# Recognizing Dew as an Indicator and an Improver of Near-Surface Air Quality

Authors: Yingying Xu; Xinyue Zhu
Journal: Advances in Meteorology
 (2017)

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## Abstract

The relationship between dew and airborne particles is important in urban ecosystems, but the capability of dew to remove airborne particles remains unclear. During 2015 in Changchun, China, 74 dew and particle samples were collected simultaneously to investigate their chemical characteristics under normal, fog, and haze conditions. Analyses included measuring total dissolved solids, total suspended particulates, PM2.5 and PM10 concentrations, major cations (NH4+, Na+, K+, Ca2+, and Mg2+), major anions (F−, Cl−, SO42-, and NO3-), and organic and elemental carbon. Results showed that air quality deteriorated during haze but improved in fog. The particle size distributions, major cations, and carbonaceous species documented in the dew and airborne particles demonstrated consistent synchronous patterns with values descending in the order haze > normal > fog conditions. We found that dew is a good indicator of near-surface air quality. Specifically, its water-soluble ions and carbonaceous species could be used to distinguish emission sources and to identify the presence of secondary organic carbon. Dew is more effective at removing airborne particles in normal weather than in haze or fog conditions; PM2.5 removal rates were 21.5%, 15.2%, and 13.7% on normal, foggy, and hazy days, respectively. Dew condensation processes reduce concentrations of gaseous and particulate pollutants in the near-surface layer.


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## Body

## 1. Introduction

Dew condensation is a common meteorological phenomenon. Because of urban surface hardening and the heat island effect, not only is the frequency of dew occurrence in urban ecosystems high, but also the condensation quantity is large [1, 2]. The dew condensation process represents effective natural atmospheric purification [3, 4]. Airborne particles can be captured as condensation nuclei as dew condenses, whereas gases or liquid particles might dissolve into the dewdrops [5]. Thus, dew formation can actually help purify urban air [3], and dew is recognized as the sink of nighttime moisture and near-surface particulate matter (e.g., PM2.5 and PM10) [6]. The concentrations of both particulate matter and ions in dew are higher than in rain samples [1, 7]. The sedimentation of airborne particles is linked to both wet deposition (rain, snow, fog, and dew) and dry sedimentation processes (gravity settling), although the former is the primary pathway via which pollutants are removed from the atmosphere [8]. Huo et al. [9] and Hu et al. [10] concluded that rain is most efficient at removing particles and gases from the atmosphere. However, the difficulties associated with dew collection have resulted in little research on near-surface airborne particle removal by dew [11]. Dew condensation is concentrated within the layer 0–3 m above the ground surface [6, 12]. Near-surface airborne particulate matter, particularly PM2.5 and PM10, has direct and strong influence on human health [13]. However, although dew is an important pathway of wet deposition in the sphere of human activity, it remains unclear how much atmospheric particulate matter might be removed by dew.Following China’s rapid urbanization, motor vehicle exhaust emissions, industrial waste gases, and coal combustion have created increasing levels of urban air pollution [14]. The associated higher concentrations of particulate matter, which lead to increased occurrences of foggy and hazy weather under conditions of high relative humidity (RH) and temperature inversion, have become problematic [15–17]. On hazy days, the concentrations of water-soluble ions in dew have been found to be 3.01–9.32 times higher than on normal days. The mean concentrations of PM2.5 and PM10 have been reported as 21.69 and 51.56 mg/L, respectively, on normal days, that is, over 2.48 and 1.79 times higher than on hazy days, respectively [18]. Thus, water vapor condensation is clearly involved in the settling of airborne particles [19], making dew condensation an effective method of their sedimentation and removal. However, a relationship between dew and airborne particle concentrations, that is, one that reflects the chemical transformation of atmospheric pollutants in condensation processes under various conditions, has yet to be established. The objectives of this study were to analyze the chemical characteristics of dew and airborne particles under normal, foggy, and hazy conditions; to discuss the relationship between particles and dew; and to identify the particle removal capability of dew under different weather conditions. The intentions were to identify changes in the chemical compositions of the dew and the airborne particles under these various conditions and to reveal the contribution of dew to the removal of near-surface airborne particles.


