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2.1 Introduction<br />

Chapter 2: Nitric oxide: pollutant to mediator<br />

<strong>The</strong>re are two lines <strong>of</strong> research, from quite disparate areas, that came together to make the<br />

studies described in Chapters 6, 7 and, 8 possible. <strong>The</strong> first is the measurement <strong>of</strong> air<br />

pollution, which has been increasingly important due to recognition that different pollutants<br />

cause or contribute to human disease, including nitrogen oxides; and the second is the<br />

increasing recognition <strong>of</strong> the importance <strong>of</strong> nitric oxide (NO) in biological systems in the last<br />

25 years. I will examine the developments in both <strong>of</strong> these areas that led to the<br />

commencement <strong>of</strong> the research described in this thesis.<br />

2.2 Pollution. nitrogen oxides and disease<br />

2.2.1 Concerns regarding pollution<br />

<strong>The</strong>re is now no doubt that episodes <strong>of</strong> air pollution have resulted in excess deaths. Concerns<br />

with regard to pollution and its effects on health date back to early last century, although the<br />

detrimental effects <strong>of</strong> poor air quality and poor housing have been recognised for far longer.<br />

Indoor air pollution can be traced to some 200,000 years ago, when humans first moved to<br />

colder climates necessitating the construction <strong>of</strong> shelters and use <strong>of</strong> indoor fires for cooking,<br />

warmth and light. <strong>The</strong>se mostly 'inside' fires likely resulted in an excess exposure to levels <strong>of</strong><br />

pollution as evidenced by the carbon soot found in prehistoric caves (Brims and Chauhan<br />

2005). Severe outdoor air pollution episodes have been documented since the early 17ft<br />

century but these became more frequent and more severe throughout the 19ft century. <strong>The</strong><br />

most definitive and well documented episodes were the great smogs that occurred in London,<br />

United Kingdom, in 1948, 1952 and 1962, with the most severe occurring in December 1952<br />

(Brims and Chauhan 2005). <strong>The</strong> smoke concentration at this time was 50 times above the<br />

average level, and this rise in pollution was followed by an equally sharp rise in mortality<br />

(Ministry <strong>of</strong> Health, UK 1954). An estimated human death toll <strong>of</strong> 4,000 occurred during this<br />

period which was three times the expected mortality for that time <strong>of</strong> year. Most deaths were<br />

among infants, the elderly and those with chronic respiratory disease (Anderson, ponce de<br />

Leon et al. 1996).In addition, emergency hospital admissions tripled for respiratory disease,<br />

and doubled for cardiovascular disease over the same period (Schwartz l99l). <strong>The</strong>se led to<br />

the Clean Air Act in 1956 and 1968 in the United Kingdom (UK), with further modifications<br />

to the Act made in 1993.<br />

49

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