Water Content and Phase Transitions in Particles of Inorganic and Organic Species and their Mixtures Using Micro-Raman Spectroscopy

Size: px
Start display at page:

Download "Water Content and Phase Transitions in Particles of Inorganic and Organic Species and their Mixtures Using Micro-Raman Spectroscopy"

Transcription

1 Aerosol Science and Technology ISSN: (Print) (Online) Journal homepage: Water Content and Phase Transitions in Particles of Inorganic and Organic Species and their Mixtures Using Micro-Raman Spectroscopy Ming Chee Yeung & Chak K. Chan To cite this article: Ming Chee Yeung & Chak K. Chan (2010) Water Content and Phase Transitions in Particles of Inorganic and Organic Species and their Mixtures Using Micro-Raman Spectroscopy, Aerosol Science and Technology, 44:4, , DOI: / To link to this article: Published online: 17 Feb Submit your article to this journal Article views: 607 View related articles Citing articles: 21 View citing articles Full Terms & Conditions of access and use can be found at

2 Aerosol Science and Technology, 44: , 2010 Copyright American Association for Aerosol Research ISSN: print / online DOI: / Water Content and Phase Transitions in Particles of Inorganic and Organic Species and their Mixtures Using Micro-Raman Spectroscopy Ming Chee Yeung 1 and Chak K. Chan 1,2 1 Department of Chemical and Biomolecular Engineering, Hong Kong University of Science and Technology, Clear Water Bay, Kowloon, Hong Kong, China 2 Division of Environment, Hong Kong University of Science and Technology, Clear Water Bay, Kowloon, Hong Kong, China Hygroscopicity and phase transitions were measured with deposited particles of ammonium sulfate (AS), ammonium nitrate (AN), malonic acid (MA), glutaric acid (GA), glyoxylic acid (GlyA), as well as two mixed particle systems AS-MA and AS-GA using micro-raman spectroscopy. Hygroscopicity was presented in terms of water-to-solute mass ratios, which were obtained from the integrated area ratios of the Raman water band to a distinct solute peak. Deliquescence and crystallization were confirmed by abrupt changes in the Raman peak positions and the full-widthhalf-heights of distinct solute peaks. The results for AS, AN, MA, and GA agreed well with literature reports and model predictions. For GlyA, we detected the Raman water band at near 0% RH, indicating that the spectral technique is sensitive for hygroscopic measurements at very low RH. Additional spectral feature at 0% RH was also observed. In the case of more complicated ASdicarboxylic acid mixed systems, the partial phase transitions of the organic components were identified using the intensity ratios of aqueous to solid C=O peaks. AS-MA particles did not completely crystallize and gradual water uptake with increasing RH from 3% was observed. Moreover, it was found that AS-GA particles showed step-wise crystallization in which the AS fraction crystallized prior to the GA fraction. The measured water content and complete DRH of both mixed systems were consistent with the published values. The results show the utility of micro-raman spectroscopic analysis in studying hygroscopicity and phase characterizations of the chemical species in mixed particles. 1. INTRODUCTION The role of atmospheric particles in global climate change has been recognized due to their effects on radiative forcing Received 9 July 2009; accepted 5 December This work was funded by Earmarked Grant from the Hong Kong s Research Grants Council and HKUST internal grant HKUST 1/CRF-SF/08. Address correspondence to Chak K. Chan, Division of Environment and Department of Chemical and Biomolecular Engineering, Hong Kong University of Science and Technology, Clear Water Bay, Kowloon, Hong Kong, China. keckchan@ust.hk (Charlson et al. 1992; Haywood and Boucher 2000; Penner et al. 2001; Kaufman et al. 2002; Forster et al. 2007). The forcing mechanisms always depend on the physical properties of the particles, such as their hygroscopic properties and phase states. As humidity cycles, hygroscopic particles can interact with water vapor and change in size, concentration and even chemical composition, all of which can influence light absorption and scattering (Horvath 1993; Nemesure et al. 1995; Pilinis et al. 1995), cloud condensation nuclei (CCN) activity (Svenningsson et al. 1997; Kreidenweis et al. 2005) as well as chemical reactivity (Herrmann 2003; Seinfeld and Pandis 2006). The transitions between the solid and aqueous phases at certain points (or in certain ranges) of relative humidity (RH) are described by the deliquescence relative humidity (DRH) where dry particles absorb water and dissolve and the crystallization relative humidity (CRH) at which solution droplets crystallize. Such transitions are important in determining optical properties, CCN activity, and chemical reactivity (Martin 2000). In depth investigation of the phase behaviors and hygroscopicity of atmospheric aerosols is therefore necessary to elucidate their impacts on global climate and tropospheric chemistry. Various techniques have been applied to studying the hygroscopicity and phase transitions of levitated particles. The electrodynamic balance (EDB) (Richardson and Spann 1984; Cohen et al. 1987; Tang et al. 1995) and humidified tandem differential mobility analyzer (HTDMA) (McMurry and Stolzenburg 1989; Svenningsson et al. 1997; Chan and Chan 2005; Swietlicki et al. 2008) have been widely used to study the hygroscopic growth of suspended particles. However, these techniques give no direct information of the phase state of the particles components. In-situ spectroscopic analysis is well known to be useful for phase characterization of chemical species. An aerosol flow tube coupled with a Fourier transform infrared (FTIR) spectrometer has been used to study phase transitions of suspended particles (Cziczo et al. 1997; Onasch et al. 1999). In addition, a combined EDB/Raman spectrometer (Fung and Tang 1988) has been demonstrated to provide solid spectral evidence of the phase 269

3 270 M. C. YEUNG AND C. K. CHAN state of a particle simultaneously with hygroscopicity measurements (Zhang and Chan 2002; Jordanov and Zellner 2006; Lee et al. 2008; Ling and Chan 2008). More recently, micro-raman spectroscopic systems have been employed to investigate the molecular interactions in supersaturated droplets of different inorganic species (Wang et al. 2005; Li et al. 2006; Dong et al. 2007) and the polymorphic transformation of NH 4 NO 3 particles deposited on a hydrophobic substrate (Wu and Chan 2008). Such micro-raman systems have also been used to study hygroscopicity and phase transitions of Ca(NO 3 ) 2 and Ca(NO 3 ) 2 /CaCO 3 (Liu et al. 2008a), and ammonium sulfate adipic acid mixtures (Yeung et al. 2009). Moreover, spatial spectroscopic imagining has proved useful for the phase and chemical characterization of heterogeneous particles (Liu et al. 2008a; Yeung et al. 2009). A similar technique that utilizes micro-ftir to study the hygroscopic behavior of pure inorganic and sea-salt particles has also been reported (Liu et al. 2008b). Compared to EDB and TDMA, systems for the microscopic spectral analysis of deposited particles are rather simple, making this a potentially useful approach for studying the phase transitions and hygroscopic properties of atmospheric aerosols. Organic components are the major constituent of atmospheric aerosols (Novakov and Penner 1993; Rogge et al. 1993; Saxena and Hildemann 1996) but they are often mixed with inorganic species (Saxena et al. 1995; Zappoli et al. 1999). Micro-Raman spectroscopic systems have previously been applied to investigate hygroscopicity and phase transitions of inorganic droplets, but they have not previously been used for studying organic or mixed inorganic organic droplets. To evaluate the capability of the micro-raman technique for studying particles involving inorganic and organic mixtures, we examined the phase and hygroscopic properties of droplets of pure ammonium sulfate (AS) and ammonium nitrate (AN), the pure organics malonic acid (MA), glutaric acid (GA), and glyoxylic acid (GlyA), and two inorganic organic mixtures AS-MA and AS-GA. Changes in peak area, peak position and full-width-athalf-height (fwhh) were quantified to determine hygroscopicity in terms of water-to-solute ratios, the phase states of the pure and mixed particles, and the transition relative humidities. The results for pure particles of the inorganic salts and dicarboxylic acids agreed well with literature reports and model predictions. Furthermore, organic compounds are known to frequently exhibit non-deliquescent behaviours upon evaporation of water. By size and mass measurements, it is not easy to confirm the existence of water at low RH or not. In this study, we confirmed the existence of supersaturated GlyA droplets at near 0% RH based on the detection of the Raman water band. Additional spectral feature of GlyA at 0% RH was also observed. The partial phase transitions and water contents of the AS-MA and AS-GA systems were determined under both aqueous and mixed phase conditions using in-situ Raman analyses. For the organic components in the mixtures, the intensity ratio of the C=O double-peak at about 1700 cm 1 was used as a spectral indicator for the partial phase transitions. Agreement between the results and published data collected using other techniques, and also agreement with modelling predictions, give us confidence in using micro-raman spectroscopy for studying more complicated mixed systems involving inorganics and organics. 2. EXPERIMENTAL 2.1. Air-Flow Observation Cell and Sample Preparation An air-flow observation cell (Yeung et al. 2009) was used to maintain stable humidity conditions for examining the particles. The cell was made of stainless steel with a quartz window in the top to allow micro-raman observations. A smooth fluorocarbon film (1.0 mil, available from YSI Inc.) was used as the hydrophobic substrate for the deposited particles. The substrate was supported by a glass plate in the cell. The environment inside the cell was monitored by a humidity sensor (HIH-3610 Series, Honeywell) and a temperature sensor (LM35CZ, RS Components) accurate to ±2% RH and ±1 C, respectively. The RH inside the cell was controlled by a filtered airflow feed. The RH of the airflow was adjusted by mixing dry air with an air stream humidified with a water bubbler. Pure AS particles reach equilibrium within 15 min (Yeung et al. 2009). To ensure that equilibrium was reached in these experiments, a minimum of an hour was allowed. Typically, the experiments were performed at ambient temperatures of 24 ± 2 C. Another observation cell with a heat plate (TCM-Series, Electron dynamics), which can control the temperature of the substrate from 10 to 100 C, was used for high temperature measurements of GlyA particles. To prepare the aqueous solutions, pure AS, AN, MA, GA, and GlyA were dissolved in 18.0 M purified water. The AS- MA and AS-GA mixed solutions were prepared at a 1:1 mole ratio. All the compounds were purchased from Sigma-Aldrich and had purity better than 99.0%. A pre-washed spray bottle was used to deposit droplets directly on the hydrophobic substrate in the observation cell. Droplets with diameters less than 40 µm were chosen by an optical microscope for investigation. The diameters of the dry particles obtained from evaporation of droplets ranged from 10 to 30 µm Raman Spectral Measurements Raman spectra were acquired under different RH conditions using a Renishaw RM series micro-raman spectrometer. This was the same Raman system used by Wu and Chan (2008). A 20 mw Argon ion laser (514.5 nm) was applied for sample excitation. Single particles were located with an optical microscope (Leica DMLM) with a reflected light illumination attached to the Raman system. The laser beam was focused on the center of a particle through a 50 objective lens, which provided spatial resolution of about 6 µm. An 1800 g mm 1 grating was used to form the spectra in the range from 200 to 4000 cm 1 with a resolution of 1.4 cm 1.

