferred not applicable for travelling to Chinese cities, because expense on air transport is always generating the most transportation cost, and the ticket prices from Europe or US to China do not differ too much. Another reason to exclude it is the difficulties of data collection, because ticket prices vary in a large range, and depend on many factors, e.g. booking time prior to travel date, the airline company selected, the travel agency contacted.
Airport ranking
Since accessibility is one of the major determinants of destination attractiveness, the existence of international airport and how many passengers it receives seem that need to be taken into account.
However, it is not selected because of two reasons. First, it might become a dominant variable, which causes other variables to become insignificant because it has too strong impact. A large number of incoming passengers mean either that the airport has many connections, or that it is located in a city that attracts many tourists; it is difficult to distinguish what resulted a high rank of airport.
Subsequently, even if you could construct a variable that exactly measures the number of destinations reachable from an airport, it would probably suffer from endogeneity. For example, if a city attracts many tourists in the previous year, its airport is likely to have a bigger number of destinations in the next year to cope with the high number of incoming tourists. Endogeneity is a problem of causation, it keeps unknown that whether an accessible airport causes more visitors to come to the city, or whether more visitors coming to the city causes the airport to become more accessible by having an increased number of connections/destinations. Therefore, it is very difficult to add a variable for transport into the estimation.
Income of the tourists from origins
In the previous discussions, the property prices of Chinese cities are included as a sign of travel expenses in China, which will matter for destination selection. If the expenses of travelling to Chinese cities are far more than the price they can afford, then tourists will visit other places instead. The affordability is certainly linked to income, in this case, is income of the tourists from the origins. However, since the origins cover all over the world, the types of inbound tourists are diversified, and the proportion of different types varies across different years, and again very detailed data is needed because 31 Chinese cities received different numbers of tourists. Therefore, it is very difficult to find an appropriate proxy to measure their incomes, or to find a suitable weighted factor to leverage all those incomes in one variable. In order to avoid disturbance of model reliability, this variable have to be left out.
It does not mean that there is no indication of how expensive the Chinese cities are for international visitors; a rough comparison could be a note for this variable. The Big Mac Index is useful to compare the price level across the countries. Besides the meanings of the other economic meanings behind, another reason for presenting the price of Big Mac is that it directly reflected the price of a Big Mac hamburger in McDonald, the most popular food in the world, which could possibly be a purchase of international tourists in China when they get tired of Chinese cuisine, which tastes very different from food from other parts of the world, and want a bite of ‘taste of home’ (for Americans) or something they are familiar with.
Regarding the origins, albeit there are many, six origins can still be the representatives to make comparisons of price levels with China. South Korea, Japan, Russia, the United States, Malaysia and Singapore have always been the origins contributing the most numbers of inbound tourists to China from 2007 to 2012 (Travel China Guide, 2012). The prices of a Big Mac from 2005 to 2012 were listed in Table 10, and China is also included for comparison purpose. The value in one month of each year is selected because McDonald usually does not adjust price of Big Mac too much during the year, and naturally, all the prices have been already adjusted to the same currency – US Dollar. From Table 10 it can be discovered that the price of Big Mac in China is the lowest among all these countries with just a few exceptions. Therefore, it gives an indication that China is not an expensive destination for the major groups of international tourists.
Table 10: The prices of a Big Mac hamburger (in USD)
Year
Country
|
2005
|
2006
|
2007
|
2008
|
2009
|
2010
|
2011
|
2012
|
China
|
1.27
|
1.30
|
1.41
|
1.83
|
1.83
|
1.95
|
2.27
|
2.44
|
South Korea
|
2.49
|
2.56
|
3.08
|
3.14
|
2.39
|
2.82
|
3.50
|
3.19
|
Japan
|
2.34
|
2.19
|
2.31
|
2.62
|
3.23
|
3.67
|
4.08
|
4.08
|
Russia
|
1.48
|
1.60
|
1.85
|
2.54
|
1.73
|
2.33
|
2.70
|
2.55
|
United States
|
3.06
|
3.15
|
3.22
|
3.57
|
3.54
|
3.73
|
4.07
|
4.20
|
Malaysia
|
1.38
|
1.47
|
1.57
|
1.70
|
1.52
|
2.19
|
2.42
|
2.34
|
Singapore
|
2.17
|
2.20
|
2.34
|
2.92
|
2.61
|
3.08
|
3.65
|
3.75
|
Source: (The Economist, 2005; The Economist, 2006; The Economist, 2007; The Economist, 2008; The Economist, 2009; The Economist, 2010; The Economist, 2011; The Economist, 2012)
The limitation of taking income out of the estimation is that it might lead to an overestimation of the impact from other variables, since the income and tourist arrivals are positively related. However, because of the difficulties mentioned previously, the inclusion of this variable can be a topic of further research.
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