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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Public Health</journal-id>
<journal-title>Frontiers in Public Health</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Public Health</abbrev-journal-title>
<issn pub-type="epub">2296-2565</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fpubh.2021.789510</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Public Health</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>How Air Quality Affect Health Industry Stock Returns: New Evidence From the Quantile-on-Quantile Regression</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Liu</surname> <given-names>Lu</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1457722/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Wang</surname> <given-names>Kai-Hua</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x0002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1181554/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Xiao</surname> <given-names>Yidong</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>School of Management, Ocean University of China</institution>, <addr-line>Qingdao</addr-line>, <country>China</country></aff>
<aff id="aff2"><sup>2</sup><institution>School of Economics, Qingdao University</institution>, <addr-line>Qingdao</addr-line>, <country>China</country></aff>
<aff id="aff3"><sup>3</sup><institution>Graduate School of Economics, The University of Tokyo</institution>, <addr-line>Tokyo</addr-line>, <country>Japan</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Tsangyao Chang, Feng Chia University, Taiwan</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Xin Li, Shanghai Jiao Tong University, China; Ran Tao, Qingdao Municipal Center for Disease Control and Prevention, China</p></fn>
<corresp id="c001">&#x0002A;Correspondence: Kai-Hua Wang <email>937276847&#x00040;qq.com</email></corresp>
<fn fn-type="other" id="fn001"><p>This article was submitted to Health Economics, a section of the journal Frontiers in Public Health</p></fn></author-notes>
<pub-date pub-type="epub">
<day>23</day>
<month>12</month>
<year>2021</year>
</pub-date>
<pub-date pub-type="collection">
<year>2021</year>
</pub-date>
<volume>9</volume>
<elocation-id>789510</elocation-id>
<history>
<date date-type="received">
<day>05</day>
<month>10</month>
<year>2021</year>
</date>
<date date-type="accepted">
<day>11</day>
<month>10</month>
<year>2021</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2021 Liu, Wang and Xiao.</copyright-statement>
<copyright-year>2021</copyright-year>
<copyright-holder>Liu, Wang and Xiao</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<abstract><p>This paper discusses the asymmetric effect of air quality (AQ) on stock returns (SR) in China&#x00027;s health industry through the quantile-on-quantile (QQ) regression method. Compared to prior literature, our study provides the following contributions. Government intervention, especially industrial policy, is considered a fresh and essential component of analyzing frameworks in addition to investors&#x00027; physiology and psychology. Next, because of the heterogeneous responses from different industries to AQ, industrial heterogeneity is thus considered in this paper. In addition, the QQ method examines the effect of specific quantiles between variables and does not consider structural break and temporal lag effects. We obtain the following empirical results. First, the coefficients between AQ and SR in the health service and health technology industries change from positive to negative as AQ deteriorates. Second, AQ always positively influences the health business industry, but the values of the coefficients are larger in good air. In addition, different from other industries, the coefficients in the health equipment industry are negative, but the values of the coefficients change with AQ. The conclusions provide important references for investors and other market participants to avoid biased decisions due to poor AQ and pay attention to government industrial policies.</p></abstract>
<kwd-group>
<kwd>air quality</kwd>
<kwd>stock return</kwd>
<kwd>health industry</kwd>
<kwd>quantile-on-quantile method</kwd>
<kwd>heterogeneity</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="2"/>
<equation-count count="7"/>
<ref-count count="100"/>
<page-count count="13"/>
<word-count count="8989"/>
</counts>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="s1">
<title>Introduction</title>
<p>Human health, which is one of the essential dimensions of and signs in sustainable development, is the comprehensive embodiment of social, economic, and physical conditions (<xref ref-type="bibr" rid="B1">1</xref>, <xref ref-type="bibr" rid="B2">2</xref>). However, human health is now confronting great challenges from the air quality problem, and the vast majority of the literature has confirmed this adverse effect (<xref ref-type="bibr" rid="B3">3</xref>&#x02013;<xref ref-type="bibr" rid="B6">6</xref>). In 2015, more than 9 million premature deaths worldwide were due to air pollution, which is much higher than the number of deaths from wars and other violence (<xref ref-type="bibr" rid="B7">7</xref>). In particular, air pollution influences human health through acute health effects, chronic health effects, and intervention effects (<xref ref-type="bibr" rid="B8">8</xref>). In addition to health problems, air pollution also results in total welfare losses and has a negative influence on economic activities (<xref ref-type="bibr" rid="B8">8</xref>, <xref ref-type="bibr" rid="B9">9</xref>). The health care costs triggered by air pollution are expected to reach 176 billion U.S. dollars in 2060, and 3.7 billion working days are expected to be lost. In addition to the traditional focus on human health and economic performance, more attention has been given to financial markets, especially stock markets. Air pollution changes investors&#x00027; moods and their trading behaviors and finally has a negative influence on stock returns (SR) (<xref ref-type="bibr" rid="B10">10</xref>&#x02013;<xref ref-type="bibr" rid="B12">12</xref>). Prior studies have mainly focused on air pollution and emphasized that SR is impacted by poor air quality (AQ). However, investors and other participants cannot be affected by only polluted air and should further consider the effects of good AQ. The good weather, such as sunshine, has been proved to be positively correlated with stock returns in London, Singapore, New York, and other major stock markets (<xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B14">14</xref>). As for good air quality, it would make people feel optimistic relax for future economic performance (<xref ref-type="bibr" rid="B15">15</xref>), and tend to risk-taking behaviors, which changes their trading activities in stock market (<xref ref-type="bibr" rid="B16">16</xref>&#x02013;<xref ref-type="bibr" rid="B19">19</xref>). Our paper depends on AQ data and the quantile-on-quantile method to capture heterogeneous responses from stock returns to healthy and unhealthy air quality at the same time, which could provide more valuable referential policy implications for market participants.</p>