4 For all the pure compounds and mixtures, duplicate particles were monitored through a full humidity cycle. The humidity cycle started from evaporation at high RH (>80%) to the dry state (near 0% RH). The particles were then allowed to grow in gradually increasing RH. Additional evaporation experiments were performed to obtain more hygroscopic data. WATER CONTENT AND PHASE TRANSITIONS IN PARTICLES Hygroscopicity Determination Based on Raman Spectra The integrated area of certain Raman peaks was used to quantify the hygroscopic properties of the particles. Yeung et al. (2009) has described a similar analysis. A big envelope of overlapping Raman peaks containing two O-H bands (3240 and 3430 cm 1 ), three NH + 4 bands (2880, 3080, and 3220 cm 1, for ammonium-containing particles) and two C-H peaks (near 3000 cm 1, for organic particles) was recorded between 2700 and 3800 cm 1. Gaussian peak fitting was used to extract individual water peaks at 3430 cm 1. To compare the water peaks measured at different RHs with different particles, normalization was performed by dividing the water peak area by the area of a distinct solute peak. The sulfate stretching peak (980 cm 1 ) was chosen for all AS-containing particles, while the nitrate (1048 cm 1 ) and C=O( 1700 cm 1 ) peaks were used for AN and organic acid particles, respectively. The peak area ratios, A(water)/A(solute) were converted to water-to-solute mass ratios (WSR). The conversion was based on the assumption that the peak area was directly proportional to the species concentration. WSR values in the aqueous phase (>80% RH) were predicted using the Extended-Aerosol Inorganic Model (E-AIM). The principle of the model to calculating solute and solvent activities in aqueous solution was described by Clegg et al. (1992). Inorganic Model II (available at was used to calculate the water activities of AN and AS (Clegg et al. 1998) and the UNIFAC model was used for the organic compounds. For the AS-organic mixed systems, the water activities were estimated using the method described by Clegg et al. (2001). The predicted WSR values were used as reference points to calculate the WSR at other RH values. In the growth experiments, no water signal was detected with the solid particles until they dissolved. The WSR was therefore set to zero for solid particles. 3. RESULTS AND DISCUSSION 3.1. Hygroscopicity AS and AN have been recognized as the predominant inorganic constituents in atmospheric aerosols. Their hygroscopic properties have been modelled and are well understood. So their hygroscopicity as determined through the Raman spectral analyses was first compared with the modelling results to validate the Raman method for quantitative hygroscopic measurements. Figures 1a and 1b illustrate the changes in the water content of pure AS and AN particles, respectively. The WSRs of aqueous AS and AN calculated from the E-AIM model are also included FIG. 1. Hygroscopicity (WSR, mass of water/mass of solute) of (a) AS and (b) AN particles as a function of RH obtained by micro-raman spectroscopy. Predictions from the E-AIM model are also included. in the figure for comparison. The water contents of both pure inorganic particles determined by Raman spectroscopy agreed well with those predicted by the model. Aqueous AS particles became more saturated with decreasing RH and finally lost all water below 40% RH. In contrast, AN either formed dry particles below 30% RH or persisted as supersaturated droplets even at 0% RH. The hygroscopic results for the organics (MA, GA, and GlyA) are shown in Figure 2. The calculated WSRs were compared with the predictions of the UNIFAC model using Peng s modified interaction parameters (Peng et al. 2001). The hygroscopic properties of pure MA agreed well with the modified UNIFAC predictions. The continuous curve down to about 10% RH was generally consistent with Peng s observation that water was retained by MA particles at decreasing RH, but no water was detected at RH less than 15% (Peng et al. 2001). The GA results were also in excellent agreement with modelling predictions. With decreasing RH, water in the GA particles gradually evaporated until the RH reached about 30%, when the WSR dropped to zero, indicating crystallization. The hygroscopicity of GlyA was recently studied by Chan et al. (2008), who found that GlyA was non-deliquescent and followed the trend

5 272 M. C. YEUNG AND C. K. CHAN FIG. 3. Hygroscopicity (WSR, mass of water/mass of solute) of AS-MA mixed particles (in 1:1 mole ratio) undergoing (a) evaporation and (b) growth processes obtained by micro-raman spectroscopy. Data from Choi and Chan (2002) and Ling and Chan (2008) and predictions from the ZSR and E-AIM models are also included. FIG. 2. Hygroscopicity (WSR, mass of water/mass of solute) of (a) MA, (b) GA, and (c) GlyA particles as a function of RH obtained by micro-raman spectroscopy. Predictions from the UNIFAC model are also included. of UNIFAC predictions. In this study, the results also indicates the presence of water at RH down to 0%, but the water contents were slightly higher than the predicted values at low RHs. For the most part the observations were generally in line with those of Chan et al. (2008), but in their measurements the mass ratios (m/m o ) in response to the changing RH were reported and the particle mass at the lowest RH (6%) was used as the reference mass (m o ). The mass ratio was unity at that RH and it did not necessarily represent the anhydrous state. Variation in the water content of the AS-MA particles in the course of a humidity cycle is shown in Figure 3 along with data from previous measurements using the EDB techniques (Choi and Chan 2002; Ling and Chan 2008). The AS-MA particles in this study are of the same composition (1:1 mole ratio) with those studied in the literature. The spectral results were consistent with the hygroscopic properties described by Ling and Chan (2008). However, a difference between these measurements and those of Choi and Chan (2002) was seen in the evaporation measurements. In that study, partial crystallization occurred at about 46% RH, as indicated by the small decrease in particle mass, and the mixture became anhydrous at RH below 20%. In the present study, water signals were detected even at 3% RH, indicating incomplete crystallization. In the growth experiments, gradual water uptake with increasing RH from 3% was

6 WATER CONTENT AND PHASE TRANSITIONS IN PARTICLES 273 FIG. 4. Hygroscopicity (WSR, mass of water/mass of solute) of AS-GA mixed particles (in 1:1 mole ratio) undergoing (a) evaporation and (b) growth processes obtained by micro-raman spectroscopy. Data from Choi and Chan (2002) and Ling and Chan (2008) and predictions from the ZSR and E-AIM models are also included. observed. This also indicates that the AS-MA particles did not completely crystallize. Moreover, a notable increase in the water content at about 74% RH indicates complete deliquescence. The black curves in Figure 3 present the E-AIM model s predictions (the solute activity was based on UNIFAC calculations). Assuming that the system partially crystallized, with only AS existing as a solid, water uptake would gradually start from the lowest RH of 10% (the lowest operating RH of the model). The growth curve overlapped the evaporation curve at 72% RH, the predicted DRH, which was close to the 74% DRH measured in the experiments. When compared with the predictions, all the laboratory studies measured lower WSR values under conditions below 70% RH. The discrepancy reveals over-prediction by the model of water uptake in supersaturated environments (Ling and Chan 2008). The water content of AS-MA system was also estimated based on the Zdanovskii-Stokes-Robinson (ZSR) relationship (Stokes and Robinson 1966; Clegg and Seinfeld 2004). The ZSR estimations are included in the figure for comparison with the E-AIM model. The E-AIM predictions were very close to the ZSR estimations for the AS-MA system. The hygroscopicity of the AS-GA system (1:1 mole ratio) is illustrated in Figure 4. The responses of the AS-GA system to water again showed trends very similar to those measured by Ling and Chan (2008). During evaporation, the AS-GA particles gradually lost water until, at an RH of 30% RH or less, the anhydrous state was reached. The CRH of the AS- GA system, as inferred from the zero WSR, ranged from 16 to 32.5% RH. Choi and Chan (2002) reported a clear mass reduction at about 60% RH, meaning that partial crystallization took place. In their study, early crystallization at significantly higher RH relative to other studies was observed with both AS-MA and AS-GA. This might have been due to heterogeneous nucleation initiated by trace amounts of contaminants. In the growth experiments, significant water uptake occurred at 78.5% RH, as indicated in Figure 4b. Hence, the DRH of the system was slightly lowered relative to the pure components. The decreased DRH has also been confirmed by studies which observed values ranging from 77 to 78.5% RH (Prenni et al. 2003; Pant et al. 2004; Zardini et al. 2008). Moreover, water absorption started at about 70% RH. The pre-deliquescence water uptake of the AS-GA system has previously been observed in EDB measurements (Choi and Chan 2002; Ling and Chan 2008). Early water uptake was also predicted by the FIG. 5. Raman spectra of a single (a) AS and (b) AN particles upon evaporation.

7 274 M. C. YEUNG AND C. K. CHAN E-AIM and the ZSR methods. However, both methods again overpredicted the water uptake during partial deliquescence. The DRH estimated by ZSR method is about 70% RH, which is even lower than that predicted by the E-AIM model (74.5% RH). Ling and Chan (2008) suggested that the higher water content was due to the over-prediction of the extent of dissolution of the organic acids during partial deliquescence Phase Transitions of Single-Component Systems Phase transitions involve the interruption of molecular interactions, leading to Raman spectral variations such as abrupt changes in the solute peak s position and shape. These can provide further evidence of phase transitions. The Raman spectra of a single AS and AN droplets undergoing evaporation with the occurrence of crystallization are presented in Figure 5a and b. From the Raman spectra, the phase transitions of particles can be directly recognized from particular spectral changes. The presence of water bands can distinguish between aqueous and dry states. Changes in the Raman shift magnitude during phase transitions of AS and AN have been reported by a few investigators (Musick et al. 2000; Zhang and Chan 2002; Jordanov and Zellner 2006). The Raman peaks of solid particles are more intense and sharper relative to aqueous particles, so a sudden change in the fwhh (normalized to that at the lowest RH) of a distinct peak is also useful for phase identification (Lee et al. 2008; Ling and Chan 2008). In this study, the changes in the fwhh and the positions of the ν 1 (SO 2 4 ) and ν 1 (NO 3 ) peaks were observed through a humidity cycle. The results are depicted in Figures 6a and b. During evaporation, the sudden drops in the fwhh at 39.5% RH (AS) and between 0 and 10% RH (AN) indicate crystallization. Clear steps in the red shift from 980 to 974 cm 1 for AS and 1048 to 1043 cm 1 for AN were also observed, consistent with literature reports. Conversely, deliquescence of dry particles was confirmed by an abrupt increase in fwhh due to peak broadening and blue shifting of the ν 1 (SO 2 4 ) and ν 1(NO 3 ) peaks. According to the parallel trend of peak position and fwhh, the DRHs measured for AS and AN particles were 79.5% and 63%, respectively. The crystallization properties of AN particles have been reported in several studies, and relatively large deviations have been reported. Tang (1996) and Chan et al. (1992) both observed solid formation near 30%. However, Dougle et al. (1998) and Cziczo and Abbatt (2000) did not detect crystallization in submicron AN particles below 10% RH. Furthermore, Lightstone et al. (2000) detected a wide range of CRH from 0 to 30% RH for the AN microparticles generated from aqueous solution. Figure 6c presents the results of three evaporation experiments. These experiments also produced evidence of supersaturated particles even at 0% RH and of crystallization between 0% and 30% RH. Lightstone et al. (2000) suggested the large deviations were due to the crystallization of larger AN particles promoted by the presence of impurities via heterogeneous nucleation. Schlenker et al. (2004) also suggested heterogeneous nucleation as the primary FIG. 6. Changes in normalized fwhh and Raman shift of the (a) sulfate peak (980 cm 1 ) of a single AS particle and (b) nitrate peak (1048 cm 1 ) of a single AN particle through a humidity cycle, and (c) changes in the Raman shift of the nitrate peak (1048 cm 1 ) of three individual AN particles upon crystallization. crystallization pathway of aqueous AN particles. They observed the noncrystallite AN particles at 1% RH. However, formation of AN solids from the initially aqueous particles via heterogeneous nucleation in the presence of sulfate crystals was evident. Figures 7a and b illustrate the Raman spectra of MA and GA droplets undergoing evaporation. Changes in the fwhh and in the position of the ν (C=O) of MA and GA are shown in Figures 8a and b. A sharp shift in the peak position and a decrease in fwhh indicate that crystallization of MA and GA particles occurred at RHs below 10% and 30%, respectively. Although

