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Handbook of Solvents - George Wypych - ChemTech - Ventech!

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1194 Michelle Bergin, Armistead Russell<br />

Although many types <strong>of</strong> reactions are involved, 4,13,16,17 the major processes for most<br />

VOCs can be summarized as follows:<br />

VOC + OH → RO 2 + products [17.4.10a]<br />

RO 2 + NO → NO 2 + radicals [17.4.10b]<br />

radicals → ...→ OH + products [17.4.10c]<br />

products → ...→...+ CO 2<br />

[17.4.10d]<br />

The last two pseudo-reactions given comprise many steps, and the products <strong>of</strong>ten include<br />

formaldehyde, carbon monoxide and organonitrates. The rate <strong>of</strong> ozone increase<br />

caused by these processes depends on the amount <strong>of</strong> VOCs present, the type <strong>of</strong> VOCs present,<br />

and the level <strong>of</strong> OH radicals and other species with which the VOCs can react. One <strong>of</strong><br />

the major determinants <strong>of</strong> a compound’s impact on ozone is the rate <strong>of</strong> the reaction <strong>of</strong> the<br />

particular VOC with the hydroxyl radical via reaction [17.4.10a], above. The total amount<br />

<strong>of</strong> ozone formed is largely determined by the amount <strong>of</strong> VOC and NO x available.<br />

The dependence <strong>of</strong> O 3 production on the initial amounts <strong>of</strong> VOC and NO x is frequently<br />

represented by means <strong>of</strong> an ozone isopleth diagram. An example <strong>of</strong> such a diagram is<br />

shown in Figure 17.4.1. The diagram is a contour plot <strong>of</strong> ozone maxima obtained from a<br />

large number <strong>of</strong> air quality model simulations using an atmospheric chemical mechanism.<br />

Initial concentrations <strong>of</strong> VOC and NO x are varied; all other variables are held constant. Notice<br />

that there is a “ridge” along a certain VOC-to-NO x ratio where the highest ozone concentrations<br />

occur at given VOC levels. This is referred to as the “optimum” VOC-to-NO x<br />

ratio. While the atmosphere is more complicated than this idealized system, important features<br />

are very similar.<br />

VOC-to-NO x ratios sufficiently low to retard ozone formation from an optimum ratio<br />

(represented in the upper left quadrant <strong>of</strong> Figure 17.4.1) can occur in central cities and in<br />

plumes immediately downwind <strong>of</strong> strong NO x sources. Rural environments tend to be characterized<br />

by fairly high VOC-to-NO x ratios because <strong>of</strong> the relatively rapid removal <strong>of</strong> NO x<br />

Figure 17.4.1. Ozone isopleth diagram showing the dependencies <strong>of</strong> ozone on varying levels <strong>of</strong> initial VOCs and<br />

NO x. Concentrations are given in ppb. [Adapted from M.S. Bergin et al., Enc. <strong>of</strong> Env. Analysis and Remediation,<br />

29, 3029, (1998)]

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