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Atmos. Chem. Phys. Discuss., 9, 4653–4689, 2009 Atmospheric www.atmos-chem-phys-discuss.net/9/4653/2009/ ACPD © Author(s) 2009. This is distributed under and Physics 9, 4653–4689, 2009 the Creative Commons Attribution 3.0 License. Discussions

This discussion paper is/has been under review for the journal Atmospheric Chemistry Measurements of and Physics (ACP). Please refer to the corresponding final paper in ACP if available. of inorganic salt

M. Kuwata and Y. Kondo

Measurements of particle masses of Title Page inorganic salt particles for calibration of Abstract Introduction cloud condensation nuclei counters Conclusions References Tables Figures M. Kuwata and Y. Kondo

Research Center for Advanced Science and Technology, the University of Tokyo, Tokyo, Japan J I

Received: 7 January 2009 – Accepted: 23 January 2009 – Published: 24 February 2009 J I Correspondence to: M. Kuwata ([email protected]) Back Close

Published by Copernicus Publications on behalf of the European Geosciences Union. Full Screen / Esc

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4653 Abstract ACPD We measured the mobility equivalent critical dry diameter for CCN activation (dc me) 9, 4653–4689, 2009 and the particle of size-selected (NH4)2SO4 and NaCl particles to calibrate a CCN counter (CCNC) precisely. The CCNC was operated downstream of a differen- 5 tial mobility analyzer (DMA) for the measurement of dc me. The particle mass was Measurements of measured using an aerosol particle mass analyzer (APM) operated downstream of particle masses of the DMA. The measurement of particle mass was conducted for 50–150-nm particles. inorganic salt −3 Effective (ρeff) of (NH4)2SO4 particles were 1.67–1.75 g cm , which corre- particles spond to the dynamic shape factors (χ) of 1.01–1.04. This shows that (NH4)2SO4 M. Kuwata and Y. Kondo 10 particles are not completely spherical. In the case of NaCl particles, ρeff was 1.75– 1.99 g cm−3 and χ was 1.05–1.14, demonstrating that their particle shape was non- spherical. Using these experimental data, the equivalent critical dry diameter Title Page (dc ve) was calculated, and it was used as an input parameter for calculations of critical supersaturation (S). Several models were used for the calculation of Abstract Introduction 15 water activity. When the Pitzer model was employed for the calculations, the critical S Conclusions References calculated for (NH4)2SO4 and NaCl agreed to well within the uncertainty of 2% (rela- tive). This result demonstrates that the use of the Pitzer model for the calibration of Tables Figures CCNCs gives the most probable value of S.

J I 1 Introduction J I

20 The number concentration of cloud condensation nuclei (CCN) is an important param- Back Close eter for cloud microphysics. The number concentration and size distribution of cloud droplets are affected by changes in the CCN number concentration. Consequently, Full Screen / Esc CCN number concentration is indirectly related to radiative forcing and the hydrological cycle. Thus, it is important to measure the CCN number concentration and CCN ac- Printer-friendly Version 25 tivity of atmospheric particles precisely (Twomey, 1974; Lohmann and Feichter, 2005, Interactive Discussion and references therein). 4654 CCN number concentration is measured using a CCN counter (CCNC). Several types of CCNCs have been developed (McMurry, 2000; Nenes et al., 2001; Roberts ACPD and Nenes, 2005). In most CCNCs, supersaturated conditions are produced by cre- 9, 4653–4689, 2009 ating a difference on wetted walls. CCN-active particles grow to large 5 droplets in the artificial supersaturated environment. The number of droplets is then counted using an optical particle counter (OPC) (e.g., Stratmann et al., 2004; Roberts Measurements of and Nenes, 2005) or a charge coupled device (CCD) camera (Otto et al., 2002). The particle masses of most important parameter in CCN measurement is the precise value of the supersatu- inorganic salt ration (S) inside the instrument, which ensures compatibility with other studies (Seinfeld particles 10 and Pandis, 2006). S inside a CCNC can be calculated theoretically (e.g., Nenes et al., 2001; Stratmann M. Kuwata and Y. Kondo et al., 2004; Roberts and Nenes, 2005). These theoretical studies are indispensable for developing CCNCs. However, theoretical results are not sufficient for practical ob- Title Page servations and experiments as the ideal instrument does not exist and instrumental 15 conditions can change with time. Therefore, routine calibrations are required for the op- Abstract Introduction eration of CCNCs (e.g., Rose et al., 2008). Unfortunately, there are no instruments that can measure S directly; thus, we have to choose an alternative method for calibration. Conclusions References

In most CCN studies, the critical dry diameters (the threshold diameters for CCN acti- Tables Figures vation, dc) of laboratory-generated particles are measured using a CCNC connected to 20 a differential mobility analyzer (DMA) in tandem to calibrate the instruments. Then, the J I critical S values corresponding to the observed dc values are calculated using Kohler¨ theory. (NH4)2SO4 is the most frequently used compound for calibration (e.g., Kumar J I et al., 2003; VanReken et al., 2005), and some studies also use NaCl particles (Riss- Back Close man et al., 2007; Shilling et al., 2007; Rose et al., 2008). However, the critical S of 25 (NH4)2SO4 particles is strongly dependent on thermodynamics models (Kreidenweis Full Screen / Esc et al., 2005), and the magnitude of the variation is large enough to change the inter- pretation of the observation results (e.g., Mochida et al., 2006). In the case of NaCl, Printer-friendly Version the differences between thermodynamics models are not as significant as those of Interactive Discussion (NH4)2SO4, and there is an excellent thermodynamics model that is based on the vari- 4655 ous experimental data (Archer, 1992). However, it is difficult to estimate the critical S of a DMA-selected NaCl particle because of its non-spherical shape (Kelly and McMurry, ACPD 1992; Zelenyuk et al., 2006a). In previous studies, S values calculated using the two 9, 4653–4689, 2009 different compounds did not always agree, and the magnitude of the difference was up 5 to 10% (relative) (e.g., Shilling et al., 2007). These discrepancies were possibly caused by the uncertainties described above. Rose et al. (2008) have described that the cali- Measurements of bration results using (NH4)2SO4 and NaCl agrees well if the dynamic shape factor (χ) particle masses of of NaCl is assumed to be 1.08, although they acknowledged that further systematic inorganic salt investigations are still needed for more quantitative measurements. particles 10 In this study, we measured the masses of (NH4)2SO4 and NaCl particles generated for the calibration of a CCNC using an aerosol particle mass analyzer (APM). The APM M. Kuwata and Y. Kondo can select particles according to their mass by virtue of the balance between electro- static and centrifugal forces (Ehara et al., 1996). Thus, the combination of a DMA and Title Page an APM (DMA-APM system) enables us to measure the mass of DMA-selected par- 15 ticles, and we can obtain parameters related to particle morphology such as χ (e.g., Abstract Introduction Park et al., 2004). Then, S values inside the CCNC were calculated using the mea- Conclusions References sured dc, particle mass, and several thermodynamics models. The calculated S values are compared to investigate the consistency of the experimental results of (NH4)2SO4 Tables Figures and NaCl particles.