<p>There are multiple explanations for the relationship between AQ and SR in China&#x00027;s health care industry. First, China is a rapidly developing country and suffers serious environmental problems (<xref ref-type="bibr" rid="B20">20</xref>&#x02013;<xref ref-type="bibr" rid="B23">23</xref>). In 2020, China emitted 9.89 billion tons of carbon dioxide (CO<sub>2</sub>), 3.7 million tons of sulfur dioxide (SO<sub>2</sub>), and 11.57 million tons of nitrogen oxide (NOx). Large amounts of CO<sub>2</sub>, SO<sub>2</sub>, NO<sub>x</sub>, and other pollutants influence the environment and further lead to haze and fog, acid rain and other problems. In 2019, China&#x00027;s average PM<sub>2.5</sub> concentration was 39.1 &#x003BC;g/m<sup>3</sup>, which was not only higher than those of the U.S. (9.01 &#x003BC;g/m<sup>3</sup>) and the U.K. (16.6 &#x003BC;g/m<sup>3</sup>) but also exceeded those of Brazil (15.77 &#x003BC;g/m<sup>3</sup>) and Malaysia (19.36 &#x003BC;g/m<sup>3</sup>). Second, air quality, especially air pollution, is an urgent public health problem. Exposure to air pollutants such as PM<sub>2.5</sub> and SO<sub>2</sub> would increase the short-term and long-term risks for diseases (<xref ref-type="bibr" rid="B24">24</xref>). For example, exposure to PM2.5, PM10, NO<sub>2</sub>, and SO<sub>2</sub> results in emergency hospital visits of 3.34, 3.96, 5.90, and 5.38%, respectively (<xref ref-type="bibr" rid="B25">25</xref>). Heyes and Zhu (<xref ref-type="bibr" rid="B26">26</xref>) also show that one standard deviation increases in AQ index and PM<sub>2.5</sub> were associated with &#x0007E;11.6 and 12.8% increases in sleeplessness, respectively. In addition, in cities of Shanghai (<xref ref-type="bibr" rid="B27">27</xref>), Dongguan (<xref ref-type="bibr" rid="B28">28</xref>), Shenzhen (<xref ref-type="bibr" rid="B29">29</xref>), Hefei (<xref ref-type="bibr" rid="B30">30</xref>) and others, the health impacts of air pollution are also found significantly. Although there are apparently many benefits resulting from decreased air pollution, we still cannot address the problem of air pollution effectively. Third, the serious consequences of air pollution are not limited to human health, but also spread to economic fields. Some studies have proved that air pollution changes investors&#x00027; mood and make them do biased decisions, and finally affects the stock market (<xref ref-type="bibr" rid="B12">12</xref>, <xref ref-type="bibr" rid="B19">19</xref>, <xref ref-type="bibr" rid="B31">31</xref>&#x02013;<xref ref-type="bibr" rid="B34">34</xref>). In addition, the existing literature (<xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B13">13</xref>) almost focus on the effect of air pollution on stock return in developed states and regions. Given the serious problem of air pollution more happens in undeveloped countries and regions, significant irrational character in their stock markets, and directly relationship with air quality, we are trying to examine the asymmetric effect of AQ on SR in China&#x00027;s health industry and offer valuable references for investors.</p>
<p>This paper discusses the link between AQ and SR across different health care industries, and we obtain the following results. First, the coefficients between AQ and SR in the health service and health technology industries change from positive to negative as AQ deteriorates. Second, AQ always positively influences the health business industry, but the values of the coefficients in the [0, 0.5] quantile are larger than those in other quantiles. In addition, different from former industries, the coefficients in the health equipment industry are negative, but the values of the coefficients change as AQ changes.</p>
<p>Compared to previous studies, this paper offers some meaningful contributions in discussing the asymmetric effect of AQ on SR in China&#x00027;s stock markets. Government intervention, especially industrial policy, is considered a new and indispensable aspect in explaining the effect of AQ on SR. Prior studies commonly choose investor mood as a major transmission mechanism for interpreting the influences of AQ (<xref ref-type="bibr" rid="B18">18</xref>, <xref ref-type="bibr" rid="B19">19</xref>, <xref ref-type="bibr" rid="B35">35</xref>&#x02013;<xref ref-type="bibr" rid="B37">37</xref>). However, government intervention has been proved to produce significant influence on stock market (<xref ref-type="bibr" rid="B38">38</xref>&#x02013;<xref ref-type="bibr" rid="B40">40</xref>), especially in China (<xref ref-type="bibr" rid="B41">41</xref>&#x02013;<xref ref-type="bibr" rid="B43">43</xref>). For example, China is implementing supply-side reform, which aims to reduce excess capacity and optimize the national industrial structure. Therefore, government intervention should be considered since it can better explain the effect of AQ on SR in China&#x00027;s stock markets. Next, the heterogeneous responses of different health care industries to air quality are sufficiently considered in this paper. Previous studies commonly employ stock market indices, such as the S&#x00026;P Composite Index, to discuss the relationship between AQ and SR (<xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B31">31</xref>, <xref ref-type="bibr" rid="B36">36</xref>, <xref ref-type="bibr" rid="B44">44</xref>, <xref ref-type="bibr" rid="B45">45</xref>). Thus, in order to obtain more accurate results, four subdivided industrial indices, including health services, health equipment, health businesses, and health technology, are chosen as our sample. This can better recognize the heterogeneous responses from different health industries to different AQ levels. Finally, we apply the quantile-on-quantile (QQ) method to explore how air quality influences stock returns across different quantiles. This method combines non-parametric estimation and traditional quantile regression, which can recognize the effects between variables in specific quantiles without considering structural break and temporal-lag effects (<xref ref-type="bibr" rid="B46">46</xref>, <xref ref-type="bibr" rid="B47">47</xref>). Thus, our study focuses on the asymmetric characteristic of the relationship between AQ and SR using the QQ method and obtains more comprehensive results.</p>
<p>The remainder of our paper is constructed as follows. Section Literature Review is the literature review. Section Transmission Mechanism presents the transmission mechanism. Section Quantile-on-Quantile Regression introduces the quantile-on-quantile method. Sections Data and Empirical Results presents the data and empirical results, respectively. Section Conclusion and Policy Implications summarizes the conclusion and policy implications.</p>
</sec>
<sec id="s2">
<title>Literature Review</title>
<sec>
<title>Air Quality and People&#x00027;s Health</title>
<p>The relationship between air pollution and health problems has been found in numerous studies (<xref ref-type="bibr" rid="B48">48</xref>). Torres et al. (<xref ref-type="bibr" rid="B49">49</xref>) indicate that air pollution is related to problems in the cardiovascular and respiratory systems and other adverse side effects. Tainio et al. (<xref ref-type="bibr" rid="B50">50</xref>) suggest that air pollution would reduce physical activity levels or hinder people from joining physical activity during heavy pollution episodes. Dominski et al. (<xref ref-type="bibr" rid="B51">51</xref>) show that long-term and direct exposure to air pollution, such as PM<sub>2.5</sub> and PM<sub>10</sub>, would raise the morbidity and mortality of the population. Giaccherini et al. (<xref ref-type="bibr" rid="B52">52</xref>) discover that air pollution leads to an increase in hospitalizations; and the effect is stronger among older adults, less educated individuals and migrants. Ma et al. (<xref ref-type="bibr" rid="B53">53</xref>) show that reducing PM<sub>10</sub> and PM<sub>2.5</sub> is considered the major way to relieve human health damage, and increased CO<sub>2</sub> levels are responsible for environmental damage. However, Dimitriou and Christidou (<xref ref-type="bibr" rid="B54">54</xref>) and Ngo et al. (<xref ref-type="bibr" rid="B55">55</xref>) demonstrate that there is no obvious relationship between air pollution and human health for residents.</p>
