<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">NS</journal-id><journal-title-group><journal-title>Natural Science</journal-title></journal-title-group><issn pub-type="epub">2150-4091</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ns.2020.125023</article-id><article-id pub-id-type="publisher-id">NS-100179</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject><subject> Chemistry&amp;Materials Science</subject><subject> Earth&amp;Environmental Sciences</subject><subject> Medicine&amp;Healthcare</subject><subject> Physics&amp;Mathematics</subject></subj-group></article-categories><title-group><article-title>
 
 
  Do We Ignore Tobacco’s Positive Ecological Role Too Long?
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Shaomin</surname><given-names>Yan</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Guang</surname><given-names>Wu</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>National Engineering Research Center for Non-Food Biorefinery, State Key Laboratory of Non-Food Biomass and Enzyme Technology, Guangxi Key Laboratory of Bio-Refinery, Guangxi Biomass Engineering Technology Research Center, Guangxi Academy of Sciences, Nanning, China</addr-line></aff><pub-date pub-type="epub"><day>28</day><month>04</month><year>2020</year></pub-date><volume>12</volume><issue>05</issue><fpage>273</fpage><lpage>280</lpage><history><date date-type="received"><day>25,</day>	<month>March</month>	<year>2020</year></date><date date-type="rev-recd"><day>11,</day>	<month>May</month>	<year>2020</year>	</date><date date-type="accepted"><day>14,</day>	<month>May</month>	<year>2020</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  Definitely, tobacco is one of the most troubling plants in this planet because of its harmful effects on humans. Therefore, tobacco plantation declines continuously in the world. For such a plant, do we need to eliminate tobacco entirely from the surface of the earth? Perhaps, humans might have ignored the tobacco’s positive role in environment and ecology, especially in the heavily industrialized environments, for too long. Because the human activity generates more and more nitrogen oxides (NO
  <sub>x</sub>
  ) in atmosphere, which not only cause imbalance in the global nitrogen cycle but also lead to haze, smog, acid rain, PM
  <sub>2.5</sub>
  , and eventually impact on environment and human health. Unfortunately the current technologies do not provide an efficient way to remove NO
  <sub>x</sub>
   from atmosphere. However, it is only tobacco can remove NO
  <sub>x</sub>
   from atmosphere. Perhaps, we should blame us, humans who use tobacco unwisely, rather than blame tobacco in nature. Anyways, the ability of tobacco to remove NO
  <sub>2</sub>
   from atmosphere should not be ignored.
 
</p></abstract><kwd-group><kwd>Air Pollution</kwd><kwd> Nitrogen Oxides</kwd><kwd> PM2.5</kwd><kwd> Phytoremediation</kwd><kwd> Tobacco</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. NITROGEN OXIDES AND THEIR EFFECTS IN ENVIRONMENT</title><p>Nitrogen is one of the most abundant elements in the earth, and accounts for 78.1% of the atmosphere. Being an inert gas, nitrogen can be used by organisms only when it is converted into reactive nitrogen [<xref ref-type="bibr" rid="scirp.100179-ref1">1</xref>], although it is essential for all the living species. There are various forms of reactive nitrogen (Nr) in the atmosphere: ammonia (NH<sub>3</sub>), nitrous oxide (N<sub>2</sub>O), nitric acid (HNO<sub>3</sub>), nitrous acid (HONO), nitrogen oxide (NO<sub>x</sub>) including nitric oxide (NO) and nitrogen dioxide (NO<sub>2</sub>). Thus, the nitrogen cycle, which undergoes its long-term evolution, maintains the balance of nitrogen.