Abstract
Abstract. The wet removal of black carbon aerosol (BC) in the atmosphere is a crucial factor in determining its atmospheric lifetime and thereby the vertical and horizontal distributions, dispersion on local and regional scales, and the direct, semi-direct and indirect radiative forcing effects. The in-cloud scavenging and wet deposition rate of freshly emitted hydrophobic BC will be increased on acquisition of more-hydrophilic components by coagulation or coating processes. The lifetime of BC is still subject to considerable uncertainty for most of the model inputs, which is largely due to the insufficient constraints on the BC hydrophobic-to-hydrophilic conversion process from observational field data. This study was conducted at a site along UK North Norfolk coastline, where the BC particles were transported from different regions within Western Europe. A hygroscopicity tandem differential mobility analyser (HTDMA) was coupled with a single particle soot photometer (SP2) to measure the hygroscopic properties of BC particles and associated mixing state in real time. In addition, a Soot Particle AMS (SP-AMS) measured the chemical compositions of additional material associated with BC particles. The ensemble of BC particles persistently contained a less-hygroscopic mode at a growth factor (gf) of around 1.05 at 90% RH (dry diameter 163 nm). Importantly, a more-hygroscopic mode of BC particles was observed throughout the experiment, the gf of these BC particles extended up to ~1.4–1.6 with the minimum between this and the less hygroscopic mode at a gf ~1.25, or equivalent effective hygroscopicity parameter κ ~0.1. The gf of BC particles (gfBC) was highly influenced by the composition of associated soluble material: increases of gfBC were associated with secondary inorganic components, and these increases were more pronounced when ammonium nitrate was in the BC particles; however the presence of secondary organic matter suppressed the gfBC below that of pure inorganics. The Zdanovskii-Stokes-Robinson (ZSR) mixing rule captures the hygroscopicity contributions from different compositions within ±30% compared to the measured results, however is subject to uncertainty due to the complex morphology of BC component and potential artefacts associated with semivolatile particles measured with the HTDMA. This study provides detailed insights on BC hygroscopicity associated with its mixing state, and the results will importantly constrain the microphysical mixing schemes of BC as used by a variety of high level models. In particular, this provides direct evidence to highlight the need to consider ammonium nitrate ageing of BC particles because this will result in particles becoming hydrophilic on much shorter timescales than for sulphate formation, which is often the only mechanism considered.
Highlights
Black carbon, or soot aerosols (BC) as a strong absorber of solar radiation, significantly perturb the radiative budget of the atmosphere, contribute to radiative forcing through heating the lower atmosphere (Ramanathan and Carmichael, 2008) and cause modifications to cloud cover through the semi-direct effect (Koch and Del Genio, 2010)
A more-hygroscopic mode of black carbon aerosol (BC) particles was observed throughout the experiment, the gf of these BC particles extended up to ∼1.4–1.6 with the
The refractory BC particles (rBC) mass fraction in total sub-micron aerosol mass is calculated as the rBC mass divided by the sum of ammonium, nitrate, sulphate, organic and chloride mass measured by the cToF-AMS
Summary
Soot aerosols (BC) as a strong absorber of solar radiation, significantly perturb the radiative budget of the atmosphere, contribute to radiative forcing through heating the lower atmosphere (Ramanathan and Carmichael, 2008) and cause modifications to cloud cover through the semi-direct effect (Koch and Del Genio, 2010). A variety of laboratory studies have been conducted to investigate how coatings or chemical reactions occurring on the soot particle could modify its initial low hygroscopicity to the point where eventually the soot particle could exhibit CCN activity These experiments include investigations on soot from diesel engines (Weingartner et al, 1997; Gysel et al, 2003; Petzold et al, 2005; Tritscher et al, 2011), wood burning (Henning et al, 2010; Snider et al, 2010) and a variety of flame generators using different chemical fuels (Zuberi et al, 2005; Zhang et al, 2008; Koehler et al, 2009). The key instruments closely related to this study are described in detail in 2.1 and 2.2
Published Version (
Free)
Talk to us
Join us for a 30 min session where you can share your feedback and ask us any queries you have