<p>For China, some studies have also started to focus on the link between air quality and health (<xref ref-type="bibr" rid="B56">56</xref>&#x02013;<xref ref-type="bibr" rid="B58">58</xref>). Chen et al. (<xref ref-type="bibr" rid="B59">59</xref>) show that the air pollution from traffic has an obvious negative influence on health status among Shanghai residents. Voorhees et al. (<xref ref-type="bibr" rid="B60">60</xref>) indicate that the estimated avoided deaths due to air pollution has increased from 13&#x0007E;55 cases per year to 300&#x0007E;800 cases per year in Shanghai. Chen et al. (<xref ref-type="bibr" rid="B4">4</xref>) offer evidence for the adverse impacts of air pollution and its spatial spillover effect on public health. Yang and Liu (<xref ref-type="bibr" rid="B61">61</xref>) discover that life satisfaction is positively related to health, and this link is influenced by the effect of air pollution. Huang et al. (<xref ref-type="bibr" rid="B62">62</xref>) show that air pollution is correlated with deaths, and the effects of both daily and durational air pollution can explain the increased disease burden. Chen and Chen (<xref ref-type="bibr" rid="B63">63</xref>) demonstrate that individuals with high incomes, high education and health insurance are more vulnerable to air pollution. Liao et al. (<xref ref-type="bibr" rid="B64">64</xref>) demonstrate that sleep loss due to air pollution has a negative influence on human fitness and further increases personal health costs. Liu and Hu (<xref ref-type="bibr" rid="B65">65</xref>) show that air quality has a significant impact on residents&#x00027; life satisfaction, and both the main pollutants and the overall air quality have a significant negative impact. Wang et al. (<xref ref-type="bibr" rid="B43">43</xref>) discover that the COVID-19 induced lockdown improves air quality, and the expected averted premature deaths due to air pollution declines are around 26,385&#x02013;38,977 during the sample period. Zhou et al. (<xref ref-type="bibr" rid="B66">66</xref>) indicate that the health risk of preterm birth is positively related to exposure to air pollutants, especially PM<sub>10</sub>, PM<sub>2.5</sub>, and SO<sub>2</sub>.</p>
</sec>
<sec>
<title>Air Quality and Stock Return</title>
<p>With the increasing prominence of air pollution and awareness of environmental protection, scholars have gradually paid more attention to the link between air pollution and stock markets. Levy and Yagil (<xref ref-type="bibr" rid="B10">10</xref>) show that air pollution is negatively related to stock returns, but the link weakens as the distance from the polluted area increases. Lepori (<xref ref-type="bibr" rid="B31">31</xref>) argues that air pollution deteriorates individuals&#x00027; moods and intensifies their risk aversion, which reduces demand and lowers stock returns. Kim and Yoo (<xref ref-type="bibr" rid="B67">67</xref>) discover that the effect of cumulative exposure to air pollutants on stock returns and volatility is greater than that of daily exposure. Nguyen and Pham (<xref ref-type="bibr" rid="B34">34</xref>) discover that stock market anomalies become more significant when severe air pollution occurs because air pollution accelerates behavioral biases. However, Andrikopoulos et al. (<xref ref-type="bibr" rid="B68">68</xref>) hold a different opinion that mood changes caused by the weather do not significantly affect stock returns.</p>
<p>Because of increasingly serious air pollution issues, a number of studies have started to pay more attention to the effects of air quality on China&#x00027;s stock markets. Zhang et al. (<xref ref-type="bibr" rid="B11">11</xref>) demonstrate that air pollution has a negative influence on stock returns and a positive effect on stock volatility. An et al. (<xref ref-type="bibr" rid="B36">36</xref>) find that air quality and investor mood are able to influence stock markets separately or jointly. Wu et al. (<xref ref-type="bibr" rid="B69">69</xref>) present that air pollution affects investors&#x00027; sentiment, which makes investors feel pessimistic regarding future stock performance and results in a decrease in stock returns. Wu et al. (<xref ref-type="bibr" rid="B70">70</xref>) demonstrate that poor air quality brings low returns, turnover, and volatility, which mainly result from home bias. Ko et al. (<xref ref-type="bibr" rid="B71">71</xref>) indicate that when the economy is depressed, investors&#x00027; emotions are more easily influenced by air pollution. Wu et al. (<xref ref-type="bibr" rid="B12">12</xref>) show that air pollution leads to a pessimistic mood among stock traders, which influences the prices of their shareholdings. Teng and He (<xref ref-type="bibr" rid="B72">72</xref>) indicate that environmental awareness would produce different influences on investor trading behaviors and corresponding stock prices under different air pollution levels. Liu et al. (<xref ref-type="bibr" rid="B73">73</xref>) find that air pollution is negatively related to the stock prices of polluting companies and positively related to the stock prices of new energy companies. Xu et al. (<xref ref-type="bibr" rid="B74">74</xref>) show that public awareness plays an essential intermediate role in connecting air pollution and stock returns. Ding et al. (<xref ref-type="bibr" rid="B75">75</xref>) show that listed companies present lower stock returns where they are located in cities with higher levels of air pollution. Although many studies argue that there is a negative relationship, some other studies hold different opinions. He and Liu (<xref ref-type="bibr" rid="B18">18</xref>) show that the effect of air pollution on China&#x00027;s stock market is non-significant over a long-term period. In addition, new research results are proposed to supplement the existing literature. Li and Peng (<xref ref-type="bibr" rid="B17">17</xref>) show that there is not only a contemporaneous negative link between air pollution and stock returns but also a 2-day lagged positive link. Giudici et al. (<xref ref-type="bibr" rid="B76">76</xref>) indicate that events and incidents related to air pollution produce obvious positive or negative stock returns, which depend on the industry.</p>
<p>Although many studies discuss the link between air quality and stock returns, research gaps remain. Few studies focus on China&#x00027;s health industry and its subdivided sectors, including health service, health equipment, health business, and health technology. Traditional econometric methods, including vector autoregression and Granger causality, do not perform well in capturing the non-linear characteristics of the link. Therefore, the quantile-on-quantile method is employed to recognize the varying degree of the influences. In addition, our study takes the effects of different quantiles of air quality into consideration, which could yield novel conclusions.</p>
</sec>
</sec>
<sec id="s3">
<title>Transmission Mechanism</title>
<p>Many studies indicate that air pollution can influence the stock market through multiple channels, which are shown in <xref ref-type="fig" rid="F1">Figure 1</xref>.</p>
<fig id="F1" position="float">
<label>Figure 1</label>
<caption><p>The transmission mechanism.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-09-789510-g0001.tif"/>
</fig>