## 2. Materials and Methods

### 2.1. Sampling Site

Dew and airborne particle samples were collected at Jilin Jianzhu University, located in the southeastern part of Changchun in Jilin Province, China. The continental monsoon climate of the area produces average annual temperatures that vary from −15°C in January to 25°C in August. Precipitation that falls mostly as rain is within the range of 522–615 mm/a. Changchun has four distinct seasons that are characterized by freezing weather in winter, relatively strong winds in spring, and highRH, an obvious diurnal temperature difference, and low wind speed (<2 m/s) in summer and fall. The synergistic atmospheric conditions of a seasonal temperature inversion and airborne pollutants caused by the burning of corn, straw, or fossil fuels mean Changchun historically suffers hazy conditions in autumn. To investigate the nature of this haze, samples of dew and aerosols were collected during the peak haze period of summer and fall (May–November) in 2015.


### 2.2. Sample Collection

#### 2.2.1. Dew

Dew samples collected using different collection surfaces can vary substantially [11]; however, a polytetrafluoroethylene (PTFE) surface is generally considered appropriate for dew collection [20]. In this study, dew was collected in clean 250 mL PTFE bottles placed (approximately 1.0 m above ground level) within the green belt along a campus road. This site is affected by residential, traffic, and construction emissions considered representative of Changchun. All dew samples were collected before sunrise on nonrainy days to avoid any effects on particle concentrations associated with rain.


#### 2.2.2. Airborne Particles

Airborne particle samples were collected simultaneously with the dew samples. Thus, the sampling time was equivalent to the dew condensation period, that is, between 18:00 and 06:00 local time. Samples were collected at approximately 1.0 m above ground level, next to the dew collector. Particles were collected onto Whatman quartz filters (QMA 1851-047), using medium-volume samplers and a flow rate of 100 L/min. After sampling, the filters were placed into polyethylene plastic bags and stored in a refrigerator.


### 2.3. Sample Analysis

#### 2.3.1. Ion Analysis

All dew water samples were filtered through 0.45μm membrane filters and stored at approximately 4°C for further chemical analysis. Major soluble cations (Ca2+, Mg2+, Na+, K+, and NH4+) and anions (F−, Cl−, NO3-, and SO42-) were analyzed using an ion chromatograph (LC-20AD, Shimadzu, Japan). Specifically, a Shim-pack IC-C1 column, with 5 mmol HNO3 as eluent and a 1.3 mL/min flow rate, was used to analyze 20 μL of each sample for cations. Similarly, a Shim-pack IC-A3 column, with 8.0 mmolp-hydroxybenzoic acid (PHBA), 3.2 mmol Bis-Tris, and 50 mmol boric acid as eluent and a 1.5 mL/min flow rate, was used to analyze 50 μL of each sample for anions [18].Airborne particles collected on the filters were submerged in 20 mL of ultrapure water, sealed, and ultrasonicated for approximately 120 min to extract soluble ions. Subsequently, the same steps as described above for dew samples were undertaken to determine the soluble ion content.


#### 2.3.2. Carbonaceous Species

The total carbon (TC) and elemental carbon (EC) quantities on each quartz filter were determined using an elemental analyzer (EA-1108 CHNS-O, Fisons, Italy). One-eighth of each filter sample was preheated at 340°C for 100 min to expel the organic carbon (OC) content; this subsample was fed into the elemental analyzer to obtain the EC content. The OC was determined by extracting the EC from the TC content.Particulate organic carbon (POC) and particulate elemental carbon (PEC) in all the dew samples were filtered through 0.45μm membrane filters to remove any particulate matter. This residue was then weighed after having been freeze-dried for 12 h. All subsequent steps were identical to the process described above for aerosol samples. The POC was determined by extracting the PEC from the particle total carbon (PTC) content.


#### 2.3.3. Particle Diameter Analysis

Particle diameters in dew were measured using a model JL-1166 Laser Particle Analyzer (JL-1166, Chengdu Jingxin Powder Analysis Instrument Co., Ltd., Chengdu, Sichuan, China).Particle diameters in dew were measured using an Aerosol Monitors Model (DUSTTRAK™ DRX 8533EP, USA).


#### 2.3.4. TDS, TSP, and PM Measurements

Data of total suspended particulate (TSP), PM2.5 (particulate matter diameter < 2.5 µm), and PM10 (particulate matter diameter 2.5–10 µm) in Changchun were collated from http://www.pm25.in/changchun.All collected dew samples were analyzed to determine the total dissolved solids (TDS), PM2.5, and PM10 using the subtraction method. The samples filtered through 10.00, 2.50, or 0.22 μm membrane filters were weighed and then dried for 12 h. After drying, the filters were reweighed and the TDS, PM2.5, and PM10 of the dew were calculated based on their differences.


