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When planning the protocol, it was obvious that the response time <strong>of</strong> the NO analyser limited<br />

the possible respiratory manoeuvres. I next considered online measurement <strong>of</strong> repeated single<br />

exhalations analogous to lung function testing versus exhaling into a reservoir that was then<br />

fed into the analysers. I briefly explored the use <strong>of</strong> a reservoir, as this had three theoretical<br />

advantages:<br />

o it would allow the measurement <strong>of</strong> a whole exhaled breath, whereas the online<br />

measurement which would control flow may mean that at low flows the subject would<br />

not reach complete exhalation before requiring to take another breath,<br />

o it would allow me as operator to put the collected sample through the machine at a<br />

constant flow instead <strong>of</strong> requiring the individual subject's voluntary but imperfect<br />

control,<br />

o performing tidal breathing over a set time or exhaling into a bag may have been easier<br />

when it came time to measure the children rather than relying on their being able to do<br />

controlled breaths into the analysers.<br />

At the time that I was commencing the experiments, there had been some studies into NO<br />

levels in exhaled air where a reservoir system had been used. <strong>The</strong> problems that had been<br />

detected and needed to be overcome involved No instability -<br />

a topic that has been touched<br />

on repeatedly. Firstly, although in O2-free and haemoglobulin-/ree solutions NO may be<br />

stable, in the presence <strong>of</strong> 02, NO levels rapidly decrease by 50Vo in 8-20 minutes. Secondly,<br />

NO is adsorbed by most plastics giving low and/or variable readings. NO also interacts with<br />

transition metals and with the sulftrydryl groups contained in rubber. Reservoir systems that<br />

had been used were polyvinyl chloride, rubber and fluoroethylene propylene' Preliminary<br />

studies in one group demonstrated that at levels <strong>of</strong> 5-30ppb there was no NO loss in the<br />

polyethylene reservoir at 6 and 12 hours post collection, although they commented that any<br />

loss may have been within the noise <strong>of</strong> the measurement that they were getting at that time <strong>of</strong><br />

10Zo (Schilling, Holzer et al. Igg4). Another group had found that using polyethylene tubing<br />

compared to Teflon tubing resulted in loss <strong>of</strong> NO presumably as it adsorbed to the former,<br />

particularly at higher (>40ppb) levels <strong>of</strong> NO (Kharitonov, logan-Sinclair et al. 1994). One<br />

group with a Douglas bag collection (an anaesthetic bag used to collect exhaled air, usually<br />

made <strong>of</strong> rubber) described no perceivable problems, but two other groups found them<br />

unreliable at higher NO concentrations (Kharitonov, logan-Sinclair et al. 1994)'<br />

Subsequently Mylar foil bags or balloons were used and seem to hold NO levels stable for at<br />

least 48 hours (Steerenberg, Nierkens et al. 2000). However, this research group also<br />

discarded the first part <strong>of</strong> exhalation to get lower respiratory tract samples and found that it<br />

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