</p><p>It is estimated that the global nitrogen fixation generates 413 Tg N every year whereas about a half, 210 Tg N, comes from human activities. Furthermore, there are 100 Tg N into the atmosphere every year from the emissions of the NH<sub>3</sub> from land and the NO<sub>x</sub> from combustion [<xref ref-type="bibr" rid="scirp.100179-ref2">2</xref>]. Without human activity, the biological nitrogen fixation and the production of NO<sub>x</sub> by lightning are the only sources for new Nr going into the environment [<xref ref-type="bibr" rid="scirp.100179-ref2">2</xref>]. Also, the estimated production of NO<sub>x</sub> by lighting is about 5 Tg N ranging from 2 to 10 Tg N every year [3 - 8].</p><p>Due to this variability, NO<sub>x</sub> produced by lighting would accounts for 20% - 80% of NO<sub>x</sub> in the world [5 - 8]. However, the NO<sub>x</sub> produced by lighting is located in rather remote regions of the troposphere [<xref ref-type="bibr" rid="scirp.100179-ref2">2</xref>]. Still, other estimates indicate that the global NO<sub>x</sub> is about 40 Tg N in 2000, of which the combustions of fossil fuel and biomass contribute to 87.5% while the emissions of soil NO account for 12.5% [<xref ref-type="bibr" rid="scirp.100179-ref9">9</xref>], i.e. each year soil microorganisms produce 9.7 - 21 Tg N NO [10,11]. In such a case, NO<sub>x</sub> produced by lighting is not particularly relevant to this estimation.</p><p>Nowadays, NO<sub>2</sub> usually serves as the indicator for NO<sub>x</sub> because of human activity. Indeed, NO<sub>2</sub> into the atmosphere comes primarily from the burning of fuel, including the emissions from cars, trucks and buses, power plants, and off-road equipment, although NO<sub>2</sub> contributes about 10% of NO<sub>x</sub> and the remaining 90% NO<sub>x</sub> is NO [<xref ref-type="bibr" rid="scirp.100179-ref11">11</xref>].</p><p>To some degree, the harmful effects of NO<sub>x</sub> to humans are mainly related to NO<sub>2</sub>. High concentrations of NO<sub>2</sub> irritate airways in the human respiratory system. For short exposures, NO<sub>2</sub> can aggravate respiratory diseases, especially asthma, and result in the respiratory symptoms, such as coughing, wheezing or difficulty breathing. For long exposures, NO<sub>2</sub> may affect immune functions of respiratory system leading to potential of infections as well as asthma. Furthermore, the respiratory system can be damaged by particulate matter and ozone, which are formed during the reactions among NO, NO<sub>2</sub> and other chemicals [<xref ref-type="bibr" rid="scirp.100179-ref13">13</xref>]. Some studies estimated that the health damage caused by NO<sub>x</sub> emission accounted for 39% - 47% of the relevant health damage in China [<xref ref-type="bibr" rid="scirp.100179-ref14">14</xref>].</p><p>Following NO<sub>x</sub> interaction with water, oxygen and other chemicals in the atmosphere, acid rain can be formed, which harms sensitive ecosystems such as lakes and forests. NO<sub>x</sub> also can form the nitrate particles, which comprise the air hazy and photochemical smog leading to low visibility, ozone and other harmful substances [<xref ref-type="bibr" rid="scirp.100179-ref15">15</xref>]. In the atmosphere active particles are closely related to the oxidizing capacity [<xref ref-type="bibr" rid="scirp.100179-ref16">16</xref>]. Still, coastal waters become nutrient enrichment due to the augmentation of air NO<sub>x</sub>. The reaction of NO<sub>x</sub> with volatile organic compounds becomes an important precursor to increase the concentration of atmospheric PM<sub>2.5</sub> [<xref ref-type="bibr" rid="scirp.100179-ref17">17</xref>], which also contains nitrated polycyclic aromatic hydrocarbons (NPAHs) and oxygenated polycyclic aromatic hydrocarbons (OPAHs) [<xref ref-type="bibr" rid="scirp.100179-ref18">18</xref>].