### 2.4. Dew Intensity Monitoring

Dew is difficult to create artificially; therefore, the experiments were conducted in situ. Poplar wooden sticks were chosen as the monitoring material. The poplar wooden sticks were polished and cut to a size of 20 × 4 × 4 cm (length × width × height).An observation shelf was set up with three layers: a lower layer (5 cm above the ground surface), a middle layer (1.5 m above the ground surface), and an upper layer (3 m above the ground surface). The middle and upper monitors mainly estimated the dew formed by condensation of atmospheric water vapor, and the lower monitor mainly estimated dew formed from water vapor rising from the surface of the ground. The monitors were weighed daily at sunset and sunrise with an electronic balance (accuracy: ±0.001 g). For each height, three monitors were set up 30 min after sunset. These monitors were gathered 30 min before sunrise and reweighed. The actual dew per unit area for each plot was computed as the average of the three heights. The monitors were left in the experiment plot during the day to prevent excessive drying and to eliminate the effects of moisture absorption on measurement accuracy.


### 2.5. Data Analysis

Statistical analyses were conducted using SPSS software version 16.0 (IBM Corp., NY, USA). Quantile-Quantile Probability Plots were used to test the normality of the meteorological data, particle removal efficiency by dew, and particle concentrations in dew and air on foggy, normal, and hazy days. Values all accorded with a normal distribution, and the average data could be used to describe the results of the analysis. Wind speed, RH, PM2.5, and PM10 data were subjected to a one-way analysis of variance with a significance threshold ofp < 0.05. Either the Least Significance Difference method or Tamhane’s T2 procedure was used to determine the differences among the meteorological data.The equations of particle removal efficiency by dew are as follows:(1)Ri%=QidewQiair×100%,where i is the type of PM (i=1 represents PM2.5, i=2 represents PM10, and i=3 represents TSP), R is the particle removal efficiency by dew, Qidew is the weight of particles after sunset in the dew (mg), and Qiair is the weight of particles in the air during the condensation time (mg);(2)Qidew=I×Ci×V3,where I is the dew intensity (mm), Ci is the concentration of particles in the dew (mg/L), V is the air inflow during dew condensation (m3), and 3 is the hypothetical dew condensation concentrated 0–3 m above the ground surface;(3)I=10×Wmr-WmsS,where Wmr is the weight of each monitor in the different layers before sunrise (g), Wms is the weight of each monitor in the different layers after sunset (g), S is the surface area of the monitor (cm2), and 10 is a conversion factor;(4)Qiair=Wfir-Wfis,where Wfir is the weight of the filter before sunrise (g) and Wfis is the weight of the filter after sunset (g).


### 2.6. Classification of Normal, Foggy, and Hazy Conditions

Normal, foggy, and hazy weather were defined based on the RH and visibility during the study period. Normal days had visibility of >10 km. Hazy days had visibility of <10 km and RH of <90%. Foggy days had visibility of <10 km but with RH of >90%. Using these criteria, airborne particles and dew samples were collected on 17 normal, 13 hazy, and 7 foggy days.The meteorological parameters for these three weather conditions are shown in Table1. Haze and fog were characterized by low visibility and a high Air Quality Index (AQI). Fog had high humidity and low wind speed, while haze was associated with stable moist air. Aside from the RH and visibility, the main meteorological parameter that differed between foggy and normal weather was wind speed (p < 0.01), while temperature (p < 0.01) distinguished hazy and normal days. The burning of coal and straw for heating is the principal cause of haze in Changchun. Therefore, haze usually occurs in fall or winter under low temperature conditions. This results in concentrations of PM2.5 and PM10 in haze that are significantly higher than on normal days (p < 0.01).Table 1
Average meteorological parameters and particle concentrations during normal, fog, and haze conditions during the study period.
Normal
Fog
Haze
AQI
87
71
272
PM2.5 (μg/m3)
32
33
230
PM10 (μg/m3)
68
52
292
RH (%)
75.27
92.12
81.25
Wind speed (m/s)
0.66
0.12
0.24
Visibility (km)
12.48
5.36
3.58
Pressure (kPa)
101.5
101.3
101.1
Dew point (°C)
19.0
18.5
4.1
Temperature (°C)
17.52
15.26
6.28
Note. AQI: Air Quality Index; PM2.5: particulate matter < 2.5 µm in diameter; PM10: particulate matter 2.5–10 µm in diameter.


### 2.7. Meteorological Data

Daily meteorological data, including air temperature (°C), dew point (°C), RH (%), wind speed (m/s) at 10 m height, and water vapor pressure (hPa), were measured at hourly intervals during the condensation period using a Milos 520 automatic weather station (Vaisala, Finland) at Jilin University. Visibility data were collated fromhttp://www.wunderground.com. Data for PM2.5 and PM10 in Changchun were collated from http://www.pm25.in/changchun.