8 WATER CONTENT AND PHASE TRANSITIONS IN PARTICLES 275 FIG. 7. Raman spectra of a single (a) MA and (b) GA particles upon evaporation. Peng et al. (2001) reported that MA particles did not crystallize at low RH of 5%, such crystallization events were observed by Braban et al. (2003) at 6% RH. During the growth process, the abrupt increase in both the ν(c=o) peak s position and fwhh at 67% RH indicates deliquescence, consistent with Peng s bulk measurement of 65.3% RH and Braban s determination of 69% RH (Peng et al. 2001; Braban et al. 2003). For GA, the CRH has been reported as 29 33% (Peng et al. 2001) and % (Pant et al. 2004). Deliquescence has been observed between 83 and 90% RH (Zardini et al and the references therein). The results of this study with GA agreed with those literature reports. No phase transition was found for GlyA, as there was no abrupt change in the position or fwhh of the ν(c=o) peak (see Figure 8c). However, additional spectral feature of GlyA particles were observed at 0% RH. The Raman spectra of a GlyA particle undergoing evaporation are presented in Figure 9a. A new small peak at 1820 cm 1 appeared to be a new C=O peak together with the aqueous C=O peak at 1735 cm 1. Due to its polar nature, GlyA dissolves in water. If the water content is greatly reduced, GlyA will form metastable solution droplets, and interactions between solutes will be enhanced. In this study, the measured WSR of GlyA near 0% RH was 0.1, at which point the GlyA molecules would be 40 times more abundant than the water molecules. Additional measurements of GlyA particles were made at 0% RH and at a temperature of 50 C to see if GlyA could retain water under dry and hot conditions. The Raman signal from the water was still detected, as seen in Figure 9b, albeit at a reduced intensity. At the same time, the C=O stretching at 1820 cm 1 intensified as the temperature increased. A possible reason for the C=O stretching at the higher shift position (>1800 cm 1 ) is the presence of some anhydride (Socrates 2001). However, the data were not sufficient to confirm the formation of anhydride. FIG. 8. Changes in normalized fwhh and Raman shift of the C=O peak of single (a) MA and (b) GA particles through a humidity cycle, and (c) a GlyA particle upon evaporation Partial Phase Transitions of AS-Organic Mixed Systems We have observed the gradual change of water content in AS- MA and AS-GA mixed systems, which suggests the presence of

9 276 M. C. YEUNG AND C. K. CHAN FIG. 10. Changes in (a) the normalized fwhh of the sulfate peak (980 cm 1 ) and (b) the intensity ratio of the C=O double-peak (I 1730 /I 1665 )ofas-ma mixed particles through a humidity cycle. FIG. 9. Raman spectra of a single GlyA particle (a) upon evaporation and (b) under dry and hot conditions. mixed-phase particles under certain RH conditions. However, WSR ratio measurements cannot provide direct information on the phase state of each species. This must be obtained through additional spectroscopic analysis. Figure 10a includes plots of the changing fwhh of the ν 1 (SO 2 4 ) peaks of two AS-MA particles, showing the two different behaviors of the AS fraction. For particle 1, crystallization was evident in the sharp decrease in the fwhh at 19.5% RH, consistent with the work of Ling and Chan (2008) in which partial crystallization for the AS-MA system was observed between 16 and 20% RH. However, no complete crystallization was observed in particle 2 down to 1% RH. The observations generally agreed with the results by Braban et al. (2004) and Parsons et al. (2004) who detected no crystallization of submicron particles and observed CRHs between 0 and 20% RH. It is clear that MA could significantly suppress or even inhibit the crystallization of AS in this system. In the growth measurements, obvious in- creases in the fwhh at 70% RH imply that the crystalline AS fraction absorbed water below the DRH of pure AS. The further increase in fwhh at 74% suggests that the AS fraction completely deliquesced at this RH. The complete DRH found in this study also agreed well with the 73.4% RH reported by Parsons et al. (2004). There was no distinct change in either the shifting or fwhh of the ν(c=o) peak (figures not shown) to indicate any phase transition in the MA fraction. However, a gradual development of a shoulder was noticeable at 1665 cm 1 which gave a ν(c=o) double-peak with decreasing RH (see Figure 11). The 1665 cm 1 shoulder, which was also observed by Ling and Chan (2008), arises from crystalline MA. Since the features of the peak at 1730 cm 1 were affected by the shoulder, the peak position and fwhh of the ν(c=o) peak might not be accurate for phase characterization. Instead, the intensity ratio of the double-peak I 1730 /I 1665 was used to identify the phase state of MA in the system. The intensity ratios at different RHs are shown in Figure 10(b). The ratio suddenly dropped at 19.5% RH (Particle 1) due to the significant contribution of the 1680 cm 1 peak. This large change serves as a good indication

10 WATER CONTENT AND PHASE TRANSITIONS IN PARTICLES 277 FIG. 11. Raman spectra of a single AS-MA mixed particle upon evaporation. of the partial crystallization of the MA at about 20% RH, and it is probably induced by the AS crystals. Ling and Chan (2008) also postulated from the presence of the shoulder peak that MA was partially crystallized. Further reduction of RH to 3% did not cause significant decrease in the ratio, meaning that aqueous and solid MA coexisted at RHs below 19.5%. As the droplet grew, the ratio gradually increased from 3% to 70% RH, which may be explained by water uptake due to the presence of aqueous MA. The ratio reached its maximum when the RH increased to 70%, indicating that the MA fraction completely dissolved below the DRH at 74%. On the other hand, the MA fraction in particle 2 did not crystallize, as indicated by the absence of any abrupt change in the ratio. The MA fraction remained as a supersaturated solution, presumably because no AS crystal was present to serve as a heterogeneous nucleus. The results with the AS-GA system are shown in Figure 12. Again, the phase of the AS fraction in AS-GA mixture was inferred from the changing fwhh of the ν 1 (SO 2 4 ) peak shown in Figure 12a. AS crystallization took place at % RH, which was confirmed by the abrupt decrease in fwhh. This observed RH value was higher than the complete CRH of the system (16 to 32.5%). This implies that partially crystallized metastable AS-GA particles were present. During the growth experiments, partial dissolution of AS starting at about 70% RH was confirmed by the gradually increasing fwhh, followed by the sharply increased fwhh at 78.5% RH that confirmed complete deliquescence, consistent with the DRH inferred from the hygroscopic observations. As with the AS-MA system, the intensity ratio of the C=O stretching peaks was used to correlate the phase properties of GA in the AS-GA system. Two peaks were observed at 1708 cm 1 and 1658 cm 1, corresponding to the aqueous phase and the solid form of GA, respectively. The variation in the intensity ratio I 1705 /I 1658 at different RHs is illustrated in Figure 12b. For Particle 1, a single-step complete crystallization was confirmed at 32.5% RH by the sudden drops in both the fwhh of the ν 1 (SO 2 4 ) peak and the intensity ratio of the C=O stretching peaks. The results were consistent with the observations of Ling and Chan (2008) and Zardini et al. (2008), who reported the single-step crystallization of AS-GA between 31 and 36% RH. On the other hand, we observed gradual reductions in the FIG. 12. Changes in (a) the normalized fwhh of the sulfate peak (980 cm 1 ) and (b) the intensity ratio of the C=O double-peak (I 1708 /I 1658 ) of AS-GA through a humidity cycle.

11 278 M. C. YEUNG AND C. K. CHAN FIG. 13. Raman spectra of a single AS-GA mixed particle upon evaporation. intensity ratio in Particles 2 and 3. When the AS fractions first crystallized at 32.5 and 36% RH, respectively, the C=O ratio dropped from 3.5 to 1.5. The ratio further gradually decreased and reached near zero upon complete crystallization at 16 and 24% RH. Figure 13 shows the Raman spectra of the gradual crystallization of Particle 3. It is apparent that AS has crystallized at 36% RH while GA remained in the aqueous state until it crystallized at 24% RH. The gradual reduction of the intensity ratio suggests that GA partially formed along with the crystalline AS prior to complete crystallization. The CRH of pure GA is generally lower than that of pure AS. This suggests that the AS fraction in the system might have crystallized first followed by that of the GA fraction, leading to partial crystallization. When the RH increased to about 70% in the growth measurement, the aqueous peak was detectable and the peak ratio increased slightly. A small and gradual increase in the ratio was observed roughly between 70% and 78% RH. More significant enhancement in the ratio was noted at 78.5% RH due to the full development of the aqueous peak and the disappearance of the solid peak. The gradual dissolution of GA below the DRH may explain the overpredicted results by the E-AIM model, in which GA was assumed to fully deliquesce at 72% RH. 4. CONCLUSIONS The application of micro-raman spectroscopy to studying the hygroscopicity and phase properties of particles incorporating inorganic species, organic species, and their mixtures has been demonstrated here. Excellent agreement between the hygroscopicity measured in this study and previously published results confirms the possibility of accurate quantitative measurements with Raman spectroscopy. Spectroscopic measurements also enable the characterization of particle phases. Changes in peak positions and fwhh serve as good indicators to identify phase transitions with both inorganic and organic solutes, especially with species that can retain water at very low RH. For example, malonic acid and glyoxylic acid remain as supersaturated droplets at low RH and exhibited continuous hygroscopicity. For mixed particles, it is not easy to infer the occurrence of the phase transition from the continuous curves of water content over the whole range of RH. Instead, spectral analysis can provide direct evidence of the phase states. EDB and HTDMA techniques are widely used to investigate the hygroscopic properties and phase transitions of levitated particles. However, without also calling on spectroscopy, these techniques cannot give direct information about the phase state of the components in mixed particles. The conventional EDB technique can be combined with spontaneous Raman spectroscopy (Fung and Tang 1988). Such a coupled system is able to measure particle mass and spectra at the same time. On the other hand, micro-raman spectroscopy is a stand-alone technique for characterization which facilitates in situ measurements of hygroscopicity and phase transition. Sampling and operation are relatively straightforward. Data generated by EDB are limited because only one particle can be examined at a time. In micro- Raman measurements, individual particles are firmly held on the substrate and can be easily located with a microscope, enabling multiple individual particles to be analyzed in a single measurement. Some limitations of the HTDMA technique can also be avoided using micro-raman analysis. Size correction is essential when using HTDMA with non-spherical particles to obtain accurate measurements. Moreover, mass transfer delay effects can be an issue in HTDMA measurements in which only a short period of time is allowed for humidity equilibration (Chan and Chan 2005). Micro-Raman spectroscopy is particularly valuable for elucidating gradual water uptake behavior and partial phase changes, which are usually expected to occur in multi-component systems. We successfully quantified the water content of mixedphase AS-MA and AS-GA particles during the course of partial deliquescence. As with pure AS, the phase properties of the AS fractions in the mixtures were easily characterized by the