<p>The first channel is that air pollution can lead to government intervention, especially industrial policies and environmental protection laws (<xref ref-type="bibr" rid="B77">77</xref>). Given the serious human health damage and welfare loss caused by air pollution, governments confront great social pressure to handle air pollution (<xref ref-type="bibr" rid="B25">25</xref>, <xref ref-type="bibr" rid="B42">42</xref>, <xref ref-type="bibr" rid="B78">78</xref>&#x02013;<xref ref-type="bibr" rid="B80">80</xref>). China&#x00027;s government has published a series of policies to support the development of the health care industry. For example, China released a document called the <italic>Development Plan of the Health Equipment Industry (2021&#x02013;2025)</italic>, which clearly establishes the goals that high-end health equipment will be safe and reliable, product performance and quality will reach international levels, and the health equipment industry system will be basically perfect by 2025. Positive and supporting policies will boost market confidence, affect people&#x00027;s expectations for companies&#x00027; performance, and finally increase the stock returns of the health care industry (<xref ref-type="bibr" rid="B37">37</xref>, <xref ref-type="bibr" rid="B81">81</xref>).</p>
<p>The second mechanism is that air pollution changes investors&#x00027; physiology and psychology (<xref ref-type="bibr" rid="B82">82</xref>, <xref ref-type="bibr" rid="B83">83</xref>), which ultimately affect stock markets (<xref ref-type="bibr" rid="B10">10</xref>, <xref ref-type="bibr" rid="B35">35</xref>, <xref ref-type="bibr" rid="B36">36</xref>). Physiologically, air pollution is correlated with the level of cortisol, which has a negative influence on risk-taking behavior (<xref ref-type="bibr" rid="B73">73</xref>). Psychologically, air pollutants lead to bad moods and cognitive impairment (<xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B19">19</xref>). First, people usually become pessimistic, tense and anxious in a polluted environment and tend to have negative expectations for listed companies&#x00027; performance (<xref ref-type="bibr" rid="B17">17</xref>). Furthermore, they may mistakenly attribute their bad emotions to economics instead of air pollution, which also reduces their expectation for economic development (<xref ref-type="bibr" rid="B16">16</xref>, <xref ref-type="bibr" rid="B18">18</xref>). Second, exposure to air pollution may damage mental attention, decrease sleep, increase logical confusion, and finally influence cognitive functioning (<xref ref-type="bibr" rid="B84">84</xref>&#x02013;<xref ref-type="bibr" rid="B86">86</xref>).</p>
</sec>
<sec id="s4">
<title>Quantile-on-Quantile Regression</title>
<p>We follow the work of Sim and Zhou (<xref ref-type="bibr" rid="B87">87</xref>) and show the QQ method as follows:</p>
<disp-formula id="E1"><label>(1)</label><mml:math id="M1"><mml:mtable class="eqnarray" columnalign="left"><mml:mtr><mml:mtd><mml:mi>S</mml:mi><mml:msub><mml:mrow><mml:mi>R</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub><mml:mo>=</mml:mo><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>&#x0002B;</mml:mo><mml:msup><mml:mrow><mml:msub><mml:mrow><mml:mi>&#x003BC;</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
<p>where <italic>AQ</italic><sub><italic>t</italic></sub> and <italic>SR</italic><sub><italic>t</italic></sub> indicate the air quality and stock return at time <italic>t</italic>, respectively. &#x003B2;, &#x003B8; and &#x003BC;<sub><italic>t</italic></sub> denote the parameter, &#x003B8;<italic>th</italic> quantile and error term, respectively. We further linearize <italic>&#x003B2;</italic><sup>&#x003B8;</sup>(&#x000B7;) by taking a first-order Taylor expansion around <italic>AQ</italic><sup>&#x003C4;</sup> (<italic>AQ</italic><sup>&#x003C4;</sup> denotes the &#x003C4; quantile of the OP). The new equation is shown as follows:</p>
<disp-formula id="E2"><label>(2)</label><mml:math id="M2"><mml:mtable class="eqnarray" columnalign="left"><mml:mtr><mml:mtd><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>&#x02248;</mml:mo><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msup><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>&#x0002B;</mml:mo><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:msup><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x02032;</mml:mi></mml:mrow></mml:msup></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msup><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub><mml:mo>-</mml:mo><mml:mi>A</mml:mi><mml:msup><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
<p>where <italic>&#x003B2;</italic><sup>&#x003B8;</sup>&#x02032; is the partial derivative of <inline-formula><mml:math id="M3"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> for <italic>AQ</italic>. However, the method presents a similar expansion for the slope parameter as in a linear regression model. Moreover, Equation (<xref ref-type="bibr" rid="B2">2</xref>) defines &#x003B8; and &#x003C4; as double indexed, and the parameters are indicated as <inline-formula><mml:math id="M4"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math id="M5"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:msup><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x02032;</mml:mi></mml:mrow></mml:msup></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula>, respectively. Hence, <inline-formula><mml:math id="M6"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math id="M7"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:msup><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x02032;</mml:mi></mml:mrow></mml:msup></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> are functions of &#x003B8; and &#x003C4;. Additionally, <inline-formula><mml:math id="M8"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math id="M9"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:msup><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x02032;</mml:mi></mml:mrow></mml:msup></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> are verified as &#x003B2;<sub>0</sub>(&#x003B8;, &#x003C4;) and &#x003B2;<sub>1</sub>(&#x003B8;, &#x003C4;), respectively. Thus, <inline-formula><mml:math id="M10"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> is further described as follows:</p>
<disp-formula id="E3"><label>(3)</label><mml:math id="M11"><mml:mtable class="eqnarray" columnalign="left"><mml:mtr><mml:mtd><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>&#x02248;</mml:mo><mml:msub><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mn>0</mml:mn></mml:mrow></mml:msub><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>&#x003B8;</mml:mi><mml:mo>,</mml:mo><mml:mi>&#x003C4;</mml:mi></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>&#x0002B;</mml:mo><mml:msub><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow></mml:msub><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>&#x003B8;</mml:mi><mml:mo>,</mml:mo><mml:mi>&#x003C4;</mml:mi></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub><mml:mo>-</mml:mo><mml:mi>A</mml:mi><mml:msup><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
<p>Then, we utilize Equation (<xref ref-type="bibr" rid="B3">3</xref>) to replace <inline-formula><mml:math id="M12"><mml:msup><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula> in Equation (<xref ref-type="bibr" rid="B1">1</xref>) and obtain the following:</p>
<disp-formula id="E4"><label>(4)</label><mml:math id="M13"><mml:mtable class="eqnarray" columnalign="left"><mml:mtr><mml:mtd><mml:mi>S</mml:mi><mml:msub><mml:mrow><mml:mi>R</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub><mml:mo>=</mml:mo><mml:mfrac><mml:mrow><mml:msub><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mn>0</mml:mn></mml:mrow></mml:msub><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>&#x003B8;</mml:mi><mml:mo>,</mml:mo><mml:mi>&#x003C4;</mml:mi></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>&#x0002B;</mml:mo><mml:msub><mml:mrow><mml:mi>&#x003B2;</mml:mi></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow></mml:msub><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>&#x003B8;</mml:mi><mml:mo>,</mml:mo><mml:mi>&#x003C4;</mml:mi></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub><mml:mo>-</mml:mo><mml:mi>A</mml:mi><mml:msup><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mrow><mml:mrow><mml:mo>&#x0002A;</mml:mo></mml:mrow></mml:mfrac><mml:mo>&#x0002B;</mml:mo><mml:msup><mml:mrow><mml:msub><mml:mrow><mml:mi>&#x003BC;</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mrow><mml:mi>&#x003B8;</mml:mi></mml:mrow></mml:msup></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