## 2.1. Sampling Site

Dew and airborne particle samples were collected at Jilin Jianzhu University, located in the southeastern part of Changchun in Jilin Province, China. The continental monsoon climate of the area produces average annual temperatures that vary from −15°C in January to 25°C in August. Precipitation that falls mostly as rain is within the range of 522–615 mm/a. Changchun has four distinct seasons that are characterized by freezing weather in winter, relatively strong winds in spring, and highRH, an obvious diurnal temperature difference, and low wind speed (<2 m/s) in summer and fall. The synergistic atmospheric conditions of a seasonal temperature inversion and airborne pollutants caused by the burning of corn, straw, or fossil fuels mean Changchun historically suffers hazy conditions in autumn. To investigate the nature of this haze, samples of dew and aerosols were collected during the peak haze period of summer and fall (May–November) in 2015.


## 2.2. Sample Collection

### 2.2.1. Dew

Dew samples collected using different collection surfaces can vary substantially [11]; however, a polytetrafluoroethylene (PTFE) surface is generally considered appropriate for dew collection [20]. In this study, dew was collected in clean 250 mL PTFE bottles placed (approximately 1.0 m above ground level) within the green belt along a campus road. This site is affected by residential, traffic, and construction emissions considered representative of Changchun. All dew samples were collected before sunrise on nonrainy days to avoid any effects on particle concentrations associated with rain.


### 2.2.2. Airborne Particles

Airborne particle samples were collected simultaneously with the dew samples. Thus, the sampling time was equivalent to the dew condensation period, that is, between 18:00 and 06:00 local time. Samples were collected at approximately 1.0 m above ground level, next to the dew collector. Particles were collected onto Whatman quartz filters (QMA 1851-047), using medium-volume samplers and a flow rate of 100 L/min. After sampling, the filters were placed into polyethylene plastic bags and stored in a refrigerator.


## 2.2.1. Dew

Dew samples collected using different collection surfaces can vary substantially [11]; however, a polytetrafluoroethylene (PTFE) surface is generally considered appropriate for dew collection [20]. In this study, dew was collected in clean 250 mL PTFE bottles placed (approximately 1.0 m above ground level) within the green belt along a campus road. This site is affected by residential, traffic, and construction emissions considered representative of Changchun. All dew samples were collected before sunrise on nonrainy days to avoid any effects on particle concentrations associated with rain.


## 2.2.2. Airborne Particles

Airborne particle samples were collected simultaneously with the dew samples. Thus, the sampling time was equivalent to the dew condensation period, that is, between 18:00 and 06:00 local time. Samples were collected at approximately 1.0 m above ground level, next to the dew collector. Particles were collected onto Whatman quartz filters (QMA 1851-047), using medium-volume samplers and a flow rate of 100 L/min. After sampling, the filters were placed into polyethylene plastic bags and stored in a refrigerator.


## 2.3. Sample Analysis

### 2.3.1. Ion Analysis

All dew water samples were filtered through 0.45μm membrane filters and stored at approximately 4°C for further chemical analysis. Major soluble cations (Ca2+, Mg2+, Na+, K+, and NH4+) and anions (F−, Cl−, NO3-, and SO42-) were analyzed using an ion chromatograph (LC-20AD, Shimadzu, Japan). Specifically, a Shim-pack IC-C1 column, with 5 mmol HNO3 as eluent and a 1.3 mL/min flow rate, was used to analyze 20 μL of each sample for cations. Similarly, a Shim-pack IC-A3 column, with 8.0 mmolp-hydroxybenzoic acid (PHBA), 3.2 mmol Bis-Tris, and 50 mmol boric acid as eluent and a 1.5 mL/min flow rate, was used to analyze 50 μL of each sample for anions [18].Airborne particles collected on the filters were submerged in 20 mL of ultrapure water, sealed, and ultrasonicated for approximately 120 min to extract soluble ions. Subsequently, the same steps as described above for dew samples were undertaken to determine the soluble ion content.