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20 2 Theoretical background J I

2.1 The relationship of dme and dve Back Close

Full Screen / Esc In this section, we summarize the relationship between mobility diameter (dme) and volume equivalent diameter (dve), because the conversion of dme to dve is needed to prepare an input parameter for calculations based on Kohler¨ theory (Sect. 2.2). For Printer-friendly Version 25 spherical particles, dme is equal to dve. However, particles are not always spherical. Interactive Discussion Using the effective (ρeff), dme is related with dve by the following equation (De- 4656 Carlo et al., 2004):

π 3 π 3 ACPD mp = ρmdve = ρeffdme (1) 6 6 9, 4653–4689, 2009 or s Measurements of 3 ρeff dve = dme (2) particle masses of ρm inorganic salt 5 where mp is particle mass, and ρm is the material density. In the DMA-APM system, particles dme is known as it is prescribed by the DMA, and mp can be measured using the APM. Thus, if we apply this experimental system to particles composed of single compounds, M. Kuwata and Y. Kondo q  we can obtain the conversion factor 3 ρeff easily, as ρ is a known parameter. ρm m Title Page dve and dme can also be related by χ, which is defined as the ratio of the drag force 10 acting on spherical particles with diameters of dve and dme. Under the equilibrium Abstract Introduction sphere approximation (ESA) (Dahneke, 1973), χ is defined by the following equation (Kasper, 1982): Conclusions References

Zp(dve) C (d ) d Tables Figures χ = = C ve me (3) Zp(dme) dve CC(dme) J I where Zp is the electrical mobility, and the slip correction factor (CC) can be calculated 15 from the following equation (Allen and Raabe, 1985): J I

   Back Close 2λ −0.999 C = 1 + 1.142 + 0.558 exp (4) C   2λ  Full Screen / Esc dp dp

where λ is mean free path of air. Although ESA is a good approximation for slightly Printer-friendly Version non-spherical particles and it is useful to calculate χ from experimental results, it is not Interactive Discussion always appropriate to use ESA for studies of χ in the transition regime (χt), especially 4657 for particles that are highly non-spherical (Dahneke, 1973). For this purpose, the ad- justed sphere approximation (ASA) was introduced (Dahneke, 1973). Using ASA, χt ACPD can be written as follows (DeCarlo et al., 2004): 9, 4653–4689, 2009 C (d ) χ χ C ve t = c   (5) C χf d Measurements of C χc ve particle masses of 5 where, χf and χc denote χ in the free molecular regime and continuous regime, re- inorganic salt spectively. particles

2.2 Kohler¨ theory M. Kuwata and Y. Kondo

The water activity of an aqueous solution (aw ) is equal to the saturation ratio of water vapor (Robinson and Stokes, 2002) Title Page

pw 10 = a (6) Abstract Introduction 0 w pw Conclusions References 0 where pw is the vapor of water and pw is the saturation vapor pressure of Tables Figures water. For an aqueous solution in -liquid equilibrium, pw is equal to the equilibrium water vapor pressure of a solution having a flat surface. In the case of particles, the J I equilibrium vapor pressure of the solution (pw aerosol) is affected by the curvature of the 15 droplet (Kelvin effect). The magnitude of this effect is described as follows (Seinfeld J I and Pandis, 2006) ! Back Close pw aerosol 4σMw = exp (7) Full Screen / Esc pw RT ρw Dp

where σ is surface tension, Mw is the molecular weight of water, R is the , Printer-friendly Version T is temperature, ρw is the density of water, and Dp is the droplet diameter. Substituting Interactive Discussion

4658 Eq. (7) into (6), we get ! p 4σM ACPD s = w aerosol = a exp w (8) 0 w RT ρ D 9, 4653–4689, 2009 pw w p

where s is the saturation ratio of water vapor. Thus, aw is needed to calculate s. Measurements of There are several expressions for the aw of solution. One of the most commonly used 5 expressions is the equation defining the molal osmotic coefficient (ϕ) (Robinson and particle masses of Stokes, 2002); inorganic salt particles υmMw ln aw = − ϕ , (9) 1000 M. Kuwata and Y. Kondo where υ is the stoichiometric number of solute ions and molecules, and m () is defined as follows: Title Page 1000ms 10 m = . (10) Msmw Abstract Introduction

In Eq. (10), ms is the mass of solute, Ms is molecular weight of solute, and mw is the Conclusions References mass of water in aqueous solution. The van’t Hoff factor (i) is also frequently used to express aw . The value i is defined as follows: Tables Figures nw aw = (11) nw + ins J I

15 where n and n are the numbers of moles of water (solvent) and solute, respectively w i J I (Pruppacher and Klett, 1997). As an example of another expression, Tang and Munkel- Back Close witz (1994) and Tang (1996) expressed aw as a polynomial equation with respect to the concentration of the solution (weight percent). Thermodynamics models employed Full Screen / Esc for the present study is summarized in Appendix B. Among the models summarized 20 in Appendix B, we regard that of Archer (1992) as the most reliable, as it is based Printer-friendly Version on a number of experimental results, including the concentration range that is impor- tant for CCN activation (Clegg, 2007). We next derive Kohler¨ theory using ϕ. Similar Interactive Discussion equations can easily be obtained for other expressions of aw . 4659 Using Eqs. (8)–(10), we get 4σM M m ACPD ln s = w − υϕ w s . (12) RT ρw Dp Msmw 9, 4653–4689, 2009

In Eq. (12), we need to know ms for the calculation of s. It is equal to mp when the Measurements of particle is composed of a single component. Then, Eq. (12) can be rewritten using dve 5 (Eq. 1), particle masses of inorganic salt 3 4σMw Mw ρmdve particles s − υϕ ln =   (13) RT ρw Dp 3 3 Msρw Dp − dve M. Kuwata and Y. Kondo

When we calculate s of a single particle as a function of Dp, it has the maximum value. S S S corresponding to this value is called the critical . If the particle is subjected to an Title Page greater than the critical S, the particle can grow into a cloud droplet. Abstract Introduction

10 3 Experiment Conclusions References

3.1 Particle generation and classification Tables Figures

The experimental setup used in this study is shown in Fig. 1. Aqueous solutions J I (∼0.1 wt.%) of (NH4)2SO4 and NaCl were prepared and introduced into an atomizer (TSI model 3075). Chemical properties of these compounds are summarized in Ta- J I 15 ble 1. Synthetic compressed air supplied from a gas cylinder was used for this atom- Back Close izer. Particles were dried by passing them through two diffusion dryers (TSI model 3062) connected in tandem. Silica gel used for the diffusion dryers was regenerated Full Screen / Esc before each run. Then, particles were charged with a 241Am neutralizer, and their size was selected by a DMA (TSI model 3081). The sheath and sample flow rates of the Printer-friendly Version 20 DMA were set at 3.0 lpm and 0.3 lpm, respectively. The size-selection of the DMA was Interactive Discussion checked by measuring size-distributions of the polystyrene latex (PSL) particles listed 4660 in Table 2. The peak diameters of the size-distributions agreed with the diameters of the PSL to within the errors given by the manufacturers. In this paper, we report diam- ACPD eters by the set values of the DMA. The random error in diameter estimated from the 9, 4653–4689, 2009 PSL measurements was less than 0.5%.