12 WATER CONTENT AND PHASE TRANSITIONS IN PARTICLES 279 changes in position and fwhh of the sulfate peak. For the organic acid components, the utility of the C=O stretching intensity ratio for identifying phase states during the partial crystallization and deliquescence has been amply demonstrated. Our measurements illustrate the complicated hygroscopic behavior and phase transitions in such mixed systems, which can be untangled by comprehensive spectral analyses. However, it should be noted that sample fluorescence is the major limitation of Raman spectroscopic studies. Relatively weak Raman signals will be overwhelmed by any broadband fluorescence background. Moreover, some species such as NaCl do not give Raman signals in solution for quantitative measurement of the water content, and external calibration is necessary. Finally, the size of particles examined by this technique is comparable with those of EDB but much larger than those of HTDMA and of ambient particles. REFERENCES Braban, C. F., and Abbatt, J. P. D. (2004). A Study of the Phase Transition Behavior of Internally Mixed Ammonium Sulfate-Malonic Acid Aerosols. Atmo. Chem. Phys. 4: Braban, C. F., Carroll, M. F., Styler, S. A., and Abbatt, J. P. D. (2003). Phase Transitions of Malonic and Oxalic Acid Aerosols. J. Phy. Chem. A 107: Chan, C. K., Flagan, R. C., and Seinfeld, J. H. (1992). Water Activities of NH 4 NO 3 /(NH 4 ) 2 SO 4 Solutions. Atmo.Env.PartA26: Chan, M. N., and Chan, C. K. (2005). Mass Transfer Effects in Hygroscopic Measurements of Aerosol Particles. Atmo. Chem. Phys. 5: Chan, M. N., Kreidenweis, S. M., and Chan, C. K. (2008). Measurements of the Hygroscopic and Deliquescence Properties of Organic Compounds of Different Solubilities in Water and Their Relationship with Cloud Condensation Nuclei Activities. Environ. Sci. Technol. 42: Charlson, R. J., Schwartz, S. E., Hales, J. M., Cess, R. D., Coakley, J. A., Hansen, J. E., and Hofmann, D. J. (1992). Climate Forcing by Anthropogenic Aerosols. Science 255: Choi, M. Y., and Chan, C. K. (2002). The Effects of Organic Species on the Hygroscopic Behaviors of Inorganic Aerosols. Environ. Sci. Technol. 36: Clegg, S. L., Brimblecombe, P., and Wexler, A. S. (1998). Thermodynamic Model of the System H + -NH + 4 -SO2 4 -NO 3 -H 2O at Tropospheric Temperatures. J. Phy. Chem. A 102: Clegg, S. L., Pitzer, K. S., and Brimblecombe, P. (1992). Thermodynamics of Multicomponent, Miscible, Ionic Solutions. II. Mixtures Including Unsymmetrical Electrolytes. J. Phys. Chem. 96: Clegg, S. L., and Seinfeld, J. H. (2004). Improvement of the Zdanovskii- Stokes- Robinson Model for Mixtures Containing Solutes of Different Charge Types. J. Phys. Chem. A 108: Clegg, S. L., Seinfeld, J. H., and Brimblecombe, P. (2001). Thermodynamic Modelling of Aqueous Aerosols Containing Electrolytes and Dissolved Organic Compounds. J. Aerosol Sci. 32: Cohen, M. D., Flagan, R. C., and Seinfeld, J. H. (1987). Studies of Concentrated Electrolyte Solutions Using the Electrodynamic Balance. 1. Water Activities for Single Electrolyte Solutions. J. Phy. Chem. 91: Cziczo, D. J., and Abbatt, J. P. D. (2000). Infrared Observations of the Response of NaCl, MgCl 2,NH 4 HSO 4,andNH 4 NO 3 Aerosols to Changes in Relative Humidity from 298 to 238 K. J. Phy. Chem. A 104: Cziczo, D. J., Nowak, J. B., Hu, J. H., and Abbatt, J. P. D. (1997). Infrared Spectroscopy of Model Tropospheric Aerosols as a Function of Relative Humidity: Observation of Deliquescence and Crystallization. J. Geophys. Res. 102: Dong, J. L., Li, X. H., Zhao, L. J., Xiao, H. S., Wang, F., Guo, X., and Zhang, Y. H. (2007). Raman Observation of the Interactions between NH + 4,SO2 4, and H 2 O in Supersaturated (NH 4 ) 2 SO 4 droplets. J. Phy. Chem. B 111: Dougle, P. G., Veefkind, J. P., and ten Brink, H. M. (1998). Crystallisation of Mixtures of Ammonium Nitrate, Ammonium Sulphate and Soot. J. Aerosol Sci. 29: Forster, P., Ramaswamy, V., Artaxo, P., Berntsen, T., B., R., Fahey, D. W., Haywood, J., Lean, J., Lowe, D. C., Myhre, G., Nganga, J., Prinn, R., Raga, G., Schulz, M., and Van Dorland, R. (2007). Changes in Atmospheric Constituents and in Radiative Forcing. In Climate Change 2007: The Physical Science Basis. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Solomon, S., Qin, D., Manning, M., Chen, Z., Marquis, M., Averyt, K. B., Tignor, M., and Miller, H. L., eds. New York, Fung, K. H., and Tang, I. N. (1988). Raman Scattering from Single Solution Droplets. Appl. Opt. 27: Haywood, J., and Boucher, O. (2000). Estimates of the Direct and Indirect Radiative Forcing due to Tropospheric Aerosols: A Review. Rev. Geophys. 38: Herrmann, H. (2003). Kinetics of Aqueous Phase Reactions Relevant for Atmospheric Chemistry. Chem. Rev. 103: Horvath, H. (1993). Atmospheric Light Absorption A Review. Atmo. Env. Part A 27: Jordanov, N., and Zellner, R. (2006). Investigations of the Hygroscopic Properties of Ammonium Sulfate and Mixed Ammonium Sulfate and Glutaric Acid Micro Droplets by Means of Optical Levitation and Raman Spectroscopy. Phys. Chem. Chem. Phys. 8: Kaufman, Y. J., Tanre, D., and Boucher, O. (2002). A Satellite View of Aerosols in the Climate System. Nature 419: Kreidenweis, S. M., Koehler, K., DeMott, P. J., Prenni, A. J., Carrico, C., and Ervens, B. (2005). Water Activity and Activation Diameters from Hygroscopicity Data Part I: Theory and Application to Inorganic Salts. Atmo. Chem. Phys. 5: Lee, A. K. Y., Ling, T. Y., and Chan, C. K. (2008). Understanding Hygroscopic Growth and Phase Transformation of Aerosols Using Single Particle Raman Spectroscopy in an Electrodynamic Balance. Faraday Discuss. 137: Li, X. H., Wang, F., Lu, P. D., Dong, J. L., Wang, L. Y., and Zhang, Y. H. (2006). Confocal Raman Observation of the Efflorescence/Deliquescence Processes of Individual NaNO 3 Particles on Qartz. J. Phy. Chem. B 110: Lightstone, J. M., Onasch, T. B., Imre, D., and Oatis, S. (2000). Deliquescence, Efflorescence, and Water Activity in Ammonium Nitrate and Mixed Ammonium Nitrate/Succinic Acid Microparticles. J. Phy. Chem. A 104: Ling, T. Y., and Chan, C. K. (2008). Partial Crystallization and Deliquescence of Particles Containing Ammonium Sulfate and Dicarboxylic Acids. J. Geophys. Res. 113:D14205, doi: /2008jd Liu, Y. J., Zhu, T., Zhao, D. F., and Zhang, Z. F. (2008a). Investigation of the Hygroscopic Properties of Ca(NO 3 ) 2 and Internally Mixed Ca(NO 3 ) 2 /CaCO 3 Particles by Micro-Raman Spectrometry. Atmo. Chem. Phys. 8: Liu, Y., Yang, Z., Desyaterik, Y., Gassman, P. L., Wang, H., and Laskin, A. (2008b). Hygroscopic Behavior of Substrate-Deposited Particles Studied by Micro-FT-IR Spectroscopy and Complementary Methods of Particle Analysis. Anal. Chem. 80: Martin, S. T. (2000). Phase Transitions of Aqueous Atmospheric Particles. Chem. Rev. 100: McMurry, P. H., and Stolzenburg, M. R. (1989). On the Sensitivity of Particle Size to Relative Humidity for Los Angeles Aerosols. Atmo. Env. 23: Musick, J., Popp, J., and Kiefer, W. (2000). Observation of a Phase Transition in an Electrodynamically Levitated NH 4 NO 3 Microparticle by Mie and Raman Scattering. J. Raman Spectrosc. 31: Nemesure, S., Wagener, R., and Schwartz, S. E. (1995). Direct Shortwave Forcing of Climate by the Anthropogenic Sulfate Aerosol: Sensitivity to Particle Size, Composition, and Relative Humidity. J. Geophys. Res. 100: Novakov, T., and Penner, J. E. (1993). Large Contribution of Organic Aerosols to Cloud Condensation Nuclei Concentrations. Nature 365:

13 280 M. C. YEUNG AND C. K. CHAN Onasch, T. B., Siefert, R. L., Brooks, S. D., Prenni, A. J., Murray, B., Wilson, M. A., and Tolbert, M. A. (1999). Infrared Spectroscopic Study of the Deliquescence and Efflorescence of Ammonium Sulfate Aerosol as a Function of Temperature. J. Geophys. Res. 104: Pant, A., Fok, A., Parsons, M. T., Mak, J., and Bertram, A. K. (2004). Deliquescence and Crystallization of Ammonium Sulfate-Glutaric Acid and Sodium Chloride-Glutaric Acid Particles. Geophys. Res. Lett. 31:L12111, doi: /2004gl Parsons, M. T., Knopf, D. A., and Bertram, A. K. (2004). Deliquescence and Crystallization of Ammonium Sulfate Particles Internally Mixed with Water Soluble Organic Compounds. J. Phy. Chem. A 108: Peng, C., Chan, M. N., and Chan, C. K. (2001). The Hygroscopic Properties of Dicarboxylic and Multifunctional Acids: Measurements and UNIFAC Predictions. Environ. Sci. Technol. 35: Penner, J. E., Andreae, M., Annegarn, H., Barrie, L., Feichter, J., Hegg, D., Jayaraman, A., Leaitch, R., Murphy, D., Nganga, J., and Pitari, G. (2001). Aerosols, Their Direct and Indirect Effects. In Climate Change 2001: The Scientific Basis. Contribution of Working Group I to the Third Assessment Report of the Intergovernmental Panel on Climate Change. Houghton, J. T., Ding, Y., Griggs, D. J., Noguer, M., van der Linden, P. J., Dai, X., Maskell, K., and Johnson, C. A., eds. New York, Pilinis, C., Pandis, S. N., and Seinfeld, J. H. (1995). Sensitivity of Direct Climate Forcing by Atmospheric Aerosols to Aerosols Size and Composition. J. Geophys. Res. 100: Prenni, A. J., De Mott, P. J., and Kreidenweis, S. M. (2003). Water Uptake of Internally Mixed Particles Containing Ammonium Sulfate and Dicarboxylic Acids. Atmo. Env. 37: Richardson, C. B., and Spann, J. F. (1984). Measurement of the Water Cycle in a Levitated Ammonium Sulfate Particle. J. Aerosol Sci. 15: Rogge, W. F., Mazurek, M. A., Hildemann, L. M., Cass, G. R., and Simoneit, B. R. T. (1993). Quantification of Urban Organic Aerosols at a Molecular Level Identification, Abundance and Seasonal Variation, Atmo. Env. Part A 27: Saxena, P., and Hildemann, L. M. (1996). Water-Soluble Organics in Atmospheric Particles: A Critical Review of the Literature and Application of Thermodynamics to Identify Candidate Compounds. J. Atmo. Chem. 24: Saxena, P., Hildemann, L. M., McMurry, P. H., and Seinfeld, J. H. (1995). Organics Alter Hygroscopic Behavior of Atmospheric Particles. J. Geophys. Res. 100: Schlenker, J. C., Malinowski, A., Martin, S. T., Hung, H. -M., and Rudich, Y. (2004). Crystals Formed at 293 K by Aqueous Sulfate-Nitrate-Ammonium- Proton Aerosol Particles. J. Phy. Chem. A 108: Seinfeld, J. H., and Pandis, S. N. (2006). Atmospheric Chemistry and Physics: From Air Pollution to Climate Change. John Wiley & Sons, New Jersey. Socrates, G. (2001). Infrared and Raman Charactristic Group Frequencies: Tables and Charts. John Wiley & Sons, Chichester. Stokes, R. H., and Robinson, R. A. (1966). Interactions in Aqueous Nonelectrolyte Solutions. I. Solute-Solvent Equilibria. J. Phys. Chem. 70: Svenningsson, B., Hansson, H. C., Martinsson, B., Wiedensohler, A., Swietlicki, E., Cederfelt, S. I., Wendisch, M., Bower, K. N., Choularton, T. W., and Colvile, R. N. (1997). Cloud Droplet Nucleation Scavenging in Relation to the Size and Hygroscopic Behaviour of Aerosol Particles. Atmo. Env. 31: Swietlicki, E., Hansson, H. C., Hameri, K., Svenningsson, B., Massling, A., McFiggans, G., McMurry, P. H., Petaja, T., Tunved, P., Gysel, M., Topping, D., Weingartner, E., Baltensperger, U., Rissler, J., Wiedensohler, A., and Kulmala, M. (2008). Hygroscopic Properties of Submicrometer Atmospheric Aerosol Particles Measured with H-TDMA Instruments in Various Environments A Review. Tellus Series B 60: Tang, I. N. (1996). Chemical and Size Effects of Hygroscopic Aerosols on Light Scattering Coefficients, J. Geophys. Res. 101: Tang, I. N., Fung, K. H., Imre, D. G., and Munkelwitz, H. R. (1995). Phase Transformation and Metastability of Hygroscopic Microparticles. Aerosol Sci. Technol. 23: Wang, F., Zhang, Y. H., Li, S. H., Wang, L. Y., and Zhao, L. J. (2005). A Strategy for Single Supersaturated Droplet Analysis: Confocal Raman Investigations on the Complicated Hygroscopic Properties of Individual MgSO 4 Droplets on the Quartz Substrate. Anal. Chem. 77: Wu, H. B., and Chan, C. K. (2008). Effects of Potassium Nitrate on the Solid Phase Transitions of Ammonium Nitrate Particles. Atmo. Env. 42: Yeung, M. C., Y., L. A. K., and Chan, C. K. (2009). Phase Transition and Hygroscopic Properties of Internally Mixed Ammonium Sulfate and Adipic Acid (AS-AA) Particles by Optical Microscopic Imaging and Raman Spectroscopy. Aerosol Sci. Technol. 43: Zappoli, S., Andracchio, A., Fuzzi, S., Facchini, M. C., Gelencser, A., Kiss, G., Krivacsy, Z., Molnar, A., Meszaros, E., Hansson, H. C., Rosman, K., and Zebuhr, Y. (1999). Inorganic, Organic and Macromolecular Components of Fine Aerosol in Different Areas of Europe in Relation to Their Water Solubility, Atmo. Env. 33: Zardini, A. A., Sjogren, S., Marcolli, C., Krieger, U. K., Gysel, M., Weingartner, E., Baltensperger, U., and Peter, T. (2008). A Combined Particle Trap/HTDMA Hygroscopicity Study of Mixed Inorganic/Organic Aerosol Particles. Atmo. Chem. Phys. 8: Zhang, Y. H., and Chan, C. K. (2002). Understanding the Hygroscopic Properties of Supersaturated Droplets of Metal and Ammonium Sulfate Solutions Using Raman Spectroscopy. J. Phy. Chem. A 106:

Hygroscopic growth of ammonium sulfate/dicarboxylic acids

Hygroscopic growth of ammonium sulfate/dicarboxylic acids JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 108, NO. D20, 4638, doi:10.1029/2003jd003775, 2003 Hygroscopic growth of ammonium sulfate/dicarboxylic acids Matthew E. Wise, Jason D. Surratt, Daniel B. Curtis, John

More information

Hygroscopicity of Inorganic Aerosols: Size and Relative Humidity Effects on the Growth Factor

Hygroscopicity of Inorganic Aerosols: Size and Relative Humidity Effects on the Growth Factor Aerosol and Air Quality Research, 10: 255 264, 2010 Copyright Taiwan Association for Aerosol Research ISSN: 1680-8584 print / 2071-1409 online doi: 10.4209/aaqr.2009.12.0076 Hygroscopicity of Inorganic

More information

Phase transitions and hygroscopic growth of aerosol particles containing humic acid and mixtures of humic acid and ammonium sulphate

Phase transitions and hygroscopic growth of aerosol particles containing humic acid and mixtures of humic acid and ammonium sulphate Atmos. Chem. Phys., 6, 755 768, 2006 Author(s) 2006. This work is licensed under a Creative Commons License. Atmospheric Chemistry and Physics Phase transitions and hygroscopic growth of aerosol particles

More information

Title of file for HTML: Supplementary Information Description: Supplementary Figures, Supplementary Tables and Supplementary References

Title of file for HTML: Supplementary Information Description: Supplementary Figures, Supplementary Tables and Supplementary References Title of file for HTML: Supplementary Information Description: Supplementary Figures, Supplementary Tables and Supplementary References Title of file for HTML: Peer Review File Description: g e (RH) (bulk)

More information

Aerosol chemistry and climate: Laboratory studies of the carbonate component of mineral dust and its reaction products

Aerosol chemistry and climate: Laboratory studies of the carbonate component of mineral dust and its reaction products GEOPHYSICAL RESEARCH LETTERS, VOL. 33, L13811, doi:10.1029/2006gl026386, 2006 Aerosol chemistry and climate: Laboratory studies of the carbonate component of mineral dust and its reaction products Elizabeth

More information

Ammonium Bisulfate/Water Equilibrium and Metastability Phase Diagrams

Ammonium Bisulfate/Water Equilibrium and Metastability Phase Diagrams J. Phys. Chem. A 1997, 101, 4191-4195 4191 Ammonium Bisulfate/Water Equilibrium and Metastability Phase Diagrams Dan G. Imre,*, Jun Xu, I. N. Tang, and R. McGraw EnVironmental Chemistry DiVision, Department

More information

Water activity and activation diameters from hygroscopicity data - Part II: Application to organic species

Water activity and activation diameters from hygroscopicity data - Part II: Application to organic species Water activity and activation diameters from hygroscopicity data - Part II: Application to organic species K. A. Koehler, S. M. Kreidenweis, P. J. Demott, A. J. Prenni, C. M. Carrico, B. Ervens, G. Feingold

More information

The effect of surface tension (Kelvin effect) on the equilibrium radius of a hygroscopic aqueous aerosol particle

The effect of surface tension (Kelvin effect) on the equilibrium radius of a hygroscopic aqueous aerosol particle Aerosol Science 37 (006) 1605 1617 www.elsevier.com/locate/jaerosci The effect of surface tension (Kelvin effect) on the equilibrium radius of a hygroscopic aqueous aerosol particle Ernie R. Lewis Atmospheric

More information

Determination of Water Activity in Ammonium Sulfate and Sulfuric Acid Mixtures Using Levitated Single Particles

Determination of Water Activity in Ammonium Sulfate and Sulfuric Acid Mixtures Using Levitated Single Particles Aerosol Science and Technology ISSN: 0278-6826 (Print) 1521-7388 (Online) Journal homepage: http://www.tandfonline.com/loi/uast20 Determination of Water Activity in Ammonium Sulfate and Sulfuric Acid Mixtures

More information

Influence of Organic-Containing Aerosols on Marine Boundary Layer Processes

Influence of Organic-Containing Aerosols on Marine Boundary Layer Processes DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited. Influence of Organic-Containing Aerosols on Marine Boundary Layer Processes John H. Seinfeld California Institute of Technology,

More information

A curved multi-component aerosol hygroscopicity model framework: Part 2 Including organic compounds

A curved multi-component aerosol hygroscopicity model framework: Part 2 Including organic compounds Atmos. Chem. Phys., 5, 1223 1242, 2005 SRef-ID: 1680-7324/acp/2005-5-1223 European Geosciences Union Atmospheric Chemistry and Physics A curved multi-component aerosol hygroscopicity model framework: Part

More information

Chapter 5 Conclusions and Future Studies

Chapter 5 Conclusions and Future Studies 177 Chapter 5 Conclusions and Future Studies 178 Conclusions and Future Studies The results of the studies presented in this thesis confirm that ambient and laboratory-generated aerosols exhibit complex

More information

A novel model to predict the physical state of atmospheric H 2 SO 4 /NH 3 /H 2 O aerosol particles

A novel model to predict the physical state of atmospheric H 2 SO 4 /NH 3 /H 2 O aerosol particles Atmos. Chem. Phys., 3, 909 924, 2003 Atmospheric Chemistry and Physics A novel model to predict the physical state of atmospheric H 2 SO 4 /NH 3 /H 2 O aerosol particles C. A. Colberg, B. P. Luo, H. Wernli,

More information

Ammonium Sulfate: Equilibrium and Metastability Phase Diagrams from 40 to -50 C

Ammonium Sulfate: Equilibrium and Metastability Phase Diagrams from 40 to -50 C 7462 J. Phys. Chem. B 1998, 102, 7462-7469 Ammonium Sulfate: Equilibrium and Metastability Phase Diagrams from 40 to -50 C Jun Xu, Dan Imre,* Robert McGraw, and Ignatius Tang BrookhaVen National Laboratory,

More information

Hygroscopic growth and water uptake kinetics of two-phase aerosol particles consisting of ammonium sulfate, adipic and humic acid mixtures

Hygroscopic growth and water uptake kinetics of two-phase aerosol particles consisting of ammonium sulfate, adipic and humic acid mixtures Aerosol Science 38 (2007) 157 171 www.elsevier.com/locate/jaerosci Hygroscopic growth and water uptake kinetics of two-phase aerosol particles consisting of ammonium sulfate, adipic and humic acid mixtures

More information

Hygroscopic Growth of Aerosols and their Optical Properties

Hygroscopic Growth of Aerosols and their Optical Properties Hygroscopic Growth of Aerosols and their Optical Properties Cynthia Randles Atmospheric & Oceanic Sciences Princeton University V. Ramaswamy and L. M. Russell ! Introduction Presentation Overview! Aerosol

More information

Highly Biased Hygroscopicity Derived from Size-Resolved Cloud Condensation Nuclei Activation Ratios without Data Inversion

Highly Biased Hygroscopicity Derived from Size-Resolved Cloud Condensation Nuclei Activation Ratios without Data Inversion ATMOSPHERIC AND OCEANIC SCIENCE LETTERS, 2014, VOL. 7, NO. 3, 254 259 Highly Biased Hygroscopicity Derived from Size-Resolved Cloud Condensation Nuclei Activation Ratios without Data Inversion DENG Zhao-Ze

More information

Size Distribution and Hygroscopic Properties of Agricultural Aerosols

Size Distribution and Hygroscopic Properties of Agricultural Aerosols Size Distribution and Hygroscopic Properties of Agricultural Aerosols Naruki Hiranuma 1, Sarah D. Brooks 1, Brent W. Auvermann 2, Rick Littleton 3 1 Department of Atmospheric Sciences, Texas A&M University.