### 2.3.2. Carbonaceous Species

The total carbon (TC) and elemental carbon (EC) quantities on each quartz filter were determined using an elemental analyzer (EA-1108 CHNS-O, Fisons, Italy). One-eighth of each filter sample was preheated at 340°C for 100 min to expel the organic carbon (OC) content; this subsample was fed into the elemental analyzer to obtain the EC content. The OC was determined by extracting the EC from the TC content.Particulate organic carbon (POC) and particulate elemental carbon (PEC) in all the dew samples were filtered through 0.45μm membrane filters to remove any particulate matter. This residue was then weighed after having been freeze-dried for 12 h. All subsequent steps were identical to the process described above for aerosol samples. The POC was determined by extracting the PEC from the particle total carbon (PTC) content.


### 2.3.3. Particle Diameter Analysis

Particle diameters in dew were measured using a model JL-1166 Laser Particle Analyzer (JL-1166, Chengdu Jingxin Powder Analysis Instrument Co., Ltd., Chengdu, Sichuan, China).Particle diameters in dew were measured using an Aerosol Monitors Model (DUSTTRAK™ DRX 8533EP, USA).


### 2.3.4. TDS, TSP, and PM Measurements

Data of total suspended particulate (TSP), PM2.5 (particulate matter diameter < 2.5 µm), and PM10 (particulate matter diameter 2.5–10 µm) in Changchun were collated from http://www.pm25.in/changchun.All collected dew samples were analyzed to determine the total dissolved solids (TDS), PM2.5, and PM10 using the subtraction method. The samples filtered through 10.00, 2.50, or 0.22 μm membrane filters were weighed and then dried for 12 h. After drying, the filters were reweighed and the TDS, PM2.5, and PM10 of the dew were calculated based on their differences.


## 2.3.1. Ion Analysis

All dew water samples were filtered through 0.45μm membrane filters and stored at approximately 4°C for further chemical analysis. Major soluble cations (Ca2+, Mg2+, Na+, K+, and NH4+) and anions (F−, Cl−, NO3-, and SO42-) were analyzed using an ion chromatograph (LC-20AD, Shimadzu, Japan). Specifically, a Shim-pack IC-C1 column, with 5 mmol HNO3 as eluent and a 1.3 mL/min flow rate, was used to analyze 20 μL of each sample for cations. Similarly, a Shim-pack IC-A3 column, with 8.0 mmolp-hydroxybenzoic acid (PHBA), 3.2 mmol Bis-Tris, and 50 mmol boric acid as eluent and a 1.5 mL/min flow rate, was used to analyze 50 μL of each sample for anions [18].Airborne particles collected on the filters were submerged in 20 mL of ultrapure water, sealed, and ultrasonicated for approximately 120 min to extract soluble ions. Subsequently, the same steps as described above for dew samples were undertaken to determine the soluble ion content.


## 2.3.2. Carbonaceous Species

The total carbon (TC) and elemental carbon (EC) quantities on each quartz filter were determined using an elemental analyzer (EA-1108 CHNS-O, Fisons, Italy). One-eighth of each filter sample was preheated at 340°C for 100 min to expel the organic carbon (OC) content; this subsample was fed into the elemental analyzer to obtain the EC content. The OC was determined by extracting the EC from the TC content.Particulate organic carbon (POC) and particulate elemental carbon (PEC) in all the dew samples were filtered through 0.45μm membrane filters to remove any particulate matter. This residue was then weighed after having been freeze-dried for 12 h. All subsequent steps were identical to the process described above for aerosol samples. The POC was determined by extracting the PEC from the particle total carbon (PTC) content.


## 2.3.3. Particle Diameter Analysis

Particle diameters in dew were measured using a model JL-1166 Laser Particle Analyzer (JL-1166, Chengdu Jingxin Powder Analysis Instrument Co., Ltd., Chengdu, Sichuan, China).Particle diameters in dew were measured using an Aerosol Monitors Model (DUSTTRAK™ DRX 8533EP, USA).


## 2.3.4. TDS, TSP, and PM Measurements

Data of total suspended particulate (TSP), PM2.5 (particulate matter diameter < 2.5 µm), and PM10 (particulate matter diameter 2.5–10 µm) in Changchun were collated from http://www.pm25.in/changchun.All collected dew samples were analyzed to determine the total dissolved solids (TDS), PM2.5, and PM10 using the subtraction method. The samples filtered through 10.00, 2.50, or 0.22 μm membrane filters were weighed and then dried for 12 h. After drying, the filters were reweighed and the TDS, PM2.5, and PM10 of the dew were calculated based on their differences.