5 3.2 CCN measurement Measurements of particle masses of The CCN measurement part of Fig. 1 was used to determine the mobility equivalent inorganic salt d critical dry diameter ( c me). A CCNC (Droplet Measurement Technologies) (Roberts particles and Nenes, 2005) was used to measure CCN number concentration, and a conden- sation particle counter (CPC: TSI model 3022) was used for CN measurement. The M. Kuwata and Y. Kondo 10 sample flow from the DMA was mixed with dry compressed particle-free air (0.5 lpm) to keep the sample flow rate of the DMA at 0.3 lpm. Dilution air was produced from air in the laboratory using a pure air generator (PAG 003, ECO Physics) and a high- Title Page efficiency particulate air (HEPA) filter. The flow rate of the dilution air was controlled by Abstract Introduction a mass flow controller. The sample flow and the sheath flow rates of the CCNC were 15 set to 0.045 lpm and 0.455 lpm, respectively. Two temperature gradient (∆T ) conditions Conclusions References of the thermal gradient chamber inside the CCNC were used as shown in Table 3 so that the measurement was performed at two S values. Solenoid pumps used for water Tables Figures circulation in the CCNC were replaced by external peristaltic pumps for flow stabiliza- tion. The air circulation system for the OPC drying system was plugged to stabilize J I 20 the airflow in the chamber. The reproducibility of dc me measurement was tested using J I (NH4)2SO4 particles. The random errors associated with dc me measurement were 0.1 and 0.3 nm for ∆T 1 and ∆T 2, respectively. The influence of this error on the critical S Back Close was calculated to be negligibly small (less than 0.001% (absolute)). Full Screen / Esc 3.3 DMA-APM system Printer-friendly Version

25 An APM (APM 302, KANOMAX JAPAN, Inc.) was employed to measure mp of particles Interactive Discussion prescribed by the DMA. The mp selected by the APM is described as follows (Ehara et 4661 al., 1996), ACPD neVAP M mp = (14) 2 2 9, 4653–4689, 2009 ω r ln(r2/r1)

where n is the number of charges, e is the elementary charge, VAP M is the voltage Measurements of applied to the APM, ω is the rotation speed, and r, r1, and r2 are the center, inner, 5 and outer radii of the APM, respectively. Particle number concentration downstream particle masses of inorganic salt of the APM was measured by a CPC (TSI model 3022). To calibrate mp and ρeff measurement by the DMA-APM system, the masses of DMA-selected PSL particles particles were measured. Figure 2 shows an example of a mass distribution of DMA-selected M. Kuwata and Y. Kondo PSL particles. The peak of the distribution, which corresponds to mp, was obtained 10 by fitting the distribution by a Gaussian function. Density calculated using Eqs. (14) and (1) (in this case, we can assume d d , as PSL particles have spherical shape) ve= me Title Page agreed with the values given by the manufacturers to within 5%, and this difference was corrected for inorganic salt particles. The random error associated with the ρeff Abstract Introduction measurement by the DMA-APM system was 1%, estimated from PSL measurements. Conclusions References 15 The measurement of ρeff was performed four times. RUN1 and RUN2 were per- formed prior to CCN measurement. RUN3 was performed soon after (within 5 h) the Tables Figures CCN measurement at ∆T 1, and we concentrated on the size range that is important

for CCN activation under these conditions. Likewise, RUN4 was performed soon after J I the CCN measurement at ∆T 2. J I

Back Close 20 4 Results and discussion

Full Screen / Esc 4.1 dc me of inorganic salt particles

Printer-friendly Version Figure 3 shows experimental results for the CCN measurement of (NH4)2SO4 and NaCl particles. CCN/CN ratios monotonically increase with increasing diameter and Interactive Discussion

4662 approach unity. The CCN/CN ratios are fitted by a sigmoid function (Eq. 15): CCN b ACPD = a + (15) CN  dc me−dme  9, 4653–4689, 2009 1 + exp c

where a, b, and c are constants determined by the fitting. dc me values were 115.2 nm Measurements of (∆T 1) and 75.3 nm (∆T 2) for (NH4)2SO4 and 94.7 nm (∆T 1) and 63.2 nm (∆T 2) for particle masses of 5 NaCl, respectively. inorganic salt particles 4.2 ρeff, χ and dve of inorganic salt particles M. Kuwata and Y. Kondo Figure 4 shows an example mass distribution of DMA-selected NaCl particles mea- sured using the APM and CPC. As in the case of PSL, these distributions were fitted by Gaussian functions to obtain the peak of the distribution, and then we obtained Title Page 10 the particle mass. ρeff, dve and χ were calculated from the experimental results. The calculated values are summarized in Fig. 5. ESA was used to calculate χ in Abstract Introduction all cases, as χ and χ are not available. In the case of (NH ) SO , the measured val- f c 4 2 4 Conclusions References −3 −3 ues of ρeff (1.67∼1.75 g cm ) were slightly smaller than the bulk density (1.77 g cm ) (Fig. 5a), and χ was slightly larger than unity (1.01∼1.04) (Fig. 5b). These values Tables Figures 15 are similar to those obtained by Zelenyuk et al. (2006a), who showed that the χ of (NH4)2SO4 is 1.03±0.01 at 160 nm using a DMA and a single-particle laser ablation J I time-of-flight mass spectrometer (SPLAT). Biskos et al. (2006a) estimated a χ for 6– J I 60-nm (NH4)2SO4 particles of 1.02 to explain the discrepancy between theoretical cal- culations and experimental results of the hygroscopicity measurement. These results Back Close 20 indicate that (NH4)2SO4 particles do not have a completely spherical shape, as ob- served by electron microscope (Dick et al., 1998; Zelenyuk et al., 2006a). Comparing Full Screen / Esc the results of RUN1∼RUN4, systematic differences are observed. ρeff was the highest in RUN2 and lowest in RUN4. These differences are greater than the uncertainty of Printer-friendly Version the ρ measurement (1%). Zelenyuk et al. (2006b) reported that rapid drying causes eff Interactive Discussion 25 particles to have a more irregular shape. Thus, we suspect that these differences found 4663 are possibly caused by different conditions of the silica gel in the diffusion dryer in each run. Figure 5c shows the relationship between dme and dve of (NH4)2SO4 particles. ACPD As can be easily expected from the values of χ, the slope is almost equal to unity 9, 4653–4689, 2009 (0.99). Considering that the error in the diameter of PSL particles is typically about 3% 5 (Table 2), this result shows that (NH4)2SO4 particles can be treated approximately as spherical in most cases. Measurements of Figure 5d and e shows ρeff and χ of NaCl particles, respectively. ρeff particle masses of (1.75∼1.99 g cm−3) was smaller than the bulk density (2.16 g cm−3), and χ was sig- inorganic salt nificantly larger than unity (1.05∼1.14). Kelly and McMurry (1992) used a DMA and particles 10 an impactor to measure ρeff of NaCl particles (dme=111 nm). They reported that ρeff −3 M. Kuwata and Y. Kondo was equal to 1.86 g cm (χ=1.08). Zelenyuk et al. (2006a) measured ρeff of NaCl −3 (dme=160∼850 nm) using a DMA and a SPLAT. They showed that ρeff∼1.95 g cm (χ∼1.06) at 160 nm. Mikhaliov et al. (2004) estimated that χ is equal to 1.06 (99 nm) Title Page and 1.07 (201 nm) from hygroscopicity measurements. These values show that the 15 shape of NaCl particles is significantly different from spherical. Our results shown in Abstract Introduction Fig. 5 are similar to these other studies except for RUN4. In that case, χ was sys- Conclusions References tematically higher than the other cases (1.10∼1.14). This value is higher than the χ for a cubic shape in the continuous regime (1.08) (Hinds, 1999). Biskos et al. (2006b) Tables Figures showed that χ calculated by ASA for a cubic shape is needed to explain hygroscopic 20 growth of dme=6–60-nm NaCl particles. χ is about 1.2 for dme=50–100 nm when we J I employ ASA to calculate the χ of cubic particles. Thus, we regard the results of RUN4 as quite reasonable, considering that the shape of NaCl particles is cubic with rounded J I