<p>The link between AQ and SR in each respective quantile is captured since the coefficients of &#x003B2;<sub>0</sub> and &#x003B2;<sub>1</sub> depend on &#x003B8; and &#x003C4;. In order to estimate Equation (<xref ref-type="bibr" rid="B4">4</xref>), <italic>AQ</italic><sub><italic>t</italic></sub> and <italic>AQ</italic><sup>&#x003C4;</sup> are required instead with their counterparts <inline-formula><mml:math id="M14"><mml:msub><mml:mrow><mml:mover accent="true"><mml:mrow><mml:mi>A</mml:mi><mml:mi>Q</mml:mi></mml:mrow><mml:mo>^</mml:mo></mml:mover></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:math></inline-formula> and <inline-formula><mml:math id="M15"><mml:msup><mml:mrow><mml:mover accent="true"><mml:mrow><mml:mi>A</mml:mi><mml:mi>Q</mml:mi></mml:mrow><mml:mo>^</mml:mo></mml:mover></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:math></inline-formula>, respectively. Therefore, the parameters <italic>b</italic><sub>0</sub> and <italic>b</italic><sub>1</sub> are estimated as the minimization problem in Equation (<xref ref-type="bibr" rid="B5">5</xref>):</p>
<disp-formula id="E5"><label>(5)</label><mml:math id="M16"><mml:mtable class="eqnarray" columnalign="left"><mml:mtr><mml:mtd><mml:mi>m</mml:mi><mml:mi>i</mml:mi><mml:msub><mml:mrow><mml:mi>n</mml:mi></mml:mrow><mml:mrow><mml:msub><mml:mrow><mml:mi>b</mml:mi></mml:mrow><mml:mrow><mml:mn>0</mml:mn></mml:mrow></mml:msub><mml:mo>,</mml:mo><mml:msub><mml:mrow><mml:mi>b</mml:mi></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow></mml:msub></mml:mrow></mml:msub><mml:mstyle displaystyle="true"><mml:munderover accentunder="false" accent="false"><mml:mrow><mml:mo>&#x02211;</mml:mo></mml:mrow><mml:mrow><mml:mi>i</mml:mi><mml:mo>=</mml:mo><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mi>N</mml:mi></mml:mrow></mml:munderover></mml:mstyle><mml:mi>&#x003C1;</mml:mi><mml:mi>&#x003B8;</mml:mi><mml:mrow><mml:mo>[</mml:mo><mml:mrow><mml:mi>S</mml:mi><mml:msub><mml:mrow><mml:mi>R</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub><mml:mo>-</mml:mo><mml:msub><mml:mrow><mml:mi>b</mml:mi></mml:mrow><mml:mrow><mml:mn>0</mml:mn></mml:mrow></mml:msub><mml:mo>-</mml:mo><mml:msub><mml:mrow><mml:mi>b</mml:mi></mml:mrow><mml:mrow><mml:mn>1</mml:mn></mml:mrow></mml:msub><mml:mrow><mml:mo stretchy="true">(</mml:mo><mml:mrow><mml:msub><mml:mrow><mml:mover accent="true"><mml:mrow><mml:mi>A</mml:mi><mml:mi>Q</mml:mi></mml:mrow><mml:mo>^</mml:mo></mml:mover></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub><mml:mo>-</mml:mo><mml:msup><mml:mrow><mml:mover accent="true"><mml:mrow><mml:mi>A</mml:mi><mml:mi>Q</mml:mi></mml:mrow><mml:mo>^</mml:mo></mml:mover></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:mrow><mml:mo stretchy="true">)</mml:mo></mml:mrow></mml:mrow><mml:mo>]</mml:mo></mml:mrow></mml:mtd></mml:mtr><mml:mtr><mml:mtd><mml:mo>&#x000D7;</mml:mo><mml:mi>K</mml:mi><mml:mrow><mml:mo stretchy="true">(</mml:mo><mml:mrow><mml:mfrac><mml:mrow><mml:msub><mml:mrow><mml:mi>F</mml:mi></mml:mrow><mml:mrow><mml:mi>n</mml:mi></mml:mrow></mml:msub><mml:mrow><mml:mo stretchy="true">(</mml:mo><mml:mrow><mml:msub><mml:mrow><mml:mover accent="true"><mml:mrow><mml:mi>A</mml:mi><mml:mi>Q</mml:mi></mml:mrow><mml:mo>^</mml:mo></mml:mover></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="true">)</mml:mo></mml:mrow><mml:mo>-</mml:mo><mml:mi>&#x003C4;</mml:mi></mml:mrow><mml:mrow><mml:mi>h</mml:mi></mml:mrow></mml:mfrac></mml:mrow><mml:mo stretchy="true">)</mml:mo></mml:mrow></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
<p>where &#x003C1;&#x003B8;(&#x003BC;) is the absolute value function of the slope. <italic>K</italic>(&#x000B7;) is a Gaussian kernel. <italic>h</italic> indicates the bandwidth parameter of the kernel method and is equal to 0.05 in our paper. We also notice that the weights are inversely related to the distribution between <inline-formula><mml:math id="M18"><mml:msub><mml:mrow><mml:mover accent="true"><mml:mrow><mml:mi>A</mml:mi><mml:mi>Q</mml:mi></mml:mrow><mml:mo>^</mml:mo></mml:mover></mml:mrow><mml:mrow><mml:mi>t</mml:mi></mml:mrow></mml:msub></mml:math></inline-formula> and <inline-formula><mml:math id="M19"><mml:msup><mml:mrow><mml:mover accent="true"><mml:mrow><mml:mi>A</mml:mi><mml:mi>Q</mml:mi></mml:mrow><mml:mo>^</mml:mo></mml:mover></mml:mrow><mml:mrow><mml:mi>&#x003C4;</mml:mi></mml:mrow></mml:msup></mml:math></inline-formula>, and the function is described as follows:</p>
<disp-formula id="E6"><label>(6)</label><mml:math id="M20"><mml:mtable class="eqnarray" columnalign="left"><mml:mtr><mml:mtd><mml:msub><mml:mrow><mml:mi>F</mml:mi></mml:mrow><mml:mrow><mml:mi>n</mml:mi></mml:mrow></mml:msub><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi><mml:mo>-</mml:mo><mml:mn>1</mml:mn></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>=</mml:mo><mml:mfrac><mml:mrow><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mi>n</mml:mi></mml:mrow></mml:mfrac><mml:mstyle displaystyle="true"><mml:munderover accentunder="false" accent="false"><mml:mrow><mml:mo>&#x02211;</mml:mo></mml:mrow><mml:mrow><mml:mi>k</mml:mi><mml:mo>=</mml:mo><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mi>n</mml:mi></mml:mrow></mml:munderover></mml:mstyle><mml:mi>I</mml:mi><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mrow><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>k</mml:mi></mml:mrow></mml:msub><mml:mo>&#x0003C;</mml:mo><mml:mi>A</mml:mi><mml:msub><mml:mrow><mml:mi>Q</mml:mi></mml:mrow><mml:mrow><mml:mi>t</mml:mi><mml:mo>-</mml:mo><mml:mn>1</mml:mn></mml:mrow></mml:msub></mml:mrow><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
<p>Similarly, the same empirical steps are repeated to investigate the cases of stock returns in each industry, and the model permits us to test and verify the mentioned hypothesis.</p>
<p>This method can fully capture the potential asymmetric response of dependent variable across distributions of both explanatory and dependent variables. In addition, it can consistently estimate the smooth changing parameters and uncover underlying structural breaks in the real data. Last, since we consider the impacts of temporal-lag in the independent variable on the contemporaneous dependent variable, the QQ method ameliorates the endogeneity problem regarding the simultaneity which is contributed into the nature of its model specification. Depending on the mentioned strengthens, the QQ method has been widely employed in following fields, including agriculture commodity futures (<xref ref-type="bibr" rid="B88">88</xref>), stock market (<xref ref-type="bibr" rid="B46">46</xref>), oil market (<xref ref-type="bibr" rid="B89">89</xref>), industrial growth (<xref ref-type="bibr" rid="B90">90</xref>), and CO<sub>2</sub> emission (<xref ref-type="bibr" rid="B91">91</xref>).</p>
</sec>
<sec id="s5">
<title>Data and Empirical Results</title>
<sec>
<title>Data Source and Description</title>