More information

Parameterization of the nitric acid effect on CCN activation

Parameterization of the nitric acid effect on CCN activation Atmos. Chem. Phys., 5, 879 885, 25 SRef-ID: 168-7324/acp/25-5-879 European Geosciences Union Atmospheric Chemistry and Physics Parameterization of the nitric acid effect on CCN activation S. Romakkaniemi,

More information

Chapter 4 Hygroscopicity Measurements of Atmospherically Relevant Organic Aerosol Species *

Chapter 4 Hygroscopicity Measurements of Atmospherically Relevant Organic Aerosol Species * 109 Chapter 4 Hygroscopicity Measurements of Atmospherically Relevant Organic Aerosol Species * * This chapter is prepared for journal submission as Hygroscopicity Measurements of Atmospherically Relevant

More information

CHAPTER 8. AEROSOLS 8.1 SOURCES AND SINKS OF AEROSOLS

CHAPTER 8. AEROSOLS 8.1 SOURCES AND SINKS OF AEROSOLS 1 CHAPTER 8 AEROSOLS Aerosols in the atmosphere have several important environmental effects They are a respiratory health hazard at the high concentrations found in urban environments They scatter and

More information

Updated H 2 SO 4 -H 2 O binary homogeneous nucleation look-up tables

Updated H 2 SO 4 -H 2 O binary homogeneous nucleation look-up tables Click Here for Full Article JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 113,, doi:10.1029/2008jd010527, 2008 Updated H 2 SO 4 -H 2 O binary homogeneous nucleation look-up tables Fangqun Yu 1 Received 2 June

More information

Supplement of Multiphase oxidation of SO 2 by NO 2 on CaCO 3 particles

Supplement of Multiphase oxidation of SO 2 by NO 2 on CaCO 3 particles Supplement of Atmos. Chem. Phys., 18, 2481 2493, 2018 https://doi.org/10.5194/acp-18-2481-2018-supplement Author(s) 2018. This work is distributed under the Creative Commons Attribution 4.0 License. Supplement

More information

Water content of ambient aerosol during the Pittsburgh Air Quality Study

Water content of ambient aerosol during the Pittsburgh Air Quality Study JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 110,, doi:10.1029/2004jd004651, 2005 Water content of ambient aerosol during the Pittsburgh Air Quality Study Andrey Khlystov Department of Civil and Environmental

More information

Application of osmolality for the determination of water activity and the modelling of cloud formation

Application of osmolality for the determination of water activity and the modelling of cloud formation Atmos. Chem. Phys. Discuss., 4, 7667 7689, 04 www.atmos-chem-phys.org/acpd/4/7667/ SRef-ID: 1680-737/acpd/04-4-7667 European Geosciences Union Atmospheric Chemistry and Physics Discussions Application

More information

ASSESSMENT OF THE MIXING STATE AND CLOUD NUCLEATING EFFICIENCY OF ASIAN AEROSOLS USING AIRCRAFT-BASED MEASUREMENTS OF HYGROSCOPICITY.

ASSESSMENT OF THE MIXING STATE AND CLOUD NUCLEATING EFFICIENCY OF ASIAN AEROSOLS USING AIRCRAFT-BASED MEASUREMENTS OF HYGROSCOPICITY. ASSESSMENT OF THE MIXING STATE AND CLOUD NUCLEATING EFFICIENCY OF ASIAN AEROSOLS USING AIRCRAFT-BASED MEASUREMENTS OF HYGROSCOPICITY A Thesis by TIMOTHY WILLIAM THOMAS Submitted to the Office of Graduate

More information

A novel tandem differential mobility analyzer with organic vapor treatment of aerosol particles

A novel tandem differential mobility analyzer with organic vapor treatment of aerosol particles Atmospheric Chemistry and Physics A novel tandem differential mobility analyzer with organic vapor treatment of aerosol particles J. Joutsensaari 1, P. Vaattovaara 1, M. Vesterinen 1, K. Hämeri 2, and

More information

Response: Changes in the manuscript: Response

Response: Changes in the manuscript: Response We would like to thank the referee for providing valuable comments on our manuscript and we have carefully addressed the referee s comments point-by-point as follows (referee s comments in black and our

More information

Cloud processing, cloud evaporation and Angström exponent

Cloud processing, cloud evaporation and Angström exponent Atmos. Chem. Phys., 9, 71 80, 2009 Author(s) 2009. This work is distributed under the Creative Commons Attribution 3.0 License. Atmospheric Chemistry and Physics Cloud processing, cloud evaporation and

More information

A cloud microphysics model including trace gas condensation and sulfate chemistry

A cloud microphysics model including trace gas condensation and sulfate chemistry BOREAL ENVIRONMENT RESEARCH 8: 43 424 ISSN 239-695 Helsinki December 23 23 A cloud microphysics model including trace gas condensation and sulfate chemistry Harri Kokkola ), Sami Romakkaniemi ), Markku

More information

CCN activation experiments with adipic acid: effect of particle phase and adipic acid coatings on soluble and insoluble particles

CCN activation experiments with adipic acid: effect of particle phase and adipic acid coatings on soluble and insoluble particles Atmos. Chem. Phys., 8, 3735 3748, 2008 Author(s) 2008. This work is distributed under the Creative Commons Attribution 3.0 License. Atmospheric Chemistry and Physics CCN activation experiments with adipic

More information

Chasing Aerosol Particles Down to Nano Sizes

Chasing Aerosol Particles Down to Nano Sizes Chasing Aerosol Particles Down to Nano Sizes ERC Seminar 13 June 2013 Armin Sorooshian Chemical & Environmental Engineering Atmospheric Sciences University of Arizona Outline of Talk 1. What are aerosol

More information

Water adsorption on ammounium sulfate and silica nanoparticles. Keywords: nanoparticles, hygroscopic growth, water monolayers INTRODUCTION

Water adsorption on ammounium sulfate and silica nanoparticles. Keywords: nanoparticles, hygroscopic growth, water monolayers INTRODUCTION Water adsorption on ammounium sulfate and silica nanoparticles Keskinen Helmi 1, Jaatinen Antti 1, Miettinen Pasi 1, Romakkaniemi Sami 1, Joutsensaari Jorma 1, Smith James N. 1, and Laaksonen Ari 1,3 1

More information

Measured and modeled equilibrium sizes of NaCl and (NH 4 ) 2 SO 4 particles at relative humidities up to 99.1%

Measured and modeled equilibrium sizes of NaCl and (NH 4 ) 2 SO 4 particles at relative humidities up to 99.1% JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 110,, doi:10.1029/2004jd005507, 2005 Measured and modeled equilibrium sizes of NaCl and (NH 4 ) 2 SO 4 particles at relative humidities up to 99.1% H. Wex, A. Kiselev,

More information

Phase Transformations of the Ternary System (NH 4 ) 2 SO 4 - H 2 SO 4 -H 2 O and the Implications for Cirrus Cloud Formation

Phase Transformations of the Ternary System (NH 4 ) 2 SO 4 - H 2 SO 4 -H 2 O and the Implications for Cirrus Cloud Formation Phase Transformations of the Ternary System (NH 4 ) 2 SO 4 - H 2 SO 4 -H 2 O and the Implications for Cirrus Cloud Formation Scot T. Martin Department of Environmental Sciences and Engineering, The University

More information

Organic aerosol formation via sulphate cluster activation

Organic aerosol formation via sulphate cluster activation JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 109,, doi:10.1029/2003jd003961, 2004 Organic aerosol formation via sulphate cluster activation Markku Kulmala, 1 Veli-Matti Kerminen, 2 Tatu Anttila, 1,2 Ari Laaksonen,

More information

Helsinki, Finland. 1 Aerodyne Research Inc., Billerica, MA, USA. 2 Chemistry Department, Boston College, Chestnut Hill, MA, USA

Helsinki, Finland. 1 Aerodyne Research Inc., Billerica, MA, USA. 2 Chemistry Department, Boston College, Chestnut Hill, MA, USA Supplementary material to article: Relationship between aerosol oxidation level and hygroscopic properties of laboratory generated secondary organic aerosol (SOA) particles (paper #0GL0 to Geophysical

More information

Abstract. 1 Introduction

Abstract. 1 Introduction Measuring and modelling of aerosol chemical composition for the SANA intensive field campaigns W. Seidl, G. Brunnemann, L. Kins, D. Kohler, E. Kohler, K. ReiBwig, K. RouB, Th. Seller, R. Dugli Meteorologisches

More information

Inferring thermodynamic properties from CCN activation experiments: single-component and binary aerosols

Inferring thermodynamic properties from CCN activation experiments: single-component and binary aerosols Atmos. Chem. Phys., 7, 5263 5274, 2007 Author(s) 2007. This work is licensed under a Creative Commons License. Atmospheric Chemistry and Physics Inferring thermodynamic properties from CCN activation experiments:

More information

Aerosol-Cloud-Radiation Interactions in Atmospheric Forecast Models

Aerosol-Cloud-Radiation Interactions in Atmospheric Forecast Models Aerosol-Cloud-Radiation Interactions in Atmospheric Forecast Models John H. Seinfeld, Principal Investigator California Institute of Technology 1200 E. California Blvd., M/C 210-41 Pasadena, CA 91125 (626)

More information

Jianfei Peng et al. Correspondence to: Jianfei Peng Min Hu and Renyi Zhang

Jianfei Peng et al. Correspondence to: Jianfei Peng Min Hu and Renyi Zhang Supplement of Atmos. Chem. Phys., 17, 10333 10348, 2017 https://doi.org/10.5194/acp-17-10333-2017-supplement Author(s) 2017. This work is distributed under the Creative Commons Attribution 3.0 License.

More information

Atmospheric Environment

Atmospheric Environment Atmospheric Environment 50 (2012) 97e102 Contents lists available at SciVerse ScienceDirect Atmospheric Environment journal homepage: www.elsevier.com/locate/atmosenv Synergistic effect in the humidifying

More information

Multiple scattering of light by water cloud droplets with external and internal mixing of black carbon aerosols

Multiple scattering of light by water cloud droplets with external and internal mixing of black carbon aerosols Chin. Phys. B Vol. 21, No. 5 (212) 5424 Multiple scattering of light by water cloud droplets with external and internal mixing of black carbon aerosols Wang Hai-Hua( 王海华 ) and Sun Xian-Ming( 孙贤明 ) School

More information

Infrared extinction spectroscopy and Raman microspectroscopy of selected components of. mineral dust with organic compounds.