edges (Zelenyuk et al., 2006a). Figure 5f shows the relationship between dme and Back Close dve of NaCl particles. dve is smaller than dme by 3–7%, and the value of the slope is 25 0.95. This shows that morphology should be considered when using NaCl particles for Full Screen / Esc calibration experiments. Printer-friendly Version

Interactive Discussion

4664 4.3 Calculation of S ACPD In this section, we estimate S inside the CCNC using experimental results shown in 9, 4653–4689, 2009 Sects. 4.1 and 4.2. In order to calculate volume equivalent critical dry diameter (dc ve), dc me and ρeff at dc me are required (Eq. 1). The dc me shown in Sect. 4.1 was used, 5 and ρeff at dc me was calculated by interpolating the corresponding experimental result Measurements of of the DMA-APM system measurement (RUN3 and RUN4 for ∆T 1 and ∆T 2, respec- particle masses of tively). The values of dc ve used for the calculation are summarized in Table 4. The inorganic salt calculation was performed using the at T 2 (Table 3). particles Table 5 shows the calculated results. As discussed in Sect. 2.2, we regard the model 10 of Archer (1992) as the most reliable. Using this model, S values were calculated to be M. Kuwata and Y. Kondo 0.117% and 0.220% for ∆T 1 and ∆T 2, respectively. Thus, we regard these values as the most probable values of S in the CCN chamber. In the case of NaCl particles at ∆T 1, the value calculated using the approach of Title Page

Tang (1996) was the lowest, and a higher S value was obtained with the approach of Abstract Introduction 15 Kreidenweis et al. (2005) and the ideal solution approximation. The values calculated using the Pitzer models (Pitzer and Mayorga, 1973; Archer et al., 1992) are the same. Conclusions References For (NH ) SO at ∆T 1, values similar to those of Archer (1992) were obtained when 4 2 4 Tables Figures we employed the Pitzer models (Pitzer and Mayorga, 1973; Clegg et al., 1996). This indicates the validity of the Pitzer model for the calculation of S. A similar value was J I 20 obtained based on the work of Young and Warren (1992). The ideal solution approxi-

mation for (NH4)2SO4 gave the lowest S. This indicates the inappropriateness of the J I use of this approximation for (NH4)2SO4. Parameterizations by Tang and Munkelwitz (1994) and Kreidenweis et al. (2005) estimated the highest values of S. These values Back Close

are significantly higher than those of Archer (1992). In the case of ∆T 2, the trend is Full Screen / Esc 25 similar to ∆T 1. For NaCl particles, aw given by Tang (1996) gave the lowest S, and the Pitzer models (Pitzer and Mayorga, 1973; Archer 1992) gave the highest S. In the case Printer-friendly Version of (NH4)2SO4, the ideal solution approximation gave the lowest values, and the Pitzer models (Pitzer and Mayorga, 1973; Clegg et al., 1996) and that of Young and Warren Interactive Discussion

4665 (1992) gave similar values. Application of the approach of Tang and Munkelwitz (1994) and Kreidenweis et al. (2005) gave the highest estimation of S. However, unlike the ACPD case of ∆T 1, a relatively large difference (0.005% in absolute terms) between Clegg 9, 4653–4689, 2009 et al. (1996) and Archer (1992) was observed at ∆T 2. So far, we have been unable to 5 determine what caused this difference. To summarize the above discussion, the Pitzer models (Pitzer and Mayorga, 1973; Measurements of Archer, 1992; Clegg, 1996) are valid to estimate critical S values within the uncer- particle masses of tainty of 2% (relative). The ideal solution approximation gives lower values of the crit- inorganic salt ical S, and the parameterizations by Tang and Munkelwitz (1994) and Kreidenweis et particles 10 al. (2005) yield higher values for (NH4)2SO4. These parameterization are based on M. Kuwata and Y. Kondo the data of hygroscopic growth up to RH=95%. The concentration of the (NH4)2SO4 −1 solution at this RH is about m=1.5 mol kg . Figure 6 shows the ϕ of (NH4)2SO4 given by Clegg et al. (1996). In the case of m<1 mol kg−1, ϕ decreases with an increase in Title Page m because of the Debye-Huckel¨ effect. However, ϕ increases with the increase in m −1 15 for m>2 mol kg due to short-range forces. This shows that the thermodynamic prop- Abstract Introduction −1 erties of (NH4)2SO4 solutions change at around 1.5 mol kg . Values of m at critical S −1 Conclusions References values of (NH4)2SO4 particles were calculated to be 0.01∼0.2 mol kg (S=0.1∼1%), and thus we need to take care in employing these parameterizations to calibrate a Tables Figures CCNC.

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20 5 Summary and conclusion J I

Back Close In this study, we measured CCN/CN ratios and mp of size-selected (NH4)2SO4 and NaCl particles. CCN/CN ratios were measured using a CCNC and a CPC, and m was p Full Screen / Esc measured using an APM and a CPC. The CCNC was operated under two conditions (∆T 1 and ∆T 2). The dc me values of (NH4)2SO4 were 115.2 nm (∆T 1) and 75.3 nm Printer-friendly Version 25 (∆T 2). In the case of NaCl, these values were 94.7 nm (∆T 1) and 63.2 nm (∆T 2). dve calculated from mp and ρm were smaller than dme by about 1 and 5% for (NH4)2SO4 Interactive Discussion and NaCl, respectively. Thus, it is a good approximation to treat (NH4)2SO4 particles 4666 as spherical particles. dc ve values were estimated from dc me and measured ρeff and they were used as ACPD input parameters for Kohler¨ theory calculations. Then, S values inside the CCNC were 9, 4653–4689, 2009 estimated using several thermodynamics models. In these calculations, we regarded 5 that the Pitzer model for NaCl (Archer, 1992) was the most reliable, as it was in ex- cellent agreement with the experimental data, including the concentration range that is Measurements of important for CCN activation. The values obtained for (NH4)2SO4 and NaCl agreed to particle masses of within a difference of 2% (relative) when the Pitzer model was employed for the calcu- inorganic salt lation. This result indicates that application of the Pitzer model for calibrating a CCNC particles 10 gives the most probable values of S. M. Kuwata and Y. Kondo

Appendix A Title Page List of parameters Abstract Introduction

ai coefficients in the polynomial equation for water density given by Kell Conclusions References 15 (1975) Tables Figures aw water activity