<p>Our sample contains daily trading data that range from January 1, 2014 to July 31, 2021. Two types of variables are employed in this paper. The independent variable is Shanghai&#x00027;s air quality index (AQ). Shanghai is located in the Yangtze River Delta and has a subtropical monsoon climate. Shanghai is one of the most urbanized and modernized cities and is the economic center in China. The AQ index data come from the Ministry of Ecology and Environment of the People&#x00027;s Republic of China (MEEPRC), which has published daily data since January 2014. The AQ index can be divided into multiple levels, which is shown in <xref ref-type="table" rid="T1">Table 1</xref>. For example, when the values of AQ range from 0 to 100, the air quality is defined as fine and moderate, which does not cause the issue of air pollution. However, when the values are bigger than 100, the air quality is regarded as unhealthy and produce a significant influence on people&#x00027;s physiology and psychology. As shown in <xref ref-type="fig" rid="F2">Figure 2</xref>, AQ presents huge volatility, and higher values usually emerge in spring and winter of the year. We provide potential reasons to explain this phenomenon. First, spring and winter are heating periods in northern China, and the major fuel is coal, which is one of the most polluting forms of energy. Second, at the end of the year, local governments tend to relax the requirement of environmental protection to reach their economic growth targets. The dependent variable is the stock return (SR). To comprehensively investigate the relationship between and SR, we choose four different health industries, which include health services (HS), health equipment (HE), health businesses (HB), and health technology (HT), as samples. The mentioned industries are tightly correlated with AQ, and their results could provide more valuable policy references. According to the traditional approach, this paper takes the logarithmic difference of the stock index to obtain SR, which can be described as SR<sub>t</sub> = LnP<sub>t</sub> -LnP<sub>t&#x02212;1</sub>. In the formula, P<sub>t</sub> and P<sub>t&#x02212;1</sub> indicate the stock indices at time t and t-1, respectively. <xref ref-type="table" rid="T2">Table 2</xref> presents the descriptive statistics for all variables. The skewness values of all variables except AQ are &#x0003C;0, which indicates that the tail of the left side of the distribution is fatter than the tail on the right side. The kurtosis values of all variables are larger than 3, which demonstrates that their tails are fatter and obey a leptokurtic distribution. The Jarque-Bera test has the null hypothesis of a normal distribution and demonstrates that all variables reject the null hypothesis and follow a non-normal distribution.</p>
<table-wrap position="float" id="T1">
<label>Table 1</label>
<caption><p>The AQ index classification levels.</p></caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th valign="top" align="left"><bold>Air quality index (values)</bold></th>
<th valign="top" align="left"><bold>Levels of health</bold></th>
<th valign="top" align="left"><bold>Health concern &#x00026; meanings</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">0&#x02013;50</td>
<td valign="top" align="left">Good</td>
<td valign="top" align="left">There is little risk and the air is not polluted. People are satisfied with this level of air quality.</td>
</tr>
<tr>
<td valign="top" align="left">51&#x02013;100</td>
<td valign="top" align="left">Moderate</td>
<td valign="top" align="left">Most people find the air acceptable, yet a few people may worry that some pollutants in the air will cause health problems.</td>
</tr>
<tr>
<td valign="top" align="left">101&#x02013;150</td>
<td valign="top" align="left">Unhealthy for sensitive groups</td>
<td valign="top" align="left">General people will not be seriously affected by this level of air quality, while people with lung disease are exposed with greater risks.</td>
</tr>
<tr>
<td valign="top" align="left">151&#x02013;200</td>
<td valign="top" align="left">Unhealthy</td>
<td valign="top" align="left">Air quality of this level poses threats to physical health of everyone, and the sensitive groups face greater risks.</td>
</tr>
<tr>
<td valign="top" align="left">201&#x02013;300</td>
<td valign="top" align="left">Very unhealthy</td>
<td valign="top" align="left">The health condition of every people is seriously affected by the mixture of pollutants in the air.</td>
</tr>
<tr>
<td valign="top" align="left">301&#x02013;500</td>
<td valign="top" align="left">Hazardous</td>
<td valign="top" align="left">The air quality is intolerant for the entire population, which causes critical health warnings.</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F2" position="float">
<label>Figure 2</label>
<caption><p>The trend of AQ index.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-09-789510-g0002.tif"/>
</fig>
<table-wrap position="float" id="T2">
<label>Table 2</label>
<caption><p>Descriptive statistics of the variables.</p></caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th/>
<th valign="top" align="center"><bold>Maximum</bold></th>
<th valign="top" align="center"><bold>Minimum</bold></th>
<th valign="top" align="center"><bold>Std. Dev</bold>.</th>
<th valign="top" align="center"><bold>Skewness</bold></th>
<th valign="top" align="center"><bold>Kurtosis</bold></th>
<th valign="top" align="center"><bold>Jarque-Bera</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">AQ</td>
<td valign="top" align="center">266</td>
<td valign="top" align="center">24</td>
<td valign="top" align="center">35.032</td>
<td valign="top" align="center">1.393</td>
<td valign="top" align="center">5.506</td>
<td valign="top" align="center">1019.027<xref ref-type="table-fn" rid="TN1"><sup>&#x0002A;&#x0002A;&#x0002A;</sup></xref></td>
</tr>
<tr>
<td valign="top" align="left">HS</td>
<td valign="top" align="center">0.077</td>
<td valign="top" align="center">&#x02212;0.089</td>
<td valign="top" align="center">0.021</td>
<td valign="top" align="center">&#x02212;0.329</td>
<td valign="top" align="center">4.685</td>
<td valign="top" align="center">251.508<xref ref-type="table-fn" rid="TN1"><sup>&#x0002A;&#x0002A;&#x0002A;</sup></xref></td>
</tr>
<tr>
<td valign="top" align="left">HE</td>
<td valign="top" align="center">0.074</td>
<td valign="top" align="center">&#x02212;0.091</td>
<td valign="top" align="center">0.021</td>
<td valign="top" align="center">&#x02212;0.465</td>
<td valign="top" align="center">5.158</td>
<td valign="top" align="center">424.476<xref ref-type="table-fn" rid="TN1"><sup>&#x0002A;&#x0002A;&#x0002A;</sup></xref></td>
</tr>
<tr>
<td valign="top" align="left">HB</td>
<td valign="top" align="center">0.069</td>
<td valign="top" align="center">&#x02212;0.093</td>
<td valign="top" align="center">0.017</td>
<td valign="top" align="center">&#x02212;0.568</td>
<td valign="top" align="center">6.505</td>
<td valign="top" align="center">1043.922<xref ref-type="table-fn" rid="TN1"><sup>&#x0002A;&#x0002A;&#x0002A;</sup></xref></td>
</tr>
<tr>
<td valign="top" align="left">HT</td>
<td valign="top" align="center">0.095</td>
<td valign="top" align="center">&#x02212;0.103</td>
<td valign="top" align="center">0.018</td>
<td valign="top" align="center">&#x02212;0.747</td>
<td valign="top" align="center">9.049</td>
<td valign="top" align="center">2986.122<xref ref-type="table-fn" rid="TN1"><sup>&#x0002A;&#x0002A;&#x0002A;</sup></xref></td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="TN1"><label>&#x0002A;&#x0002A;&#x0002A;</label><p><italic>denotes significance at 1% level</italic>.</p></fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec>
<title>Empirical Results</title>