## 2.4. Dew Intensity Monitoring

Dew is difficult to create artificially; therefore, the experiments were conducted in situ. Poplar wooden sticks were chosen as the monitoring material. The poplar wooden sticks were polished and cut to a size of 20 × 4 × 4 cm (length × width × height).An observation shelf was set up with three layers: a lower layer (5 cm above the ground surface), a middle layer (1.5 m above the ground surface), and an upper layer (3 m above the ground surface). The middle and upper monitors mainly estimated the dew formed by condensation of atmospheric water vapor, and the lower monitor mainly estimated dew formed from water vapor rising from the surface of the ground. The monitors were weighed daily at sunset and sunrise with an electronic balance (accuracy: ±0.001 g). For each height, three monitors were set up 30 min after sunset. These monitors were gathered 30 min before sunrise and reweighed. The actual dew per unit area for each plot was computed as the average of the three heights. The monitors were left in the experiment plot during the day to prevent excessive drying and to eliminate the effects of moisture absorption on measurement accuracy.


## 2.5. Data Analysis

Statistical analyses were conducted using SPSS software version 16.0 (IBM Corp., NY, USA). Quantile-Quantile Probability Plots were used to test the normality of the meteorological data, particle removal efficiency by dew, and particle concentrations in dew and air on foggy, normal, and hazy days. Values all accorded with a normal distribution, and the average data could be used to describe the results of the analysis. Wind speed, RH, PM2.5, and PM10 data were subjected to a one-way analysis of variance with a significance threshold ofp < 0.05. Either the Least Significance Difference method or Tamhane’s T2 procedure was used to determine the differences among the meteorological data.The equations of particle removal efficiency by dew are as follows:(1)Ri%=QidewQiair×100%,where i is the type of PM (i=1 represents PM2.5, i=2 represents PM10, and i=3 represents TSP), R is the particle removal efficiency by dew, Qidew is the weight of particles after sunset in the dew (mg), and Qiair is the weight of particles in the air during the condensation time (mg);(2)Qidew=I×Ci×V3,where I is the dew intensity (mm), Ci is the concentration of particles in the dew (mg/L), V is the air inflow during dew condensation (m3), and 3 is the hypothetical dew condensation concentrated 0–3 m above the ground surface;(3)I=10×Wmr-WmsS,where Wmr is the weight of each monitor in the different layers before sunrise (g), Wms is the weight of each monitor in the different layers after sunset (g), S is the surface area of the monitor (cm2), and 10 is a conversion factor;(4)Qiair=Wfir-Wfis,where Wfir is the weight of the filter before sunrise (g) and Wfis is the weight of the filter after sunset (g).


## 2.6. Classification of Normal, Foggy, and Hazy Conditions

Normal, foggy, and hazy weather were defined based on the RH and visibility during the study period. Normal days had visibility of >10 km. Hazy days had visibility of <10 km and RH of <90%. Foggy days had visibility of <10 km but with RH of >90%. Using these criteria, airborne particles and dew samples were collected on 17 normal, 13 hazy, and 7 foggy days.The meteorological parameters for these three weather conditions are shown in Table1. Haze and fog were characterized by low visibility and a high Air Quality Index (AQI). Fog had high humidity and low wind speed, while haze was associated with stable moist air. Aside from the RH and visibility, the main meteorological parameter that differed between foggy and normal weather was wind speed (p < 0.01), while temperature (p < 0.01) distinguished hazy and normal days. The burning of coal and straw for heating is the principal cause of haze in Changchun. Therefore, haze usually occurs in fall or winter under low temperature conditions. This results in concentrations of PM2.5 and PM10 in haze that are significantly higher than on normal days (p < 0.01).Table 1
Average meteorological parameters and particle concentrations during normal, fog, and haze conditions during the study period.
Normal
Fog
Haze
AQI
87
71
272
PM2.5 (μg/m3)
32
33
230
PM10 (μg/m3)
68
52
292
RH (%)
75.27
92.12
81.25
Wind speed (m/s)
0.66
0.12
0.24
Visibility (km)
12.48
5.36
3.58
Pressure (kPa)
101.5
101.3
101.1
Dew point (°C)
19.0
18.5
4.1
Temperature (°C)
17.52
15.26
6.28
Note. AQI: Air Quality Index; PM2.5: particulate matter < 2.5 µm in diameter; PM10: particulate matter 2.5–10 µm in diameter.


## 2.7. Meteorological Data

Daily meteorological data, including air temperature (°C), dew point (°C), RH (%), wind speed (m/s) at 10 m height, and water vapor pressure (hPa), were measured at hourly intervals during the condensation period using a Milos 520 automatic weather station (Vaisala, Finland) at Jilin University. Visibility data were collated fromhttp://www.wunderground.com. Data for PM2.5 and PM10 in Changchun were collated from http://www.pm25.in/changchun.