</p></sec><sec id="s2"><title>2. REMOVAL OF NITROGEN OXIDES FROM THE ATMOSPHERE</title><p>The two common methods to reduce NO<sub>x</sub> emissions are the selective catalytic reduction (SCR) and the selective non-catalytic reduction (SNCR), and SCR is considered the most widely-used method. Generally, SCR can remove around 90% NO<sub>x</sub> from emissions whereas SNCR can remove about 30% - 70% NO<sub>x</sub> from emissions. In fact, the NO<sub>x</sub> removed by SCR and SNCR are the NO<sub>x</sub> that has yet to enter into the atmosphere, because both SCR and SNCR are implemented in power plans, combustion engines, etc. So there is still a certain amount of NO<sub>x</sub> passing into the atmosphere even after SCR and SNCR treatment. For example, the total emission of Nr in China has been doubled and the emission of Nr in heavily polluted areas is about 10 times of that in other areas over the last 30 years [<xref ref-type="bibr" rid="scirp.100179-ref12">12</xref>]. This amount of NO<sub>x</sub> actually raises the health and environmental concerns. Currently, projected regulations for NO<sub>x</sub> control in the US, EU and Asia define the limit of NO<sub>x</sub> around 30 to 200 mg/NM<sup>3</sup>.</p><p>It is generally considered that NO could be very slowly removed from the atmosphere through wet and dry deposition [<xref ref-type="bibr" rid="scirp.100179-ref2">2</xref>]. However, we would like to indicate that an important natural source to remove NO<sub>x</sub> from the atmosphere has been so far ignored. This is tobacco (Nicotiana tabacum L.), which, to the best of our knowledge, is probably the only natural source to remove NO<sub>x</sub> from the atmosphere although smoking is harmful to human health.</p><p>The top part in <xref ref-type="fig" rid="fig1">Figure 1</xref> shows the overall scenario for NO<sub>x</sub> in the atmosphere, where the left-hand and right-hand sides represent the fresh air with its composition and the polluted air, respectively. The polluted air can form PM<sub>2.5</sub> whereas the fresh air comes from removal of NO<sub>x</sub> from the atmosphere. In the</p><p>middle of <xref ref-type="fig" rid="fig1">Figure 1</xref> shows how tobacco removes NO<sub>x</sub> from the atmosphere through nitrosition. There are two pathways for nitrosition, 1) nicotine can directly be nitrosated into the nicotine-derived nitrosamine ketone (NNK) [<xref ref-type="bibr" rid="scirp.100179-ref19">19</xref>], or 2) nicotine can be demethylated into nornicotine by P450 enzymes and then nornicotine can furthermore be nitrosated into N-nitrosonornicotine (NNN) [<xref ref-type="bibr" rid="scirp.100179-ref19">19</xref>]. The nitrosation for both nicotine and nornicotine requires a NO 2 − from environments [<xref ref-type="bibr" rid="scirp.100179-ref20">20</xref>] (yellow dashed circle in <xref ref-type="fig" rid="fig1">Figure 1</xref>). Thus, tobacco helps to remove NO<sub>x</sub> from the atmosphere as indicated by green dashed polygon in the left part in <xref ref-type="fig" rid="fig1">Figure 1</xref>. This nitrosition occurs during tobacco leaves change from green to yellow (lower left-hand part of <xref ref-type="fig" rid="fig1">Figure 1</xref>) rather than during smoking (lower right-hand part of <xref ref-type="fig" rid="fig1">Figure 1</xref>), so tobacco plantation is helpful to remove NO<sub>x</sub> from the atomosphere. On the other hand, NNN, NNK and NNAL are carcinogenic to humans [<xref ref-type="bibr" rid="scirp.100179-ref21">21</xref>] as indicated by red dashed polygon in the right part of <xref ref-type="fig" rid="fig1">Figure 1</xref>.