Aϕ Debye-Huckel¨ constant for the osmotic coefficient J I

CC Cunningham slip correction factor J I Back Close Ci coefficients in the polynomial equation for water activity given by Tang 20 and Munkelwitz (1994) and Tang (1996) Full Screen / Esc ϕ (0) (1) CMX , CMX , CMX parameters for the Pitzer equation Printer-friendly Version dc critical dry diameter for CCN activation Interactive Discussion

4667 dc me, dc ve critical dry diameter (mobility equivalent diameter and volume equiv- alent diameter, respectively) ACPD

dme mobility equivalent diameter 9, 4653–4689, 2009

dve volume equivalent diameter Measurements of 5 Dp droplet diameter particle masses of inorganic salt dp particle diameter particles e elementary charge M. Kuwata and Y. Kondo I ion strength i van’t Hoff factor Title Page

10 m molality of solution Abstract Introduction m mass of particle p Conclusions References m mass of water w Tables Figures

ms mass of solute J I Mw molecular weight of water J I 15 Ms molecular weight of solute Back Close n particle charge Full Screen / Esc nw number of moles of water

Printer-friendly Version ns number of moles of solute

0 Interactive Discussion pw saturation vapor pressure of water 4668 pw equilibrium water vapor pressure of aqueous solution having a flat surface ACPD

pw aerosol equilibrium water vapor pressure of aerosol particle 9, 4653–4689, 2009 R gas constant Measurements of 5 r, r1, r2 center, inner, and outer radii of the operating space of the APM particle masses of s saturation ratio of water vapor inorganic salt particles S supersaturation of water vapor M. Kuwata and Y. Kondo T temperature (K) ∆T temperature gradient of CCNC Title Page

10 V voltage applied to APM AP M Abstract Introduction x concentration of solution in weight percent (%) Conclusions References Z electrical mobility p Tables Figures

zm, zx charges of ions m and x J I α a constant in the Pitzer equation J I 15 α2 a constant in the revised Pitzer equation given by Archer (1991) Back Close (0) (1) βMX , βMX parameters in the Pitzer equation Full Screen / Esc λ mean free path of air σ surface tension Printer-friendly Version Interactive Discussion ρeff effective density 4669 ρm density of the material in the particle ACPD ρw density of water 9, 4653–4689, 2009 υ υm+υx

υm, υx stoichiometric number of ions m and x Measurements of particle masses of 5 ϕ molal osmotic coefficient inorganic salt ω rotation speed of APM particles

χ dynamic shape factor M. Kuwata and Y. Kondo

χc, χt, χf dynamic shape factor of continuum, transition, and free molecular regimes Title Page

Abstract Introduction 10 Appendix B Conclusions References Thermodynamics models for aw of inorganic salt Tables Figures

In this section, we review the thermodynamics models of (NH4)2SO4 and NaCl em- ployed in this study to estimate S in the CCNC. J I

J I 15 Ideal solution approximation Back Close The simplest model is the ideal solution approximation (ϕ=1). Although it may be too simple (e.g., Young and Warren, 1992), this approximation has been used to calibrate Full Screen / Esc CCNCs in many studies (e.g., Raymond and Pandis, 2002; Roberts and Nenes, 2005). The manufacture of CCNC also relies on this model (Shilling et al., 2007). Thus, it is Printer-friendly Version 20 important to compare this model with more sophisticated models. Interactive Discussion

4670 Pitzer model ACPD Pitzer developed a semi-empirical model to calculate ϕ (Pitzer, 1973). Using the orig- inal Pitzer model, ϕ of a single electrolyte can be calculated by the following equation 9, 4653–4689, 2009 (refer Appendix A for the notation of parameters): √ Measurements of I 2υmυx  (0) (1) p  5 ϕ = 1 − |z z |A √ + m β + β exp(−α I) m x ϕ υ MX MX particle masses of 1 + 1.2 I inorganic salt 3/2 2(υ υ ) ϕ particles +m2 m x C . (B1) υ MX M. Kuwata and Y. Kondo The first two terms are derived from Debye-Huckel¨ theory, and the third and fourth terms express short-range interactions (e.g., ion-molecular interactions). Aϕ can be calculated as a function of temperature using the polynomial equation given by Clegg et Title Page 10 al. (1994), which is based on the study of Archer and Wang (1990). Pitzer and Mayorga (0) (1) ϕ Abstract Introduction (1973) determined three parameters (βMX , βMX and CMX ) for NaCl and (NH4)2SO4 us- ing experimental data reviewed by Electrolyte Solutions (Robinson and Stokes, 2002). Conclusions References The model has been used for the calibration of CCNCs (e.g., Mochida et al., 2006) and compared with other models by Rose et al. (2008). Tables Figures 15 Archer (1991) modified Eq. (B1) as follows: √ J I I 2υmυx  (0) (1) p  ϕ = 1 − |zmzx|Aϕ √ + m βMX + βMX exp(−α I) 1 + 1.2 I υ J I 2 4υ υ  (0) (1) p  Back Close + m2 m x C + C exp(−α I) . (B2) υ MX MX 2 Full Screen / Esc Archer (1992) gave the parameters of the above equation for NaCl as a function of temperature and pressure. Experimental data used by Archer (1992) cover the con- Printer-friendly Version 20 centration range that is important for the calculation of critical S (on the order of −1 −2 10 ∼10 m). Thus, we regard this model as giving the most reliable value (Clegg, Interactive Discussion 2007). Note that the correction given by Clegg et al. (1994) should be employed for the 4671 use of the work of Archer (1992). Clegg et al. (1996) obtained parameters for Eq. (B2) for (NH4)2SO4, and their results have been used in some CCN studies (e.g., Kumar et ACPD al., 2003), and it has been compared extensively with other models by Kreidenweis et 9, 4653–4689, 2009 al. (2005).

5 van’t Hoff factor Measurements of particle masses of Another method to express the non-ideal behavior of inorganic electrolyte solutions is inorganic salt the use of i. One of the most widely-used expressions for i was derived by Young and particles Warren (1992): i = 1.9242 − 0.1844 ln(m) − 0.007931(ln(m))2 (B3) M. Kuwata and Y. Kondo

10 This equation is applicable only to (NH4)2SO4. The value from this model has been used in some studies (e.g., Svenningsson et al., 2006; Frank et al., 2007) and com- Title Page pared with other models by Rose et al. (2008). Abstract Introduction Polynomial equation Conclusions References

Tang and Munkelwitz (1994) and Tang (1996) measured hygroscopic growth of Tables Figures 15 (NH4)2SO4 and NaCl using the electrodynamic balance (EDB) technique. They sum- marized the experimental results with the following polynomial function: J I X i aw = 1.0 + Ci x (B4) J I where Ci are constants, and x is the concentration of the solution in wt.%. This model Back Close has also been used to calibrate a CCNC (e.g., Snider et al., 2006) and compared with 20 other models by Kreidenweis et al. (2005) and Rose et al. (2008). Full Screen / Esc Kreidenweis et al. (2005) fitted the growth factors (GFs) of (NH4)2SO4 and NaCl particles measured by a hygroscopic tandem DMA with the following equation: Printer-friendly Version  1/3 dme wet  2  aw Interactive Discussion GF = = 1 + a + baw + caw (B5) dme dry 1 − aw 4672 where a, b, and c are constants, and dme wet and dme dry denote the wet and dry particle diameters, respectively. This model has also been used for some CCN studies ACPD (e.g., Mochida et al., 2006; Rose et al., 2008). 9, 4653–4689, 2009