## 3. Results and Discussion

### 3.1. Particulate Matter

Under normal conditions, in this study, most airborne particles comprised PM20–PM50 (diameter: 20–50 µm), accounting for 28.32% of the total particulate mass (Figure 1). Meanwhile, the proportions of PM2.5, PM10, and >PM10 were 11.83%, 25.69%, and 62.48%, respectively. Thus, coarse particles >PM10 formed the dominant fraction of the particulate matter. In fog, the particle size distributions changed little with proportions of PM2.5, PM10, and >PM10 established as 12.78%, 27.23%, and 59.99%, respectively. Because fog usually occurred after rainfall, air quality on such days was generally good. Thus, the coarse particle fraction PM20–PM50 declined under fog from normal levels (28.32%) to 18.58%. Air pollution is most serious during haze because of the much higher concentrations of fine particulate matter. In haze, the proportions of PM2.5 and PM10 increased from normal levels to 19.35% and 31.10%, respectively, while the proportion of >PM10 declined to 49.55%.Figure 1
Frequency size distributions of air particles and dew in normal, hazy, and foggy conditions in Changchun, China.Because airborne particles near the surface act as condensation nuclei for dew, the particle size distributions for both dew and airborne particles were concordant (Figure1). Under normal weather conditions, dew preferentially removed coarse airborne particles, resulting in a proportion of >PM10 of 67.14%. Particle size distributions in dew associated with foggy and normal weather were identical; however, during hazy weather, the fine particulate fraction in dew was clearly enhanced, increasing from 32.86% under normal weather conditions to 46.78% in haze. Removal of coarse airborne particles by dew is clearly a dominant process under normal, foggy, and hazy weather (Table 2).Table 2
Summary of removal efficiency (%) of total dissolved solids (TDS), PM2.5, and PM10 by dew in Changchun during the study period.
Normal (n = 17)
Fog (n = 7)
Haze (n = 13)
TDS
PM2.5
PM10
TDS
PM2.5
PM10
TDS
PM2.5
PM10
Mean ± SD
28.2
±
3.6
21.5
±
3.8
25.9
±
2.5
23.7
±
3.1
15.2
±
3.5
18.1
±
4.1
18.5
±
3.9
13.7
±
1.1
15.7
±
1.2
Max.
32.3
25.9
28.5
27.4
19.5
25.4
24.1
14.5
18.4
Min.
17.5
18.7
19.5
18.4
10.5
14.1
15.2
11.8
12.7As shown in Table3, the mass concentrations of TSP, PM2.5, and PM10 in the atmosphere were 165.24, 40.22, and 72.34 μg/m3 on normal days. In contrast, the mass concentrations of TSP, PM2.5, and PM10 deceased 0.66–0.75 times in fog. Such decreases reflect the better air quality under fog conditions. In contrast, a reduction in air quality was obvious in hazy weather with mass concentrations of TSP, PM2.5, and PM10 having values 2.78–4.29 times those of normal weather. Mean concentrations of TDS, PM2.5, and PM10 in dew were all higher in haze compared with normal days, reflecting the higher total dissolved ions in dew produced on hazy days. Table 2 shows that dew can effectively remove airborne particles. In normal weather, the removal rates of TSP, PM10, and PM2.5 by dew were 28.2%, 25.9%, and 21.5%, respectively. In foggy and hazy weather, the capability of dew to remove airborne particles decreased significantly, especially in haze. The removal rates of TSP, PM10, and PM2.5 by dew decreased to 18.5%, 15.7%, and 13.7% under haze. Hazy and foggy weather limit the airborne particle removal capability of dew condensation.Table 3
Summary of total dissolved solids (TDS), PM2.5, and PM10 of dew, as well as total suspended particulates (TSP), PM2.5, and PM10 of air particles under normal (n = 17), fog (n = 7), and haze (n = 13) conditions in Changchun during the study period.
Dew (mg/L)
Air (µg/m3)
Normal (n = 17)
Fog (n = 7)
Haze (n = 13)
Normal (n = 17)
Fog (n = 7)
Haze (n = 13)
TDS
PM2.5
PM10
TDS
PM2.5
PM10
TDS
PM2.5
PM10
TSP
PM2.5
PM10
TSP
PM2.5
PM10
TSP
PM2.5
PM10
Mean ± SD
175 ± 31.54
24.39 ± 8.57
49.65 ± 12.86
95.28 ± 26.12
12.26 ± 5.32
31.65 ± 5.28
281.36 ± 29.86
61.22 ± 19.59
89.24 ± 29.19
165.24 ± 25.35
40.22 ± 8.25
72.34 ± 9.48
110.25 ± 20.24
29.85 ± 4.75
49.25 ± 7.42
458.67 ± 32.54
172.36 ± 21.26
205.31 ± 25.47
Max.
249.12
53.25
82.50
157.12
35.18
56.34
332.28
93.00
159.13
193.21
54.23
92.78
170.23
39.54
70.21
523.42
200.52
296.25
Min.
128.90
9.80
23.31
64.58
3.80
14.41
234.14
22.50
48.25
89.62
21.32
52.31
69.25
17.52
34.21
365.24
142.31
124.25
Note. PM2.5: particulate matter < 2.5 µm in diameter; PM10: particulate matter 2.5–10 µm in diameter; SD: standard deviation.Particle concentrations in dew were similar to those in the atmosphere under all conditions. Mass concentrations of TDS, PM2.5, and PM10 in dew were 175.31, 24.39, and 49.65 mg/L on normal days. Their values declined 0.50–0.63 times in fog but increased 1.60–2.54 times in haze. Therefore, the capability of dew to remove particulate matter appears to be diminished under fog and haze. This might reflect the more static meteorological conditions during fog and haze events, in which floating particles do not settle easily. Only a fraction of near-surface atmospheric particulate matter appeared to act as condensation nuclei, adsorbing water vapor. Under normal weather conditions, particles removed by dew include condensation nuclei and any airborne particles that would naturally undergo sedimentation.