</p><p>The nicotine content is about 19.63 mg/g tobacco [<xref ref-type="bibr" rid="scirp.100179-ref22">22</xref>] because the molar weight of nicotine is 162.23 g/mol, so 1 ton tobacco would have 19.63 kg nicotine (121 mol). If all of the nicotine would be converted to NNN/NNK, then this reaction requires 5.57 kg NO<sub>2</sub> (molar weight 46 g/mol), i.e. one-ton tobacco can absorb 5.57 kg NO<sub>2</sub> because the reaction consumes NO 2 − [<xref ref-type="bibr" rid="scirp.100179-ref20">20</xref>]. Usually, about 5% - 20% nicotine goes to NNN/NNK [<xref ref-type="bibr" rid="scirp.100179-ref19">19</xref>], then one-ton tobacco can absorb 0.28 - 1.10 kg NO<sub>2</sub>. It is estimated that all smoked cigarettes produce 12,000 - 47,000 tons of nicotine annually yearly [<xref ref-type="bibr" rid="scirp.100179-ref23">23</xref>]. Accordingly, these amounts of nicotine could neutralize 171.17 - 670.40 tons of NO<sub>2</sub> in terms of 5% - 20% nicotine goes to NNN/NNK yearly.</p></sec><sec id="s3"><title>3. EFFECTS OF DECREASED TOBACCO PLANTATION ON NO<sub>X</sub> REMOVAL FROM THE ATMOSPHERE</title><p>Because of tobacco’s harmful effects on humans, its plantation is actually decreasing year by year. For example, the tobacco plantation decreased from 1553 k hectares in 2014 to 1314 k hectares in 2015, and then further decreased to 1273 k hectares in 2016 in China. Accordingly, the tobacco production decreased from 2,994,471 tons in 2014 to 2,832,385 tons in 2015, and then further decreased to 2,725,685 tons in 2016 [<xref ref-type="bibr" rid="scirp.100179-ref24">24</xref>]. In fact, the tobacco production in China was 2,839,947 tons in 2008, and was peaked in 2012 with 3,408,142 tons. Since 2012, the tobacco production in China has been continuously decreasing and reached to 2,392,090 tons in 2017. Consequently, the removal of NO<sub>x</sub> from the atmosphere also decreased, and the un-removal of NO<sub>x</sub> should be progressively accumulated in the atmosphere because the lifetime of reactive nitrogen can range from a few weeks to few decades, even to 10<sup>2</sup> - 10<sup>3</sup> years in peatlands [<xref ref-type="bibr" rid="scirp.100179-ref15">15</xref>].</p><p><xref ref-type="fig" rid="fig2">Figure 2</xref> displays the accumulation of NO<sub>x</sub> with reference to the reduction of tobacco production in China and the world since 2008. As can be seen, the tobacco production has begun to decrease in China since 2012 (red bars in lower panel), while the removal of NO<sub>x</sub> also has begun to drop in the atmosphere since 2012 (red and black lines in upper panel). In the rest of world, the tobacco plantation decreases from 3564 k hectares in 2016 to 3529 k hectares in 2017 whereas the tobacco production increases from 6,399,092 tons in 2016 to 6,501,646 tons in 2017 [<xref ref-type="bibr" rid="scirp.100179-ref25">25</xref>]. So the accumulated NO<sub>x</sub> in the atmosphere does not change significantly in contrast to China.</p><p>Due to the reduction of tobacco plantation, several hundred tons of NO<sub>2</sub> per year are accumulating in atmosphere each year. Naturally, this amount is not big, but the accumulated amount of NO<sub>x</sub> over years would be significant. Indeed, it is not clear how many hectares of tobacco plantation have been terminated due to the harmful effects of tobacco since the industrial revolution. So arguably the accumulated NO<sub>x</sub> would be a lot. Because of the harmful effect to humans, the tobacco production would be expected to continuously reduce year by year. If the tobacco production in China will reduce 5% each year, then the accumulated NO<sub>x</sub> will reach 12,805.42 tons in 2030 (<xref ref-type="fig" rid="fig3">Figure 3</xref>).</p><p>Undeniably, the tobacco creates many healthy problems such as seven million people per year dying globally from tobacco use and exposure [26 - 28]. Also, tobacco industry creates environmental problems, i.e. deforestation [29,30], cigarette butt waste [31 - 33]. However, these problems are created by humans rather than tobacco itself.