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Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra

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<strong>PM2.5</strong> <strong>in</strong> the UK<br />

106<br />

77. Early efforts towards understand<strong>in</strong>g secondary organic aerosol formation were<br />

based on the assumption that each SOA precursor formed a SOA surrogate<br />

species by atmospheric oxidation. When the concentrations of the SOA<br />

surrogates reached saturation <strong>in</strong> the gas phase, then any additional material<br />

formed was transferred to the <strong>particulate</strong> phase and equilibrium was restored<br />

(Pandis et al., 1992). Odum et al. (1996) built upon the absorptive partition<strong>in</strong>g<br />

approach of Pankow (1994) by assum<strong>in</strong>g that each SOA precursor formed<br />

several SOA surrogates, typically two products. A major improvement to this<br />

approach, referred to as the Volatility Basis Set (VBS), was proposed by Donahue<br />

et al. (2006). This assigns compounds to volatility categories which partition <strong>in</strong>to<br />

the particles accord<strong>in</strong>g to empirically-derived factors. These approaches based<br />

on absorptive partition<strong>in</strong>g are the basis for the methods of SOA modell<strong>in</strong>g<br />

that have been implemented <strong>in</strong> the CMAQ and CAMx models <strong>in</strong> the USA.<br />

When Utembe et al. (2005) tried to use absorptive partition<strong>in</strong>g to describe the<br />

<strong>in</strong>corporation of secondary organic <strong>matter</strong> <strong>in</strong>to airborne particles, they found<br />

that they needed to <strong>in</strong>crease the partition coefficients by a factor of several<br />

hundred <strong>in</strong> order to simulate the measured mass of organic <strong>matter</strong>. This has<br />

led to a recognition that most secondary organic compounds are appreciably<br />

oxidised and are therefore rather polar molecules which partition far more<br />

effectively <strong>in</strong>to aqueous droplets than organic liquids. This is lead<strong>in</strong>g to the<br />

development of models of the partition<strong>in</strong>g <strong>in</strong>to the aqueous phase of particles,<br />

but even that is likely to prove an <strong>in</strong>adequate descriptor of the partition process<br />

as there is now accumulat<strong>in</strong>g evidence for chemical reactions of secondary<br />

organic compounds with<strong>in</strong> the aqueous phase, hence displac<strong>in</strong>g the equilibrium<br />

further <strong>in</strong> favour of the condensed (particle) phase.<br />

78. Another important process affect<strong>in</strong>g semi-volatile materials is connected with<br />

the fact that the vapour pressure above a highly curved surface exceeds that<br />

above a less curved surface (the so-called Kelv<strong>in</strong> effect). The implication is that<br />

semi-volatile materials have a tendency to evaporate from smaller particles<br />

and condense <strong>in</strong>to larger particles, hence affect<strong>in</strong>g the PM size distribution.<br />

However, this process is not generally sufficiently rapid or important enough<br />

to <strong>in</strong>fluence the distribution of material <strong>in</strong>to the coarse particle fraction. One<br />

process, however, which is important <strong>in</strong> shift<strong>in</strong>g material from the f<strong>in</strong>e to<br />

the coarse particle mode <strong>in</strong>volves chemical reaction. In particular, nitric acid<br />

vapour, either aris<strong>in</strong>g directly from the oxidation of nitrogen dioxide or from<br />

the dissociation of ammonium nitrate (reaction (1) above), can react with<br />

the surface of coarse particles, as exemplified <strong>in</strong> equations (3) and (4) below<br />

for sodium chloride and calcium carbonate respectively. As a result, one acid<br />

displaces another and nitrate is <strong>in</strong>corporated <strong>in</strong>to coarse particles with the<br />

displacement of hydrogen chloride or carbon dioxide respectively <strong>in</strong>to the gas<br />

phase.<br />

NaCl + HNO3 → NaNO3 + HCl (3)<br />

CaCO3 + 2HNO3 → Ca(NO3)2 + H2O + CO2 (4)

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