Appendix C Measurements of 5 particle masses of ρ σ w and inorganic salt particles Here we summarize values of ρw and σ employed for the calculation of critical S. ρw depends both on temperature (Kell, 1975) and the concentration of solute (Tang and M. Kuwata and Y. Kondo Munkelwitz, 1994; Tang, 1996). However, the density of the solution is available only ◦ 10 at 25 C, and the influence of the solute on the density of solution near the critical Dp is estimated to be small. Thus, we employed the temperature-dependent water density Title Page given by Kell (1975), which is written as follows: Abstract Introduction 5 P i ai T Conclusions References i=0 ρw = (C1) Tables Figures 1 + a−1T

where ai are constants. J I 15 σ also depends on temperature and chemical composition (Seinfeld and Pandis,

2006). We employed the following set of equations to calculate σ: J I −3 σ = σ (T ) + 2.17 × 10 m (C2) Back Close (NH4)2SO4 water (NH4)2SO4 −3 σNaCl = σ water(T ) + 1.62 × 10 mNaCl (C3) Full Screen / Esc where Printer-friendly Version  1.256    −3 Tc − T Tc − T 20 σ water = 235.8 × 10 1 − 0.625 (Tc = 647.15 K) (C4) Interactive Discussion Tc Tc 4673 Equations (C2) and (C3) are taken from Seinfeld and Pandis (2006) and Eq. (C4) was given by Vargaftik et al. (1983). ACPD Acknowledgement. This work was supported by the Ministry of Education, Culture, Sports, 9, 4653–4689, 2009 Science, and Technology (MEXT), the global environment research fund of the Japanese Min- 5 istry of the Environment (B-083). M. Kuwata thanks to the Japan Society for the Promotion of Science (JSPS) for a JSPS Research Fellowship for Young Scientists. Measurements of particle masses of inorganic salt References particles