</p><p>At this present, it is unknown how to remove NO<sub>x</sub> from the atmosphere without tobacco, and then NO<sub>x</sub> would be accumulated in the atmosphere. A point of view is that humans have no need to remove NO<sub>x</sub> from the atmosphere because NO<sub>x</sub> is useful to agriculture and fishery, and the elimination of NO<sub>x</sub> emission using the current technologies generates too much CO<sub>2</sub> further leading to global warming [<xref ref-type="bibr" rid="scirp.100179-ref12">12</xref>] as the elimination of NO<sub>x</sub> consumes equal molar ammonia, whose production generates CO<sub>2</sub> [34,35].</p><p>However, it seems not acceptable to conduct the approach not to remove NO<sub>x</sub> from atmosphere for the sake of agriculture and fishery because NO<sub>x</sub> do have well-known unhealthy effects on humans and unwanted pollution effects on environment and ecology.</p></sec><sec id="s4"><title>4. CONCLUSION</title><p>Apparently, this is a dilemma: humans need to eliminate smoking for health reason through reduction of tobacco plantation, but humans also need to remove NO<sub>x</sub> from the atmosphere also for health reason. At this point, we feel tobacco innocent when humans consider it as a killer. Ecology is such a delicate system, where nature evolves various items to balance each other. In fact, tobacco plays an important role in the balance of nitrogen cycle by removing NO<sub>x</sub>, which generated by lighting, natural fire of biomass, and soil, from the atmosphere. Perhaps, we should blame ourselves, humans who use tobacco unwisely, rather than blame tobacco in nature. We are not in favor tobacco smoking, but its unique ability to remove NO<sub>2</sub> from atmosphere should not be ignored.</p></sec><sec id="s5"><title>ETHICAL APPROVAL STATEMENT</title><p>This article does not contain any studies with human or animal participants.</p></sec><sec id="s6"><title>ACKNOWLEDGEMENTS</title><p>This study was supported by National Natural Science Foundation of China (31560315), and Key Project of Guangxi Scientific Research and Technology Development Plan (AB17190534).</p></sec><sec id="s7"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec></body><back><ref-list><title>References</title><ref id="scirp.100179-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Stevens, C.J. (2019) Nitrogen in the Environment. Science, 363, 578-580.  
https://doi.org/10.1126/science.aav8215</mixed-citation></ref><ref id="scirp.100179-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Fowler, D., Coyle, M., Skiba, U., Sutton, M.A., Cape, J.N., Reis, S., Sheppard, L.J., Jenkins, A., Grizzetti, B., Galloway, J.N., Vitousek, P., Leach, A., Bouwman, A.F., Butterbach-Bahl, K., Dentener, F., Stevenson, D., Amann, M. and Voss, M. (2013) The Global Nitrogen Cycle in the Twenty-First Century. Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences, 368, 20130164. https://doi.org/10.1098/rstb.2013.0164</mixed-citation></ref><ref id="scirp.100179-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Levy, H., Moxim, W.J. and Kasibhatla, P.S. (1996) A Global Three-Dimensional Time-Dependent Lightning Source of Tropospheric NOx. Journal of Geophysical Research: Atmospheres, 101, 22911-22922.  
https://doi.org/10.1029/96JD02341</mixed-citation></ref><ref id="scirp.100179-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Tie, X.X., Zhang, R.Y., Brasseur, G. and Lei, W.F. (2002) Global NOx Production by Lightning. Journal of Atmospheric Chemistry, 43, 61-74. https://doi.org/10.1023/A:1016145719608</mixed-citation></ref><ref id="scirp.100179-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">David, A. (2005) Bridging Ocean Color Observations of the 1980s and 2000s in Search of Long-Term Trends. Journal of Geophysical Research, 110, 1-12. https://doi.org/10.1029/2004JC002620</mixed-citation></ref><ref id="scirp.100179-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">Watson, W.G., Margarita, E.C., Paul, G., O'Reilly, J.E. and Nancy, W.C. (2003) Ocean Primary Production and Climate: Global Decadal Changes. Geophysical Research Letters, 30, 1809.  
