01.12.2012 Views

View - ResearchSpace@Auckland - The University of Auckland

View - ResearchSpace@Auckland - The University of Auckland

View - ResearchSpace@Auckland - The University of Auckland

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

is set at 5ppm (AIHA 1966) based on pulmonary oedema that developed in welders who had a<br />

severe acute exposure to an estimated 9ppm <strong>of</strong> ozone (plus other pollutants) (Giel, Kleinfeld<br />

et al. t957). Fifteen to 20ppm is lethal to animals in two hours, exposure to 50ppm for one<br />

hour "would likely prove fatal to humans" (King 1963).<br />

4.7 Chapter summary<br />

This chapter has reviewed the possible compounds and methods that could be used to<br />

determine the level <strong>of</strong> NO based around the known pathway <strong>of</strong> formation from L-arginine to<br />

L-citrulline and NO, and the nitrogen compounds. <strong>The</strong> chemiluminescence technique was the<br />

most appropriate for use in measuring exhaled NO in humans. This analysis is based on the<br />

reaction <strong>of</strong> NO with ozone which produces light, and the light intensity has been shown to be<br />

directly proportional to the concentration <strong>of</strong> NO in the sample. <strong>The</strong> chemiluminscence<br />

technique appeared to be both appropriately sensitive and specific for NO for this purpose.<br />

<strong>The</strong> chemiluminescent NO analysers available at that time had been developed to measure<br />

NO in air pollution. <strong>The</strong> job now was to assess their use and examine what technical<br />

alterations were required to enable measurement <strong>of</strong> NO in exhaled air in humans in a reliable<br />

and reproducible way. This was needed before discussion as to what these levels meant, and<br />

before a trial <strong>of</strong> measurement in children. Initial testing showed that the response time <strong>of</strong> the<br />

analyser was too slow for our purpose initially, but a rerouting <strong>of</strong> the signal to a chart recorder<br />

decreased the response time and meant that it was practical for use for the studies that follow.<br />

Finally in this chapter, I have reviewed the toxicity <strong>of</strong> NO, NOz and ozone. Although I was<br />

only going to be measuring NO in exhalate and therefore it was unlikely to reach high levels,<br />

I was using NO calibration gases. NOz and ozone are the two gases created by this technique<br />

so I wanted to also assess their toxicity, although I was planning to remove them immediately<br />

by having them 'scrubbed' with a soda lime column and a charcoal column respectively.<br />

<strong>The</strong> next chapter examines the chemiluminescent analyser Model 2107 @asibi<br />

Environmental Corporation, Glendale, California, USA) in more detail, and the<br />

commencement <strong>of</strong> the machine and subject methodology studies. What was known about<br />

exhaled NO levels at the time <strong>of</strong> cornmencement <strong>of</strong> these studies in 1995 will also be<br />

reviewed here.<br />

108

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!