Ground level ice nuclei particle measurements including Saharan dust events at a Po Valley rural site (San Pietro Capofiume, Italy)
Introduction
Insoluble aerosol particles that catalyze the formation of ice crystals in clouds are called ice nuclei particles (INP) (Vali et al., 2015) and can form ice through four different thermodynamic mechanisms: deposition, condensation-freezing, immersion-freezing, and contact-freezing.
Ice nuclei can be measured with a variety of techniques: mixing chambers (Langer, 1973, Bundke et al., 2008), expansion cloud chambers (Möhler et al., 2003, Tajiri et al., 2013), continuous flow diffusion chambers (Al-Naimi and Saunders, 1985, Rogers et al., 2001), and the filter method (Bigg, 1996, Klein et al., 2010, Langer and Rodgers, 1975). Each device has advantages and disadvantages. For instance, the continuous flow diffusion chamber (CFCD) cannot detect contact-freezing, and aerosol particles larger than about 2 μm need to be removed with an impactor to distinguish ice crystals reliably from background aerosols. In addition, the CFCD provides no information on the size distribution of INP. Besides cloud chambers and CFDC devices, many droplet-freezing techniques are available for immersion mode ice nucleation (Ardon-Dryer et al., 2011, Budke and Koop, 2015, Knopf and Alpert, 2013, Murray et al., 2011, Vali, 2008).
Membrane filter techniques have been used in different forms for a number of years. Particle sampling on filters can be convenient, because the samples can be processed later without nuclei degradation, and aerosol activation can be measured in all size ranges, and can simulate deposition, condensation and contact nucleation modes (Bigg, 1990a, Cooper, 1980, Stevenson, 1968). The temporal resolution is usually no better than 20–30 min. Early designs used a static vapour diffusion field, but several factors led to an underestimation of the ice nuclei (volume effect, chamber height effect, vapour depletion on the filter around growing crystals and hygroscopic particles, vapour competition between ice nuclei). However, Bigg (1990a) concluded that with suitable precautions the filter method is adequate for INP measurements. In order to circumvent some of the problems arising with the static chamber, a dynamic chamber filter processing chamber (DFPC) was introduced (Langer and Rodgers, 1975).
CFDC measurements sometimes yielded INP higher concentrations than the filter method (Al-Naimi and Saunders, 1985, Hussain and Saunders, 1984). In simultaneous comparison, Hussain and Kayani (1988) found that at water saturation their CFDC detected fourteen times as many nuclei than filters processed in a static chamber. However, in a similar comparison Saunders and Al-Juboory (1988) found nearly equivalent results between a CFDC and DFPC filters at − 16 °C and supersaturation with respect to water between − 3% and + 5%.
Plaude et al. (1996) performed simultaneous measurements on INP concentration using a cloud chamber and a filter technique on the territory of the former USSR over a five-year period. The agreement between the results obtained by the two techniques was found to depend on the overall pollution of the region, and is higher in a relatively clean atmosphere (INPchamber/INPfilter ~ 1.9), and lower in an urban area which is more polluted (INPchamber/INPfilter in the range 4 to 7).
Most INP measurements concern total INP number concentrations with less emphasis on determining their size distribution. In point of fact, information on airborne INP size distribution may be helpful to identify the predominant INP sources. For instance, primary biological aerosol particles can span physical dimensions of a few nanometers to hundred of micrometers (Huffman et al., 2012), whereas black carbon particles are mainly in the submicron range (Clarke et al., 2004, Schwarz et al., 2008). Therefore, size-resolved measurements of ice nucleating particles should be performed and even super-micron particles should be considered. Previous field size-resolved INP measurements are scarce (Berezinski et al., 1988, Huffman et al., 2013, Rosinski et al., 1986, Rosinski et al., 1988, Santachiara et al., 2010).
Mason et al. (2016) recently attempted to tackle this problem using a technique which combines aerosol particle collection by a cascade inertial impactor (Moudi MSP Corp., USA) and a microscope-based immersion-freezing apparatus. The results showed that coarse aerosol particles are a significant component of the ice nuclei population in many different ground-level environments (see Table 2a, Table 2b of the paper).
Our paper reports the results of two experimental campaigns performed with the filter method at a rural background site. This procedure activates all size ranges of aerosol in the deposition and condensation-freezing modes for the examination of fine and coarse particles. Even if the sampling site is a rural area, it is surrounded by highly populated industrialized regions.
Our measurements were performed at ground level. To date, few INP measurements at ground level in low polluted areas have been reported in the literature. Ground-based INP measurements are important as INP can originate from the surface and be transported to higher levels (Ardon-Dryer et al., 2011, Alizadeh-Choobari et al., 2015, Després et al., 2012, Mamouri and Ansmann, 2015). The aim of the campaigns was to characterize the considered site with respect to certain INP properties, i.e. concentrations, and their relationship with particle number concentration, diurnal variations and possible sources.
Section snippets
Experimental
Two experimental campaigns were performed at the “Giorgio Fea” Meteorological Station in San Pietro Capofiume (SPC), a rural site located at about 30 km north-east of Bologna in the eastern Po Valley (44°39′16.33″N; 11°37′22.28″E) in the periods 10–21 February 2014 and 19–30 May 2014. The first campaign was characterized by air masses from the North Atlantic at the beginning of the sampling period, and from Northern Africa in the central part of the campaign, giving rise to Saharan dust episodes
Results and discussion
Table 1a shows meteorological data, INP and particle number concentrations for each sampling day of the first campaign, while the INP averaged value and the INP ratio between PM1 and PM10 are given in Table 1b. The data of the second campaign are shown in Table 2a, Table 2b.
In a few cases, the INP concentration in PM1 fraction, reported in the above cited Tables, is higher than the corresponding PM10 concentration. It is known that INP measurements performed by off-line methods include a
Conclusion
The main conclusions of the campaigns performed at San Pietro Capofiume near Bologna in the periods 10–21 February 2014 and 19–30 May 2014 can be summarized as follows:
- a)
Prevalently higher average INP concentrations were measured in the morning with respect to the afternoon, in the PM1 fraction with respect to PM1–10 and at water super-saturation with respect to water sub-saturation. Only in the first campaign, at Sw = 1.01, there was a prevalence of INPPM1–10 (coarse fraction) with respect to INP
Acknowledgments
This work is funded by FP7-ENV-2013 Project BACCHUS (grant no. 603445) and by the CNR funded bilateral project Air-Sea Lab: Climate air pollution interaction in coastal environment (http://www.isac.cnr.it/airsealab).
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