Allen, M. D. and Raabe, O. G.: Slip correction measurements of spherical solid aerosol particles M. Kuwata and Y. Kondo in an improved Millikan apparatus, Aerosol. Sci. Technol., 4, 269–286, 1985. 10 Archer, D. G. and Wang, P.: The dielectric constant of water and Debye-Huckel¨ limiting law slopes, J. Phys. Chem. Ref. Data., 19, 371–411, 1990. Title Page Archer, D. G.: Thermodynamic properties of the NaBr+H2O system, J. Phys. Chem. Ref. Data., 20, 509–535, 1991. Abstract Introduction Archer, D. G.: Thermodynamic properties of the NaCl+H2O system II. Thermodynamic prop- 15 erties of NaCl(aq), NaCl·2H2O(cr), and phase equilibria, J. Phys. Chem. Ref. Data., 21, Conclusions References 793–821, 1992. Biskos, G., Paulsen, D., Russel, L. M., Buseck, P. R., and Martin, S. T.: Prompt deliquescence Tables Figures and efflorescence of aerosol nanoparticles, Atmos. Chem. Phys., 6, 4633–4642, 2006a, http://www.atmos-chem-phys.net/6/4633/2006/. J I 20 Biskos, G., Russel, L. M., Buseck, P. R., and Martin, S. T.: Nanosize effect on the hygroscopic growth factor of aerosol particles, Geophys. Res. Lett., 33, L07801, J I doi:10.1029/2005GL025199, 2006b. −1 Clegg, S. L., Rard, J. A., and Pitzer, K. S.: Thermodynamic properties of 0–6 mol kg aqueous Back Close sulfuric acid from 273.15 to 328.15 K, J. Chem. Soc. – Faraday Trans., 90(13), 1875–1894, 25 1994. Full Screen / Esc Clegg, S. L., Milioto, S., and Palmer, D. A.: Osmotic and activity coefficients of aque- ous (NH4)2SO4 as a function of temperature, and aqueous (NH4)2SO4-H2SO4 mixtures at Printer-friendly Version 298.15 K and 323.15 K, J. Chem. Eng. Data, 41, 455–467, 1996. Clegg, S. L.: Interactive comment on “Calibration and measurement uncertainties of Interactive Discussion 30 a continuous-flow cloud condensation nuclei counter (DMT-CCNC): CCN activation of am- 4674 monium sulfate and sodium chloride aerosol particles in theory and experiments” by D. Rose et al., Atmos. Chem. Phys. Discuss., 7, S4180–S4183, 2007. ACPD Dahneke, B. E.: Slip correction factors for nonspherical bodies-III the form of the general law, J. Aerosol. Sci., 4, 163–170, 1973. 9, 4653–4689, 2009 5 DeCarlo, P. F., Slowik, J. G., Worsnop, D. R., Davidovits, P., and Jimenez, J. L.: Particle mor- phology and density characterization by combining mobility and aerodynamic diameter mea- surements. Part 1: Theory, Aerosol. Sci. Technol., 38, 1185–1205, 2004. Measurements of Dick, W. D., Ziemann, P. J., Huang, P.-F., and McMurry, P. H.: Optical shape fraction mea- particle masses of surements of submicrometre laboratory and atmospheric aerosols, Meas. Sci. Technol., 9, inorganic salt 10 183–196, 1998. particles Ehara, K., Hagwood, C., and Coakley, K. J.: Novel method to classify aerosol particles ac- cording to their mass-to-charge ratio-aerosol particle mass analyzer, J. Aerosol. Sci., 27(2), M. Kuwata and Y. Kondo 217–234, 1996. Frank, G. P., Dusek, U., and Andreae, M. O.: Technical Note: Characterization of a static 15 thermal-gradient CCN counter, Atmos. Chem. Phys., 7, 3071–3080, 2007, Title Page http://www.atmos-chem-phys.net/7/3071/2007/. Hinds, W. C.: Aerosol Technology, John Wiley and Sons, Inc., 1999. Abstract Introduction Kasper, G.: Dynamics and measurements of Smokes. I size characterization of nonspherical particles, Aerosol. Sci. Technol., 1, 187–199, 1982. Conclusions References 20 Kell, G. S.: Precise representation of volume properties of water at one atmosphere, J. Chem. Eng. Data, 12(1), 66–69, 1967. Tables Figures Kelly, W. P. and McMurry, P. H.: Measurements of particle density by inertial classification of differential mobility analyzer-generated monodisperse aerosols, Aerosol. Sci. Technol., 17, J I 199–212, 1992. 25 Kreidenweis, S. M., Koehler, K., DeMott, P. J., Prenni, A. J., Carrico, C., and Ervens, B.: Water J I activity and activation diameters from hygroscopicity data – Part 1: Theory and application to inorganic salts, Atmos. Chem. Phys., 5, 1357–1370, 2005, Back Close http://www.atmos-chem-phys.net/5/1357/2005/. Full Screen / Esc Pradeep Kumar, P., Broekhuizen, K., and Abbatt, J. P. D.: Organic acids as cloud condensation 30 nuclei: Laboratory studies of highly soluble and insoluble species, Atmos. Chem. Phys., 3, 509–520, 2003, Printer-friendly Version http://www.atmos-chem-phys.net/3/509/2003/. Lohmann, U. and Feichter, J.: Global indirect aerosol effects: a review, Atmos. Chem. Phys., 5, Interactive Discussion 4675 715–737, 2005, http://www.atmos-chem-phys.net/5/715/2005/. ACPD McMurry, P. H.: A review of atmospheric aerosol measurements, Atmos. Environ., 34, 1959– 1999, 2000. 9, 4653–4689, 2009 5 Mikhailov, E., Vlasenko, S., Niessner R., and Poschl,¨ U.: Interaction of aerosol particles com- posed of protein and salts with water vapor: hygroscopic growth and microstructural rear- rangement, Atmos. Chem. Phys., 4, 323–350, 2004, Measurements of http://www.atmos-chem-phys.net/4/323/2004/. particle masses of Mochida, M., Kuwata, M., Miyakawa, T., Takegawa, N., Kawamura, K., and Kondo, Y.: Rela- inorganic salt 10 tionship between hygroscopicity and cloud condensation nuclei activity for urban aerosols in particles Tokyo, J. Geophys. Res., 111, D23204, doi:10.1029/2005JD006980, 2006. Nenes, A., Chuang, P. Y., Flagan, R. C., and Seinfeld, J. H.: A theoretical analysis of cloud M. Kuwata and Y. Kondo condensation nucleus (CCN) instruments, J. Geophys. Res., 106(D4), 3449–3474, 2001. Otto, P., Georgii, H.-W., and Bingemer H.: A new three-stage continuous flow CCN-counter, 15 Atmos. Res., 61, 299–310, 2002. Title Page Park, K., Kittelson, D. B., and McMurry, P. H.: Structural properties of diesel exhaust particles measured by transmission electron microscope (TEM): relationships to particle mass and Abstract Introduction mobility, Aerosol. Sci. Technol., 38, 881–889, 2004. Pitzer, K. S.: Thermodynamics of electrolytes. I. Theoretical basis and general equations, J. Conclusions References 20 Phys. Chem., 77(2), 268–277, 1973. Pitzer, K. S. and Mayorga, G.: Thermodynamics of electrolytes. II. Activity and osmotic co- Tables Figures efficients for strong electrolytes with one or both ions univalent, J. Phys. Chem., 77(19), 2300–2308, 1973. J I Pruppacher, H. R. and Klett, J. D.: Microphysics of Clouds and Precipitation, Kluwer Academic 25 Publishers, 1997. J I Raymond, T. M. and Pandis, S. N.: Cloud activation of single-component organic aerosol parti- cles, J. Geophys. Res., 107(D24), 4787, doi:10.1029/2002JD002159, 2002. Back Close Rissman, T. A., Varutbangkul, V., Surratt, J. D., Topping, D. O., McFiggans, G., Flagan, R. C., Full Screen / Esc and Seinfeld, J. H.: Cloud condensation nucleus (CCN) behavior of organic aerosol particles 30 generated by atomization of water and methanol solutions, Atmos. Chem. Phys., 7, 2949– 2971, 2007, Printer-friendly Version http://www.atmos-chem-phys.net/7/2949/2007/. Roberts, G. C. and Nenes, A.: A continuous-flow streamwise thermal-gradient CCN chamber Interactive Discussion 4676 for atmospheric measurements, Aerosol. Sci. Technol., 39, 206–221, 2005. Robinson, R. A. and Stokes, R. H.: Electrolyte Solutions, second revised edition, Dover Publi- ACPD cations, Inc., 2002. Rose, D., Gunthe, S. S., Mikhailov, E., Frank, G. P., Dusek, U., Andreae, M. O., and Poschl,¨ U.: 9, 4653–4689, 2009 5 Calibration and measurement uncertainties of a continuous-flow cloud condensation nuclei counter (DMT-CCNC): CCN activation of ammonium sulfate and sodium chloride aerosol particles in theory and experiment, Atmos. Chem. Phys., 8, 1153–1179, 2008, Measurements of http://www.atmos-chem-phys.net/8/1153/2008/. particle masses of Seinfeld, J. H. and Pandis, S. N.: Atmospheric Chemistry and Physics, John Wiley and Sons, inorganic salt 10 Inc., New York, 2006. particles Shilling, J. E., King, M. E., Mochida, M., Worsnop, D. R., and Martin, S. T.: Mass spectral evi- dence that small changes in composition caused by oxidative aging processes alter aerosol M. Kuwata and Y. Kondo CCN properties, J. Phys. Chem. A., 111, 3358–3368, 2007. Snider, J. R., Petters, M. D., Wechsler, P., and Liu, P. S.: Supersaturation in the Wyoming CCN 15 instrument, J. Atmos. Ocean. Technol., 23, 1323–1339, 2006. Title Page Stratmann, F., Kiselev, A., Wendisch, M., Heintzenberg, J., Charlson, R. J., Diehl, K., Wex, H., and Schmidt, S.: Laboratory studies and numerical simulations of cloud droplet formation Abstract Introduction under realistic supersaturation conditions, J. Atmos. Ocean. Technol., 21, 876–887, 2004. Svenningsson, B., Rissler, J., Swietlicki, E., Mircea, M., Blide, M., Facchini, M. C., Deccesari, S., Conclusions References 20 Fuzzi, S., Zhou, J., Mønster, J., and Rosenørn, T.: Hygroscopic growth and critical super- saturations for mixed aerosol particles of inorganic and organic compounds of atmospheric Tables Figures relevance, Atmos. Chem. Phys., 6, 1937–1952, 2006, http://www.atmos-chem-phys.net/6/1937/2006/. J I Tang, I. N. and Munkelwitz, H. R.: Water activities, densities, and refractive indices, of aqueous 25 sulfates and sodium nitrate droplets of atmospheric importance, J. Geophys. Res., 99(D9), J I 18801–18808, 1994. Tang, I. N.: Chemical and size effects of hygroscopic aerosols on light scattering coefficients, J. Back Close Geophys. Res., 101(D14), 19245–19250, 1996. Full Screen / Esc Twomey, S.: Pollution and the planetary albedo, Atmos. Environ., 8, 1251–1256, 1974. 30 VanReken, T. M., Ng, N. L., Flagan, R. C., and Seinfeld, J. H.: Cloud condensation nuclei activation properties of biogenic secondary organic aerosol, J. Geophys. Res., 110, D07206, Printer-friendly Version doi:10.1029/2004JD005465, 2005. Vargaftik, N. B., Volkov, B. N., and Voljak, L. D.: International tables of the surface tension of Interactive Discussion 4677 water, J. Chem. Engi. Data., 12(3), 817–820, 1983. Young, K. C. and Warren, A. J.: A reexamination of the derivation of the equilibrium supersatu- ACPD ration curve for soluble particles, J. Atmos. Sci., 49(13), 1138–1143, 1992. Zelenyuk, A., Cai, Y., and Imre, D.: From agglomerates of spheres to irregularly shaped par- 9, 4653–4689, 2009 5 ticles: determination of dynamic shape factors from measurements of mobility and vacuum aerodynamic diameter, Aerosol. Sci. Technol., 40, 190–217, 2006a. Zelenyuk, A., Imre, D., and Cuadra-Rodriguez, A. L.: Evaporation of water from particles in the Measurements of aerodynamic lens inlet: an experimental study, Anal. Chem., 78, 6942–6947, 2006b. particle masses of inorganic salt particles