https://doi.org/10.1029/2003GL016889</mixed-citation></ref><ref id="scirp.100179-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Watson, W.G. and Margarita, E.C. (2002) Decadal Changes in Global Ocean Chlorophyll. Geophysical Research Letters, 29, 20-24. https://doi.org/10.1029/2002GL014689</mixed-citation></ref><ref id="scirp.100179-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Dionysios, E.R. (2005) Extending the Sea WiFS Chlorophyll Data Set Back 50 Years in the Northeast Atlantic. Geophysical Research Letters, 32, L06603. https://doi.org/10.1029/2005GL022484</mixed-citation></ref><ref id="scirp.100179-ref9"><label>9</label><mixed-citation publication-type="other" xlink:type="simple">van Vuuren, D.P., Bouwman, L.F., Smith, S.J. and Dentener, F. (2011) Global Projections for Anthropogenic Reactive Nitrogen Emissions to the Atmosphere: An Assessment of Scenarios in the Scientific Literature. Current Opinion in Environmental Sustainability, 3, 359-369. https://doi.org/10.1016/j.cosust.2011.08.014</mixed-citation></ref><ref id="scirp.100179-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Potter, C.S., Matson, P.A., Vitousek, P.M. and Davidson, E. (1996) Process Modeling of Controls on Nitrogen Trace Gas Emissions from Soils Worldwide. Journal of Geophysical Research, 101, 1361-1377.  
https://doi.org/10.1029/95JD02028</mixed-citation></ref><ref id="scirp.100179-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">Davidson, E.A. and Kingerlee, W. (1997) A Global Inventory of Nitric Oxide Emissions from Soils. Nutrient Cycling in Agroecosystems, 48, 37-50. https://doi.org/10.1023/A:1009738715891</mixed-citation></ref><ref id="scirp.100179-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Ozaki, S. (2017) NOx Is Best Compound to Reduce CO2. European Journal of Experimental Biology, 7, 12.  
https://doi.org/10.21767/2248-9215.100012</mixed-citation></ref><ref id="scirp.100179-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">US EPA (US Environmental Protection Agency) (2019)  
https://www.epa.gov/no2-pollution/basic-information-about-no2#What%20is%20NO2</mixed-citation></ref><ref id="scirp.100179-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Gu, B., Ge, Y., Ren, Y., Xu, B., Luo, W., Jiang, H., Gu, B. and Chang, J. (2012) Atmospheric Reactive Nitrogen in China: Sources, Recent Trends, and Damage Costs. Environmental Science &amp; Technology, 46, 9420-9427.  
https://doi.org/10.1021/es301446g</mixed-citation></ref><ref id="scirp.100179-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Wayne, R.P. (1991) Chemistry of Atmospheres. 2nd Edition, Clarendon Press, Oxford, UK.</mixed-citation></ref><ref id="scirp.100179-ref16"><label>16</label><mixed-citation publication-type="other" xlink:type="simple">Isaksen, I.S.A., Granier, C., Myhre, G., Berntsen, T.K., Dals&amp;#248ren, S.B., Gauss, M., Klimont, Z., Benestad, R., Bousquet, P., Collins, W., Cox, T., Eyring, V., Fowler, D., Fuzzi, S., J&amp;#246ckel, P., Laj, P., Lohmann, U., Maione, M., Monks, P., Prevot, A.S.H., Raes, F., Richter, A., Rognerud, B., Schulz, M., Shindell, D., Stevenson, D.S., Storelvmo, T. Wang, W.C., van Weele, M., Wild, M. and Wuebbles, D. (2009) Atmospheric Composition Change: Climate-Chemistry Interactions. Atmospheric Environment, 43, 5138-5192.  