Infrared extinction spectroscopy and Raman microspectroscopy of selected components of. mineral dust with organic compounds. Infrared extinction spectroscopy and Raman microspectroscopy of selected components of mineral dust with organic compounds. 1. Introduction Mineral dust is one of the major constituents of particulate

More information

The Pennsylvania State University. The Graduate School. Eberly College of Science HYSTERESIS AND HISTORY EFFECTS OF ORGANIC AEROSOL PARTICLES

The Pennsylvania State University. The Graduate School. Eberly College of Science HYSTERESIS AND HISTORY EFFECTS OF ORGANIC AEROSOL PARTICLES The Pennsylvania State University The Graduate School Eberly College of Science HYSTERESIS AND HISTORY EFFECTS OF ORGANIC AEROSOL PARTICLES CONTAINING PHENYLGLYOXYLIC ACID AND 3,4- DIMETHOXYPHENYLACETIC

More information

The Atmospheric Chemistry and Physics of Ammonia

The Atmospheric Chemistry and Physics of Ammonia The Atmospheric Chemistry and Physics of Ammonia Russell Dickerson Dept. Meteorology, The University of Maryland Presented at the National Atmospheric Deposition Program Ammonia Workshop October 23, 2003

More information

3) Big Bend s Aerosol and Extinction Budgets during BRAVO

3) Big Bend s Aerosol and Extinction Budgets during BRAVO 3) Big Bend s Aerosol and Extinction Budgets during BRAVO 3.1 Introduction The primary goal of the BRAVO study was to apportion the major aerosol species to their emission sources, with the secondary goals

More information

Organic acids as cloud condensation nuclei: Laboratory studies of highly soluble and insoluble species

Organic acids as cloud condensation nuclei: Laboratory studies of highly soluble and insoluble species Atmos. Chem. Phys., 3, 59 52, 23 www.atmos-chem-phys.org/acp/3/59/ Atmospheric Chemistry and Physics Organic acids as cloud condensation nuclei: Laboratory studies of highly soluble and insoluble species

More information

Ice nucleation in sulfuric acid and ammonium sulfate particles Anthony J. Prenni, Matthew E. Wise, Sarah D. Brooks, and Margaret A.

Ice nucleation in sulfuric acid and ammonium sulfate particles Anthony J. Prenni, Matthew E. Wise, Sarah D. Brooks, and Margaret A. JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 106, NO. D3, PAGES 3037-3044, FEBRUARY 16, 2001 Ice nucleation in sulfuric acid and ammonium sulfate particles Anthony J. Prenni, Matthew E. Wise, Sarah D. Brooks,

More information

Role of molecular size in cloud droplet activation

Role of molecular size in cloud droplet activation GEOPHYSICAL RESEARCH LETTERS, VOL. 36, L22801, doi:10.1029/2009gl040131, 2009 Role of molecular size in cloud droplet activation M. D. Petters, 1,2 S. M. Kreidenweis, 1 A. J. Prenni, 1 R. C. Sullivan,

More information

Study of water activities of supersaturated aerosols

Study of water activities of supersaturated aerosols JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 105, NO. D9, PAGES 11,699-11,709, MAY 16, 2000 Study of water activities of supersaturated aerosols of sodium and ammonium salts Zhanyao Ha, Lee Choy, and Chak Keung

More information

In situ determination of atmospheric aerosol composition as a function of hygroscopic growth

In situ determination of atmospheric aerosol composition as a function of hygroscopic growth JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 113,, doi:10.1029/2008jd009954, 2008 In situ determination of atmospheric aerosol composition as a function of hygroscopic growth Hanna Herich, 1 Lukas Kammermann,

More information

The Importance of Adsorption for CCN Activity and Hygroscopic Properties of Mineral Dust Aerosol

The Importance of Adsorption for CCN Activity and Hygroscopic Properties of Mineral Dust Aerosol 1 2 The Importance of Adsorption for CCN Activity and Hygroscopic Properties of Mineral Dust Aerosol 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Prashant Kumar 1, Athanasios Nenes 1,2, and

More information

Chemical Closure Study on Hygroscopic Properties of Urban Aerosol Particles in Sapporo, Japan

Chemical Closure Study on Hygroscopic Properties of Urban Aerosol Particles in Sapporo, Japan Environ. Sci. Technol. 2007, 41, 6920-6925 Chemical Closure Study on Hygroscopic Properties of Urban Aerosol Particles in Sapporo, Japan SHANKAR GOPALA AGGARWAL,*, MICHIHIRO MOCHIDA,, YUYUKI KITAMORI,

More information

Determination of the deliquescence point in salt mixtures and in in-situ multicomponent salts with DVS equipment

Determination of the deliquescence point in salt mixtures and in in-situ multicomponent salts with DVS equipment SWBSS2014 3 rd International Conference on Salt Weathering of Buildings and Stone Sculptures 14-16 October 2014 Determination of the deliquescence point in salt mixtures and in in-situ multicomponent salts

More information

Sensitivity of cloud condensation nuclei activation processes to kinetic parameters

Sensitivity of cloud condensation nuclei activation processes to kinetic parameters JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 111,, doi:10.1029/2005jd006529, 2006 Sensitivity of cloud condensation nuclei activation processes to kinetic parameters P. Y. Chuang 1 Received 25 July 2005; revised

More information

Relative humidity impact on aerosol parameters in a Paris suburban area

Relative humidity impact on aerosol parameters in a Paris suburban area Relative humidity impact on aerosol parameters in a Paris suburban area H. Randriamiarisoa, P. Chazette, P. Couvert, J. Sanak, G. Mégie To cite this version: H. Randriamiarisoa, P. Chazette, P. Couvert,

More information

An adsorption model of insoluble particle activation: Application to black carbon

An adsorption model of insoluble particle activation: Application to black carbon Click Here for Full Article JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 112,, doi:10.1029/2007jd008549, 2007 An adsorption model of insoluble particle activation: Application to black carbon B. F. Henson 1 Received

More information

Chapter Eight: Conclusions and Future Work

Chapter Eight: Conclusions and Future Work 2004 PhD Thesis 202 Chapter Eight: Conclusions and Future Work 8.1 Conclusions The Aerodyne aerosol mass spectrometer is capable of providing quantitative information on the chemical composition of the

More information

Investigation of the hygroscopic properties of Ca(NO 3 ) 2 and internally mixed Ca(NO 3 ) 2 /CaCO 3 particles by micro-raman spectrometry

Investigation of the hygroscopic properties of Ca(NO 3 ) 2 and internally mixed Ca(NO 3 ) 2 /CaCO 3 particles by micro-raman spectrometry Author(s) 2008. This work is distributed under the Creative Commons Attribution.0 License. Atmospheric Chemistry and Physics Investigation of the hygroscopic properties of Ca(NO ) 2 and internally mixed

More information

Hygroscopic behavior of atmospheric aerosols containing nitrates and water-soluble organic acids

Hygroscopic behavior of atmospheric aerosols containing nitrates and water-soluble organic acids Atmos. Chem. Phys. Discuss., https://doi.org/0./acp-0-00 Discussion started: November 0 c Author(s) 0. CC BY.0 License. Hygroscopic behavior of atmospheric aerosols containing nitrates and water-soluble

More information

Lecture 7: quick review

Lecture 7: quick review Lecture 7: quick review We discussed the meaning of the critical r* and ΔG*: since it s unstable, if we can form a drop with r > r*, the system will keep going falling down the energy curve, trying to

More information

Comparison of AERONET inverted size distributions to measured distributions from the Aerodyne Aerosol Mass Spectrometer

Comparison of AERONET inverted size distributions to measured distributions from the Aerodyne Aerosol Mass Spectrometer Comparison of inverted size distributions to measured distributions from the Aerodyne Aerosol Mass Spectrometer Peter DeCarlo Remote Sensing Project April 28, 23 Introduction The comparison of direct in-situ

More information

The Assessment of Aviation Cloudiness in IPCC Climate Change The Physical Science Basis

The Assessment of Aviation Cloudiness in IPCC Climate Change The Physical Science Basis The Assessment of Aviation Cloudiness in IPCC Climate Change 2007 - The Physical Science Basis I. Introduction II. IPCC Science Assessment III. Aviation cloudiness - linear contrails - contrail (induced)

More information

Hygroscopic growth and activation of HULIS particles: experimental data and a new iterative parameterization scheme for complex aerosol particles

Hygroscopic growth and activation of HULIS particles: experimental data and a new iterative parameterization scheme for complex aerosol particles Atmos. Chem. Phys., 8, 1855 1866, 2008 Author(s) 2008. This work is distributed under the Creative Commons Attribution 3.0 License. Atmospheric Chemistry and Physics Hygroscopic growth and activation of

More information

A comprehensive study of hygroscopic properties of calcium- and magnesium-

A comprehensive study of hygroscopic properties of calcium- and magnesium- 1 2 A comprehensive study of hygroscopic properties of calcium- and magnesium- containing salts: implication for hygroscopicity of mineral dust and sea salt aerosols 3 4 5 6 Liya Guo, 1,5,a Wenjun Gu,

More information

JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 112, D24S13, doi: /2007jd008424, 2007

JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 112, D24S13, doi: /2007jd008424, 2007 JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 112,, doi:10.1029/2007jd008424, 2007 A phase equilibrium model for atmospheric aerosols containing inorganic electrolytes and organic compounds (UHAERO), with application

More information

P = x i. P i. = y i. Aerosol and Aqueous Chemistry. Raoult s Law. Raoult s Law vs. Henry s Law. or C i. = HC i. = k H

P = x i. P i. = y i. Aerosol and Aqueous Chemistry. Raoult s Law. Raoult s Law vs. Henry s Law. or C i. = HC i. = k H The Great Smog Aerosol and Aqueous Chemistry Equilibrium Partitioning Oxidation and Oxidants Other Surface-driven Fogs in London were a common occurrence, but the events that began on the 5th of December

More information

Kinetics of Deliquescence of Ammonium Sulfate Particles

Kinetics of Deliquescence of Ammonium Sulfate Particles Kinetics of Deliquescence of Ammonium Sulfate Particles By Rocsana Gabriela Pancescu A thesis presented to the University of Waterloo in fulfillment of the thesis requirement for the degree of Doctor of

More information

Aerosol hygroscopicity at high (99 to 100%) relative humidities

Aerosol hygroscopicity at high (99 to 100%) relative humidities Atmos. Chem. Phys., 10, 139 1344, 010 www.atmos-chem-phys.net/10/139/010/ Author(s) 010. This work is distributed under the Creative Commons Attribution 3.0 License. Atmospheric Chemistry and Physics Aerosol

More information

Depositional ice nucleation onto crystalline hydrated NaCl particles: a new mechanism for ice formation in the troposphere

Depositional ice nucleation onto crystalline hydrated NaCl particles: a new mechanism for ice formation in the troposphere 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 Depositional ice nucleation onto crystalline hydrated NaCl particles: a new mechanism for ice formation in the troposphere Matthew E. Wise 1,2, Kelly J. Baustian

More information

In situ DRIFTS study of hygroscopic behavior of mineral aerosol

In situ DRIFTS study of hygroscopic behavior of mineral aerosol Journal of Environmental Sciences 2010, 22(4) 555 560 In situ DRIFTS study of hygroscopic behavior of mineral aerosol Qingxin Ma, Hong He, Yongchun Liu State Key Laboratory of Environmental Chemistry and

More information

Uptake of HNO 3 to deliquescent sea-salt particles: a study using the short-lived radioactive isotope tracer 13 N

Uptake of HNO 3 to deliquescent sea-salt particles: a study using the short-lived radioactive isotope tracer 13 N Atmospheric Chemistry and Physics Uptake of HNO 3 to deliquescent sea-salt particles: a study using the short-lived radioactive isotope tracer 3 N C. Guimbaud, F. Arens, L. Gutzwiller, H. W. Gäggeler,2,