M. Kuwata and Y. Kondo

Title Page

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4678 ACPD 9, 4653–4689, 2009

Measurements of particle masses of inorganic salt particles

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Table 1. Ms, ρm, and ν of (NH4)2SO4 and NaCl. Title Page

Ms ρm ν Abstract Introduction (NH ) SO 132.14 1.77 (g cm−3) 3 4 2 4 Conclusions References NaCl 58.44 2.16 2 Tables Figures

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Measurements of particle masses of inorganic salt particles

M. Kuwata and Y. Kondo Table 2. List of PSL particles used for the calibration of the DMA and APM.

d ρa b p m Mass range Manufacturer (product name) Title Page 48±1 (nm) 1.061 (g cm−3) 0.058–0.065 (fg) JSR corporation (STADEX SC-0050-D) 61±1 1.065 0.12–0.13 JSR corporation (STADEX SC-0060-D) Abstract Introduction 76±2 1.057 0.22–0.26 JSR corporation (STADEX SC-0075-D) 102±3 1.05 0.53–0.64 Duke Scientific Corporation (NANOSPHERE SIZE STANDARDS) Conclusions References 152±5 1.05 1.7–2.1 Duke Scientific Corporation (NANOSPHERE SIZE STANDARDS)

Tables Figures a Density given by the manufacturers as a reference. b Particle mass was calculated using the diameter range and density. J I

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Table 3. Temperatures of the thermal gradient chamber in the CCNC. T 1, T 2, and T 3 corre- spond to the temperatures at the top, middle, and the bottom of the chamber, respectively. Title Page

T inlet T 1 T 2 T 3 Abstract Introduction

∆T 1 301.3±0.1 (K) 300.48±0.02 301.86±0.02 303.16±0.02 Conclusions References ∆T 2 301.9±0.1 301.10±0.02 303.18±0.02 305.08±0.02 Tables Figures

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Table 4. Values of dc ve used for the calculation of S. Title Page

∆T 1 ∆T 2 Abstract Introduction (NH4)2SO4 NaCl (NH4)2SO4 NaCl Conclusions References dc ve (nm) 113.9 90.3 74.0 59.2 Tables Figures

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4682 ACPD 9, 4653–4689, 2009

Measurements of particle masses of inorganic salt Table 5. S values calculated using several thermodynamics models. See text for the input particles parameters and descriptions of the models. “N/A” denotes that the thermodynamic data is not available. M. Kuwata and Y. Kondo

∆T 1 ∆T 2 Title Page Model (NH4)2SO4 NaCl (NH4)2SO4 NaCl Ideal solution approximation 0.110 (%) 0.115 0.207 0.214 Abstract Introduction Archer (1992) N/A 0.117 N/A 0.220 Clegg et al. (1996) 0.117 N/A 0.225 N/A Conclusions References Pitzer and Mayorga (1973) 0.117 0.117 0.225 0.220 Young and Warren (1992) 0.118 N/A 0.228 N/A Tables Figures Tang and Munkelwitz (1994) 0.135 N/A 0.256 N/A Tang (1996) N/A 0.113 N/A 0.211 J I Kreidenweis et al. (2005) 0.139 0.115 0.262 0.215 J I

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Measurements of particle masses of inorganic salt m measurement particles p M. Kuwata and Y. Kondo APM CPC to exhaust Compressed air 0.3 lpm Atomizer Diffusion dryer 241Am DMA Title Page

Abstract Introduction CCNC Room air 0.5 lpm Compressor PAG HEPA filter MFC Conclusions References CPC ※ PAG: pure air generator Tables Figures

MFC: mass flow controller CCN measurement : valve J I

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4684 ACPD 9, 4653–4689, 2009

Measurements of PSL = 102 ± 3 nm particle masses of 0.15 DMA (set) = 103.5 nm inorganic salt particles

M. Kuwata and Y. Kondo 0.10

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(a) ACPD (NH4)2SO4

1.0 9, 4653–4689, 2009 ΔT1 ΔT2 Measurements of particle masses of 0.5 CCN/CN inorganic salt particles

M. Kuwata and Y. Kondo 0.0 60 80 100 120 140 d (nm) (b) me Title Page

NaCl Abstract Introduction 1.0 ΔT1 ΔT2 Conclusions References

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Fig. 3. CCN activation curves of (NH ) SO and NaCl particles under two experimental condi- 4 2 4 Printer-friendly Version tions (∆T 1 and ∆ T 2). Interactive Discussion Figure 3 4686 ACPD 9, 4653–4689, 2009

Measurements of -3 25x10 particle masses of NaCl (DMA = 70 nm) inorganic salt

particles 20 M. Kuwata and Y. Kondo 15

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0.1 0.2 0.3 0.4 0.5 J I mp (fg) J I

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(a) (d) 1.80 (NH ) SO 2.2 NaCl ACPD 4 2 4 1.75 ) ) -3 -3 2.0 9, 4653–4689, 2009 1.70 (g cm cm (g cm (g eff eff

ρ ρ 1.8 1.65 RUN1 RUN3 RUN1 RUN3 RUN2 RUN4 bulk density RUN2 RUN4 bulk density 1.60 1.6 Measurements of 60 80 100 120 140 60 80 100 120 140 d (nm) d (nm) particle masses of me me inorganic salt (b) (e) 1.20 particles (NH4)2SO4 RUN1 RUN3 NaCl RUN2 RUN4 1.04 1.15 M. Kuwata and Y. Kondo χ χ 1.10 1.02 1.05 RUN1 RUN3 1.00 RUN2 RUN4 1.00 60 80 100 120 140 60 80 100 120 140 Title Page dme (nm) dme (nm) (c) (f) Abstract Introduction NaCl (NH4)2SO4 140 140 d = 0.95 d dve = 0.99 dme ve me Conclusions References 120 120 Tables Figures

100 100 (nm) (nm) ve ve d

d 80 80 J I RUN1 RUN1 RUN2 60 RUN2 60 RUN3 RUN3 RUN4 RUN4 J I

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Full Screen / Esc Fig. 5. ρeff, χ, and dve of (NH4)2SO4 and NaCl particles measured using the DMA-APM system. (a) ρeff of (NH4)2SO 4, (b) χ of (NH4)2SO4, (c) dve of (NH4)2SO4, (d) ρeff of NaCl, (e) χ of NaCl, and (f) dve of NaClFigure particles. 5 Printer-friendly Version

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Measurements of 1.0 0.6 m at critical S m at RH = 95% particle masses of inorganic salt short-range forces particles 0.8 0.4 M. Kuwata and Y. Kondo

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Debye-Hückel , φ Abstract Introduction φ Debye-Hückel short-range forces Conclusions References

0.4 0.0 Tables Figures

0.001 0.01 0.1 1 -1 J I m (mol Kg )

J I Fig. 6.Figureϕ and 6 related parameters for an aqueous solution of (NH4)2SO4 calculated based on the work of Clegg et al. (1996). “Debye-Huckel¨ term” is the first two terms in Eq. (B2), and Back Close

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