<p><xref ref-type="fig" rid="F3">Figure 3</xref> presents the results regarding the effect of air quality on the stock returns of HS using the QQ regression approach. As shown in the figure, the scale of the colored bar indicates the coefficients between AQ and HS, inferring the influence of different quantiles of AQ on health services. Dark blue and dark red indicate the lowest and highest values of the coefficients, respectively. We find that the coefficients are positive in the [0, 0.2] and [0.4, 0.8] quantiles and negative in the [0.2, 0.4] and [0.8, 1] quantiles for AQ. This demonstrates that good AQ decreases SR and bad AQ increases SR, which can be explained in the following ways. First, the phenomenon of an aging population in China is intensifying. The number of people over 60 years old has increased rapidly from 178 million in 2010 to 260 million in 2020, increasing from 13.3% of the total population in 2010 to 18.7% of the total population in 2020. Luo et al. (<xref ref-type="bibr" rid="B92">92</xref>) clearly state that long-term exposure to air pollution would damage mental abilities and episodic memory among middle-aged and old adults in China. Woodward and Levine (<xref ref-type="bibr" rid="B93">93</xref>) also indicate that older adults, accompanied by decreased cardiovascular function, experience higher mortality risks due to exposure to air pollution. Therefore, the increasing number of old adults in China brings great needs for health services. Second, China has published a series of policies to support the development of the health service industry. The National Health and Family Planning Commission (NHFPC) issued a document to effectively integrate social health services into the overall consideration of regional health planning. In 2015, the State Council released a document to further relax access to social health services and control the scale of public hospitals. Since then, many policies have been issued to encourage the access conditions, administrative examination and approval, investment and financing channels, hierarchical diagnosis and treatment, and expansion of high-quality societal hospitals. Since 2019, policy has emphasized supporting social health services in various specialized health service fields and accelerating the creation of a number of competitive brand service institutions in ophthalmology, orthopedics and other fields.</p>
<fig id="F3" position="float">
<label>Figure 3</label>
<caption><p>The coefficients between AQ and HS.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-09-789510-g0003.tif"/>
</fig>
<p><xref ref-type="fig" rid="F4">Figure 4</xref> indicates that the coefficients between AQ and HE are negative in all quantiles of AQ, except in the [0.4, 0.5] quantile. Air pollution directly influences body organs and tissues, which results in respiratory disease, poor mental health, and subjective illness (<xref ref-type="bibr" rid="B64">64</xref>, <xref ref-type="bibr" rid="B94">94</xref>). People are concerned about their health and reflect on the stock of the health industry through investors&#x00027; behaviors. Therefore, the negative relationship between AQ and HE can be explained from physiological and psychological perspectives. Air pollution produces stressful stimuli; thus, people experience emotional, mental, and physical changes (<xref ref-type="bibr" rid="B95">95</xref>). Investors and other market participants are more pessimistic as air pollution increases and mistakenly attribute bad moods to depressed economic performance instead of air pollution (<xref ref-type="bibr" rid="B17">17</xref>, <xref ref-type="bibr" rid="B96">96</xref>). This may lead to biased decisions and reduce stock purchases, which ultimately influence stock returns. In addition, government policy also plays a key role in explaining the negative relationship. Considering the health risks brought by air pollution, the government has proposed the concept of &#x0201C;Healthy China&#x0201D; to develop the health industry to reduce this type of risk. From 2010 to 2015, the total value of the health equipment of all of China&#x00027;s hospitals nearly doubled and reached 629 billion RMB (<xref ref-type="bibr" rid="B97">97</xref>). In 2020, the global health equipment market reached nearly 500 billion U.S. dollars, with a growth rate of nearly 4%. The scale of China&#x00027;s market is nearly 800 billion RMB, with a growth rate of nearly 20%, much higher than the global average. In the future, China is expected to cultivate a number of global health equipment leaders. First, the rapid growth of the domestic market will become important support for the rise of domestic leaders. Second, local equipment leaders are expected to continue to expand their shares in the international market. As shown by the NHFPC, China has proposed a strategy for developing modern health equipment with the purpose of constructing high-technology, large-scale, precise and valuable instruments. However, we should note that developing HE requires a long time, which indicates that bad air quality cannot influence the health equipment industry immediately.</p>
<fig id="F4" position="float">
<label>Figure 4</label>
<caption><p>The coefficients between AQ and HE.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-09-789510-g0004.tif"/>
</fig>
<p><xref ref-type="fig" rid="F5">Figure 5</xref> shows the coefficients between AQ and HB, and a positive relationship exists. Although a positive link exists in all quantiles of AQ, the values of the coefficients in the [0, 0.5] quantile are larger than those in the other quantiles. Air quality is able to bring changes in investors&#x00027; physiology and psychology and further influences the stock market. Liu et al. (<xref ref-type="bibr" rid="B73">73</xref>) indicate that exposure to good air can trigger decreases in cortisol levels in humans, which makes people more likely to engage in risk-taking behaviors. Hence, good air quality would decrease investors&#x00027; risk aversion and cause individual investors to purchase more stocks. Furthermore, health studies also find that exposure to good air quality increases spirits, concentration, relaxation and optimism, which are beneficial for performing cognitive functioning (<xref ref-type="bibr" rid="B19">19</xref>). Because trading decisions require strong cognitive function, cognitive functioning may lead investors to make the most appropriate trading decisions. However, in an environment with air pollution, the relationship between AQ and HB is still positive, which is mainly due to industrial policies rather than physiology and psychology. China has become the second largest health care market in the world. Depending on the prosperous economy, booming electronic commerce, and participating in the World Trade Organization, China&#x00027;s distribution and logistics systems in the health market have greatly improved (<xref ref-type="bibr" rid="B98">98</xref>). Since 2015, a number of policies related to drugs have been revised and newly published, which has had a significant influence on China&#x00027;s health care industry (<xref ref-type="bibr" rid="B99">99</xref>). In 2017, some key changes occurred, such as the new version of the National Reimbursement Drug List that determines which drugs are included in national health insurance. In addition, several new regulations were launched to change the clinical trial process, optimize the drug registration process, and manage drug prices. In addition, in recent years, China has also encouraged investments by leading health device companies, both foreign and domestic. The National Healthcare Security Administration (NHSA) and the National Health Commission (NHC) are promoting the reform of the &#x0201C;drug dual channel,&#x0201D; which aims to meet the reasonable needs of drug supply guarantees and clinical use through two channels, designated health institutions and designated retail pharmacies; and simultaneously incorporate the two channels into the payment mechanism of health insurance.</p>
<fig id="F5" position="float">
<label>Figure 5</label>
<caption><p>The coefficients between AQ and HB.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-09-789510-g0005.tif"/>
</fig>