https://doi.org/10.1016/j.atmosenv.2009.08.003</mixed-citation></ref><ref id="scirp.100179-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Yan, S. and Wu, G. (2016) Network Analysis of Fine Particulate Matter (PM2.5) Emissions in China. Scientific Reports, 6, 33227. https://doi.org/10.1038/srep33227</mixed-citation></ref><ref id="scirp.100179-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">Li, J., Yang, L., Gao, Y., Jiang, P., Li, Y., Zhao, T., Zhang, J. and Wang, W. (2019) Seasonal Variations of NPAHs and OPAHs in PM2.5 at Heavily Polluted Urban and Suburban Sites in North China: Concentrations, Molecular Compositions, Cancer Risk Assessments and Sources. Ecotoxicology and Environmental Safety, 178, 58-65.  
https://doi.org/10.1016/j.ecoenv.2019.04.009</mixed-citation></ref><ref id="scirp.100179-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">Siminszky, B., Gavilano, L., Bowen, S.W. and Dewey, R.E. (2005) Conversion of Nicotine to Nornicotine in Nicotiana tabacum Is Mediated by CYP82E4, a Cytochrome P450 Monooxygenase. Proceedings of the National Academy of Sciences of the United States of America, 102, 14919-14924.  
https://doi.org/10.1073/pnas.0506581102</mixed-citation></ref><ref id="scirp.100179-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">Lusso, M., Gunduz, I., Kondylis, A., Jaccard, G., Ruffieux, L., Gadani, F., Lion, K., Adams, A., Morris, W., Danielson, T., Warek, U. and Strickland, J. (2017) Novel Approach for Selective Reduction of NNN in Cigarette Tobacco Filler and Mainstream Smoke. Regulatory Toxicology and Pharmacology, 89, 101-111.  
https://doi.org/10.1016/j.yrtph.2017.07.019</mixed-citation></ref><ref id="scirp.100179-ref21"><label>21</label><mixed-citation publication-type="book" xlink:type="simple">IARC (2007) Smokeless Tobacco and Some Tobacco-Specific N-Nitrosamines. In: International Agency for Research on Cancer (Ed.), IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. World Health Organization, Lyon, France.</mixed-citation></ref><ref id="scirp.100179-ref22"><label>22</label><mixed-citation publication-type="other" xlink:type="simple">O’Connor, R.J., Schneller, L.M., Caruso, R.V., Stephens, W.E., Li, Q., Yuan, J. and Fong, G.T. (2015) Toxic Metal and Nicotine Content of Cigarettes Sold in China, 2009 and 2012. Tobacco Control, 24, iv55-iv59.  
https://doi.org/10.1136/tobaccocontrol-2014-051804</mixed-citation></ref><ref id="scirp.100179-ref23"><label>23</label><mixed-citation publication-type="other" xlink:type="simple">Novotny, T.E., Bialous, S.A., Burt, L., Curtis, C., da Costa, V.L., Iqtidar, S.U., Liu, Y., Pujari, S. and Tursan d'Espaignet E. (2015) The Environmental and Health Impacts of Tobacco Agriculture, Cigarette Manufacture and Consumption. Bulletin of the World Health Organization, 93, 877-880.  
https://doi.org/10.2471/BLT.15.152744</mixed-citation></ref><ref id="scirp.100179-ref24"><label>24</label><mixed-citation publication-type="other" xlink:type="simple">(2019) Statistics from Ministry of Agriculture and Rural Affairs of the People’s Republic of China.  