More information

Cloud Condensation Nuclei Hygroscopic Parameter Kappa

Cloud Condensation Nuclei Hygroscopic Parameter Kappa Cloud Condensation Nuclei Hygroscopic Parameter Kappa Covers Reading Material in Chapter 17.5 Atmospheric Sciences 5200 Physical Meteorology III: Cloud Physics Cloud Condensation Nuclei (CCN) Form a cloud

More information

Application of IR Raman Spectroscopy

Application of IR Raman Spectroscopy Application of IR Raman Spectroscopy 3 IR regions Structure and Functional Group Absorption IR Reflection IR Photoacoustic IR IR Emission Micro 10-1 Mid-IR Mid-IR absorption Samples Placed in cell (salt)

More information

APPLICATION OF KOHLER THEORY: MODELING CLOUD CONDENSATION NUCLEI ACTIVITY

APPLICATION OF KOHLER THEORY: MODELING CLOUD CONDENSATION NUCLEI ACTIVITY 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 APPLICATION OF KOHLER THEORY: MODELING CLOUD CONDENSATION NUCLEI ACTIVITY Gavin Cornwell, Katherine Nadler, Alex Nguyen, and Steven Schill Department of

More information

CHEMICAL IDENTIFICATION OF SEMI-URBAN AEROSOLS BY LASER RAMAN SPECTROSCOPY

CHEMICAL IDENTIFICATION OF SEMI-URBAN AEROSOLS BY LASER RAMAN SPECTROSCOPY Global NEST Journal, Vol 8, No 3, pp 260-264, 2006 Copyright 2006 Global NEST Printed in Greece. All rights reserved CHEMICAL IDENTIFICATION OF SEMI-URBAN AEROSOLS BY LASER RAMAN SPECTROSCOPY V.M. HARPALE

More information

Atmospheric Chemistry and Physics

Atmospheric Chemistry and Physics Atmos. Chem. Phys., 0, 5625 5639, 200 www.atmos-chem-phys.net/0/5625/200/ doi:0.594/acp-0-5625-200 Author(s) 200. CC Attribution 3.0 License. Atmospheric Chemistry and Physics Hygroscopic properties of

More information

Chapter 2 Aerosol Mass Transfer

Chapter 2 Aerosol Mass Transfer Chapter 2 Aerosol Mass Transfer The size distribution of aerosol particles has a significant impact on their chemical and physical properties, including their optical properties and ability to act as cloud

More information

Hygroscopic Behavior of NaCl-Bearing Natural Aerosol Particles Using Environmental Transmission Electron Microscopy

Hygroscopic Behavior of NaCl-Bearing Natural Aerosol Particles Using Environmental Transmission Electron Microscopy Concordia University - Portland CU Commons Faculty Research Math & Science Department 5-26-2007 Hygroscopic Behavior of NaCl-Bearing Natural Aerosol Particles Using Environmental Transmission Electron

More information

Oxalic acid as a heterogeneous ice nucleus in the upper troposphere and its indirect aerosol effect

Oxalic acid as a heterogeneous ice nucleus in the upper troposphere and its indirect aerosol effect Atmos. Chem. Phys., 6, 3115 3129, 2006 Author(s) 2006. This work is licensed under a Creative Commons License. Atmospheric Chemistry and Physics Oxalic acid as a heterogeneous ice nucleus in the upper

More information

Implications of Sulfate Aerosols on Clouds, Precipitation and Hydrological Cycle

Implications of Sulfate Aerosols on Clouds, Precipitation and Hydrological Cycle Implications of Sulfate Aerosols on Clouds, Precipitation and Hydrological Cycle Source: Sulfate aerosols are produced by chemical reactions in the atmosphere from gaseous precursors (with the exception

More information

Infrared spectroscopic study of the low-temperature phase behavior of ammonium sulfate

Infrared spectroscopic study of the low-temperature phase behavior of ammonium sulfate JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 107, NO. D10, 4088, 10.1029/2001JD000677, 2002 Infrared spectroscopic study of the low-temperature phase behavior of ammonium sulfate Tara J. Fortin, John E. Shilling,

More information

Organic Component Vapor Pressures and Hygroscopicities of Aqueous Aerosol Measured by Optical Tweezers

Organic Component Vapor Pressures and Hygroscopicities of Aqueous Aerosol Measured by Optical Tweezers This is an open access article published under an ACS AuthorChoice License, which permits copying and redistribution of the article or any adaptations for non-commercial purposes. pubs.acs.org/jpca Downloaded

More information

Cloud condensation nucleus (CCN) behavior of organic aerosol particles generated by atomization of water and methanol solutions

Cloud condensation nucleus (CCN) behavior of organic aerosol particles generated by atomization of water and methanol solutions Atmos. Chem. Phys., 7, 2949 2971, 2007 Author(s) 2007. This work is licensed under a Creative Commons License. Atmospheric Chemistry and Physics Cloud condensation nucleus (CCN) behavior of organic aerosol

More information

The Effect of Kelvin Effect on the Equilibrium Effective Radii and Hygroscopic Growth of Atmospheric Aerosols

The Effect of Kelvin Effect on the Equilibrium Effective Radii and Hygroscopic Growth of Atmospheric Aerosols The Effect of Kelvin Effect on the Equilibrium Effective Radii and Hygroscopic Growth of Atmospheric Aerosols B.I. Tijjani 1 G.S.M. Galadanci 1 A.I. Abubakar 2 F. S. Koki 1 I. D. Adamu 1 A. M. Nura 1 M.

More information

Evidence that Nitric Acid Increases Relative Humidity in Low-Temperature Cirrus

Evidence that Nitric Acid Increases Relative Humidity in Low-Temperature Cirrus Supporting Online Material for: Evidence that Nitric Acid Increases Relative Humidity in Low-Temperature Cirrus Clouds R. S. Gao, P. J. Popp, D. W. Fahey, T. P. Marcy, R. L. Herman, E. M. Weinstock, D.

More information

Parameterization of cloud droplet activation using a simplified treatment of the aerosol number size distribution

Parameterization of cloud droplet activation using a simplified treatment of the aerosol number size distribution JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 113,, doi:10.1029/2007jd009485, 2008 Parameterization of cloud droplet activation using a simplified treatment of the aerosol number size distribution Niku Kivekäs,

More information

Physio-chemical and Optical Characterization of Anthropogenic and Natural Aerosol: Implications for Assessing Global Effects

Physio-chemical and Optical Characterization of Anthropogenic and Natural Aerosol: Implications for Assessing Global Effects Physio-chemical and Optical Characterization of Anthropogenic and Natural Aerosol: Implications for Assessing Global Effects GLOBE Pollution Southern Japan TRACE-P, 2001 Dust Antony Clarke, University

More information

Lab 4 Major Anions In Atmospheric Aerosol Particles

Lab 4 Major Anions In Atmospheric Aerosol Particles Georgia Institute of Technology School of Earth and Atmospheric Sciences EAS 4641 Spring 2008 Lab 4 Major Anions In Atmospheric Aerosol Particles Purpose of Lab 4: This experiment will involve determining

More information

Ice nucleation in sulfuric acid/organic aerosols: implications for cirrus cloud formation

Ice nucleation in sulfuric acid/organic aerosols: implications for cirrus cloud formation Author(s) 2006. This work is licensed under a Creative Commons License. Atmospheric Chemistry and Physics Ice nucleation in sulfuric acid/organic aerosols: implications for cirrus cloud formation M. R.

More information

Studies of the uptake of gaseous ethyl-3-ethoxy propionate onto ammonium sulfate and ammonium nitrate aerosol particles

Studies of the uptake of gaseous ethyl-3-ethoxy propionate onto ammonium sulfate and ammonium nitrate aerosol particles Air Pollution XIII 519 Studies of the uptake of gaseous ethyl-3-ethoxy propionate onto ammonium sulfate and ammonium nitrate aerosol particles K. D. Stewart & J. M. Andino Department of Environmental Engineering

More information

Influence of Organic-Containing Aerosols on Marine Boundary Layer Processes

Influence of Organic-Containing Aerosols on Marine Boundary Layer Processes DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited. Influence of Organic-Containing Aerosols on Marine Boundary Layer Processes John H. Seinfeld California Institute of Technology

More information

Boston College. The Graduate School of Arts and Sciences. Department of Chemistry CHEMICAL KINETICS AND MICROPHYSICS OF ATMOSPHERIC AEROSOLS

Boston College. The Graduate School of Arts and Sciences. Department of Chemistry CHEMICAL KINETICS AND MICROPHYSICS OF ATMOSPHERIC AEROSOLS Boston College The Graduate School of Arts and Sciences Department of Chemistry CHEMICAL KINETICS AND MICROPHYSICS OF ATMOSPHERIC AEROSOLS a dissertation by JAMES WALTER MORRIS submitted in partial fulfillment

More information

REQUEST FOR A SPECIAL PROJECT

REQUEST FOR A SPECIAL PROJECT REQUEST FOR A SPECIAL PROJECT 2010 2012 MEMBER STATE: Switzerland Principal Investigator 1 : Affiliation: Prof. Ulrike Lohmann Institute for Atmospheric and Climate Science, ETH Zurich Address: Universitaetstrasse

More information

Deliquescence and Efflorescence Processes of Aerosol. Particles Studied by Molecular Spectroscopy

Deliquescence and Efflorescence Processes of Aerosol. Particles Studied by Molecular Spectroscopy Deliquescence and Efflorescence Processes of Aerosol Particles Studied by Molecular Spectroscopy Li-Jun Zhao 1,2, Feng Wang 1, Kun Zhang 1, Qing-Xuan Zeng 2, Yun-Hong Zhang 1* 1 The Institute of Chemical

More information

Aerosol Basics: Definitions, size distributions, structure

Aerosol Basics: Definitions, size distributions, structure Aerosol Basics: Definitions, size distributions, structure Antti Lauri NetFAM Summer School Zelenogorsk, 9 July 2008 Department of Physics, Division of Atmospheric Sciences and Geophysics, University of

More information

Volatility of Organic Aerosol: Evaporation of Ammonium Sulfate/ Succinic Acid Aqueous Solution Droplets

Volatility of Organic Aerosol: Evaporation of Ammonium Sulfate/ Succinic Acid Aqueous Solution Droplets pubs.acs.org/est Terms of Use Downloaded via 148.251.232.83 on December 29, 2018 at 13:19:31 (UTC). See https://pubs.acs.org/sharingguidelines for options on how to legitimately share published articles.

More information

Supplementary Figures

Supplementary Figures 1 Supplementary Figures 2 3 4 5 6 7 Supplementary Figure 1. Schematic of the experimental setup. Juelich Plant Atmosphere Chamber (JPAC) is shown. SMPS: scanning mobility particle sizer; CPC: condensation

More information

Phys Biomedical Physics: Yong-qing Li, PhD. Department of Physics, East Carolina University Greenville, NC 27858, USA.

Phys Biomedical Physics: Yong-qing Li, PhD. Department of Physics, East Carolina University Greenville, NC 27858, USA. Phys 6715 - Biomedical Physics: Optical Trapping in Air Yong-qing Li, PhD Department of Physics, East Carolina University Greenville, NC 27858, USA Email: liy@ecu.edu 1 Outline 1. Why optical trapping

More information