<p><xref ref-type="fig" rid="F6">Figure 6</xref> shows that the coefficients between AQ and HT are positive in the [0, 0.5] quantile and decrease and even become negative in the [0.5, 1] quantile of AQ. As explained in the health business industry, both physiological and psychological factors play important roles in this positive relationship. Some prior health studies have demonstrated that air quality significantly affects people&#x00027;s cognitive functions (<xref ref-type="bibr" rid="B7">7</xref>, <xref ref-type="bibr" rid="B12">12</xref>, <xref ref-type="bibr" rid="B34">34</xref>). Contact with good air can increase the ability of red blood cells to transfer oxygen to human organs, which is beneficial for concentrating spirit and avoiding confusion. Under this situation, people are more optimistic and relaxed and possess strong cognition, which makes them more likely to purchase stocks and engage in more stock trading (<xref ref-type="bibr" rid="B100">100</xref>). However, exposure to air pollution would have negative influences on stock markets in the following ways. First, a number of studies offer evidence that exposure to air pollution would damage the human brain and impair cognitive function, which has a negative influence on activities and decisions. Because stock trading involves cognitively demanding decisions, contact with polluted air damages investors&#x00027; cognitive abilities. Second, air pollution can lead to mood changes for individuals; and moods are tightly related to investment decisions, asset valuation, and asset pricing in stock markets. In addition, long-term exposure to air pollution would result in sleep loss, which further brings the problems of judgment errors, attention loss, and inefficient information processing capabilities. Government industrial policies need time to play better roles in the health technology industry. In 2016, China&#x00027;s health care market grew by 10.6% to reach 1.5 trillion RMB and is estimated to reach 2 trillion RMB in 2021. Thus, China published a document of the guiding opinions on accelerating the structural adjustment of the health care industry, which includes promoting cross regional and cross ownership mergers and acquisitions and improving the economies of scale and industrial concentrations of companies. However, the health technology industry has the characteristics of high investments, high risk, high returns and a long cycle. The global health technology industry is increasingly showing a highly concentrated oligopolistic and monopolistic competition pattern. Bayer, Sanofi-Aventis, Merck, GlaxoSmithKline, Johnson &#x00026; Johnson and fourteen other international health giants occupy 70% of the global market. Based on serious foreign competition, China&#x00027;s industrial supporting policies for health technology companies need time to take effect and thus affect stock markets in a timely manner.</p>
<fig id="F6" position="float">
<label>Figure 6</label>
<caption><p>The coefficients between AQ and HT.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpubh-09-789510-g0006.tif"/>
</fig>
<p>Summarily, the link between air quality and stock returns present heterogeneous characters in different industries. For the HS and HT, good AQ decreases SR and bad AQ increases SR, which can be explained by healthcare demand. In addition, the coefficients between AQ and HE are negative in all quantiles of AQ, except in quantile of [0.4, 0.5]. Oppositely, the coefficients between AQ and HB, and there exists positive relationship. Given the complex relationship between AQ and SR in China&#x00027;s health industry, the government and health enterprises need to employ multiple policy tools, such as increasing R&#x00026;D expenditure and improving health system, to main stable development of health industry and reduce shocks from changes in air quality.</p>
</sec>
</sec>
<sec id="s6">
<title>Conclusion and Policy Implications</title>
<p>This paper discusses the asymmetric link between air quality and stock returns for the health service (HS), health equipment (HE), health business (HB), and health technology (HT) industries. The major empirical results reveal that SR responds differently to AQ, which depends on the industry. First, the coefficients in HS and HT would change from positive to negative, but they have different turning points with respect to AQ. For example, the negative links for HS and HT are in the [0.8, 1] and [0.5, 1] quantiles, respectively. Second, the coefficients between AQ and HB have a positive relationship. Although a positive link exists in all quantiles of AQ, the values of the coefficients in the [0, 0.5] quantiles are larger than those in the other quantiles. Third, the coefficients between AQ and HE are negative in all quantiles of AQ, except in the [0.4, 0.5] quantile, which is different from other industries. When compared with previous literature, our study provides valuable contributions. First, we provide a new channel from government intervention to explain the influence of AQ on SR. China&#x00027;s government has launched a series of industrial structure upgrading guidelines; thus, these guidelines should be considered in explaining the relationship between AQ and SR. Second, industrial heterogeneity is fully considered in this study. Industries respond differently to the same external shock due to their industrial characteristics. Last, the quantile-on-quantile method, which can examine the effects of specific quantiles between variables without considering structural break and temporal lag effects, combines non-parametric estimation and the traditional quantile regression.</p>
<p>According to the conclusions, some policy implications are provided. First, investors, regulators and other market participants should notice that their biased decisions may be caused by air pollution instead of depressed economic development. Therefore, air quality should be regarded as an important factor in making cognitively demanding decisions in stock markets. Second, air pollutants seriously affect people&#x00027;s physiology, such as their cortisol levels; cognition and psychology, such as tension and anxiety. Hence, authorities should establish environmental protection law systems to decrease pollutant emissions and construct a strict mechanism for the disclosure of environmental information to the public. Third, China should optimize the structure of its health industry, encourage mergers and acquisitions across regions, construct independent health and medical innovation systems, and strengthen awareness of obeying laws and regulations among health companies. Besides, health education is needed to improve the residents&#x00027; health literacy, such as how to make proper utilization of social security policies to protect themselves. More attention should be paid to vulnerable groups, such as rural, female, and old residents, to promote their equal access to basic public health service.</p>
</sec>
<sec sec-type="data-availability" id="s7">
<title>Data Availability Statement</title>
<p>The original contributions presented in the study are included in the article/supplementary material, further inquiries can be directed to the corresponding author/s.</p>
</sec>
<sec id="s8">
<title>Author Contributions</title>
<p>LL: conceptualization. K-HW: methodology and write. YX: visualization and investigation. All authors contributed to the article and approved the submitted version.</p>
</sec>
<sec sec-type="funding-information" id="s9">
<title>Funding</title>
<p>This research has been supported by the Social Science Foundation of Shandong, China (Grant Number: 21DJJJ09).</p>
</sec>
<sec sec-type="COI-statement" id="conf1">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="disclaimer" id="s10">
<title>Publisher&#x00027;s Note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
</body>
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