http://zdscxx.moa.gov.cn:8080/misportal/public/publicationRedStyle.jsp</mixed-citation></ref><ref id="scirp.100179-ref25"><label>25</label><mixed-citation publication-type="other" xlink:type="simple">Food and Agriculture Organization of the United Nations. (2019)  
http://www.fao.org/faostat/en/#data/QC/visualize</mixed-citation></ref><ref id="scirp.100179-ref26"><label>26</label><mixed-citation publication-type="other" xlink:type="simple">Ng, M., Freeman, M.K., Fleming, T.D., Robinson, M., Dwyer-Lindgren, L., Thomson, B., Wollum, A., Sanman, E., Wulf, S., Lopez, A.D., Murray, C.J. and Gakidou, E. (2014) Smoking Prevalence and Cigarette Consumption in 187 Countries, 1980-2012. JAMA, 311, 183-192. https://doi.org/10.1001/jama.2013.284692</mixed-citation></ref><ref id="scirp.100179-ref27"><label>27</label><mixed-citation publication-type="other" xlink:type="simple">GBD 2015 Tobacco Collaborators (2017) Smoking Prevalence and Attributable Disease Burden in 195 Countries and Territories, 1990-2015: A Systematic Analysis from the Global Burden of Disease Study 2015. Lancet, 389, 1885-1906. https://doi.org/10.1016/S0140-6736(17)30819-X</mixed-citation></ref><ref id="scirp.100179-ref28"><label>28</label><mixed-citation publication-type="other" xlink:type="simple">World Health Organization (2017) WHO Report on the Global Tobacco Epidemic, 2017: Monitoring Tobacco Use and Prevention Policies. WHO, Geneva.</mixed-citation></ref><ref id="scirp.100179-ref29"><label>29</label><mixed-citation publication-type="other" xlink:type="simple">Otanez, M.G., Mamudu, H.M. and Glantz, S.A. (2009) Tobacco Companies’ Use of Developing Countrie’ Economic Reliance on Tobacco to Lobby against Global Tobacco Control: the Case of Malawi. The American Journal of Public Health, 99, 1759-1771. https://doi.org/10.2105/AJPH.2008.146217</mixed-citation></ref><ref id="scirp.100179-ref30"><label>30</label><mixed-citation publication-type="other" xlink:type="simple">Otanez, M. and Glantz, S.A. (2011) Social Responsibility in Tobacco Production? Tobacco Companies’ Use of Green Supply Chains to Obscure the Real Costs of Tobacco Farming. Tobacco Control, 20, 403-411.  
https://doi.org/10.1136/tc.2010.039537</mixed-citation></ref><ref id="scirp.100179-ref31"><label>31</label><mixed-citation publication-type="other" xlink:type="simple">Novotny, T.E., Lum, K., Smith, E., Wang, V. and Barnes, R. (2009) Cigarettes Butts and the Case for an Environmental Policy on Hazardous Cigarette Waste. International Journal of Environmental Research and Public Health, 6, 1691-1705. https://doi.org/10.3390/ijerph6051691</mixed-citation></ref><ref id="scirp.100179-ref32"><label>32</label><mixed-citation publication-type="other" xlink:type="simple">Healton, C.G., Cummings, K.M., O'Connor, R.J. and Novotny, T.E. (2011) Butt Really? The Environmental Impact of Cigarettes. Tobacco Control, 20, i1. https://doi.org/10.1136/tc.2011.043729</mixed-citation></ref><ref id="scirp.100179-ref33"><label>33</label><mixed-citation publication-type="other" xlink:type="simple">Curtis, C., Collins, S., Cunningham, S., Stigler, P. and Novotny, T.E. (2014) Extended Producer Responsibility and Product Stewardship for Tobacco Product Waste. International Journal of Waste Resources, 4, 157.</mixed-citation></ref><ref id="scirp.100179-ref34"><label>34</label><mixed-citation publication-type="other" xlink:type="simple">Chambers, J.Q., Higuchi. N., Tribuzy, E.S. and Trumbore, S.E. (2001) Carbon Sink for a Century. Nature, 410, 429. https://doi.org/10.1038/35068624</mixed-citation></ref><ref id="scirp.100179-ref35"><label>35</label><mixed-citation publication-type="other" xlink:type="simple">Fourqurean, J.W., Duarte, C.M., Kennedy, H., Marba, N. and Holmer, M. (2012) Seagrass Ecosystems as a Globally Significant Carbon Stock. Nature Geoscience, 5, 505-509. https://doi.org/10.1038/ngeo1477</mixed-citation></ref></ref-list></back></article>