### 3.2. Ionic Composition

Air quality obviously decreases during haze. Mass concentrations of PM2.5 and PM10 are typically 4–6 times higher during haze than on normal days [21] with almost all concentrations of water-soluble ions (NH4+, Mg2+, Ca2+, K+, Na+, Cl−, NO3-, F−, and SO42-) showing increases during haze events [22, 23]. In particular, the concentrations of K+ and other secondary aerosol indicators (NH4+, NO3-, and SO42-) increase markedly in haze [21, 23]. This study focused on air quality during haze events (Table 1), when haze formed more than 10 m above ground level [21, 24, 25]. We found that ion concentrations in both dew and particulate matter of the atmosphere were similar (Figure 2). In decreasing order of ionic concentration, airborne particles comprised SO42- > NO3- >NH4+ > Ca2+ > Cl− > Na+ > F− > K+ > Mg2. Although ion concentrations in fog were reduced, this order did not change. In contrast, during haze, ion concentrations increased and the decreasing order of ionic concentrations in airborne particles changed to SO42- > NO3- > NH4+ > Cl− > Ca2+ > K+ > F− > Na+ > Mg2+. Ions from anthropogenic pollution sources were the highest contributors to airborne particles in normal, foggy, and hazy weather. In particular, Cl− from coal and K+ from biomass burning were most enhanced in haze events. In dew, the decreasing order of ionic concentrations under normal and foggy conditions was SO42- > NH4+ > Ca2+ > NO3- > Cl− > Na+ > F− > K+ > Mg2+. In addition to the finding that all ion concentrations in dew during hazy weather were enhanced considerably, their order was also changed to SO42- > NH4+ > Ca2+ >NO3- > K+ > Cl− > F−> Na+ > Mg2+.Figure 2
Ionic concentrations ofNH4+, Mg2+, Ca2+, K+, Na+, Cl−, NO3-, F−, and SO42- of air particles and dew under normal (white), foggy (green), and hazy (red) conditions in Changchun, China.At the study site, ammonia (NH3) constituted an important alkaline gas in the atmosphere. The secondary aerosol was NO3-, which results from the transformations of various precursors of NOx [22]. The concentration of NH4+ was higher than NO3- in dew but not in airborne particles. Furthermore, NH4+ showed strong correlations with SO42- and [SO42- + NO3-] (p<0.01) in both dew and particle samples. The slopes of the regression equations between NH4+ and [SO42- + NO3-] and NH4+ and SO42- in dew were both smaller than unity (0.76 and 0.85), indicating incomplete neutralization of acidic species (HNO3 and H2SO4) by ammonia during the study period. This suggests the dominance of (NH4)2SO4 and NH4HSO4 [26] in the urban atmosphere. Thus, excess ammonia could combine with chloride and oxalate to form NH4Cl and (NH4)2CO3. Diurnal variability was observed for gaseous NH3 in the surface layer, and its concentration was higher than NO2 during periods of dew condensation [27]. Meanwhile, the concentration of HNO3 was higher during daytime [28]. This suggests that NH3 is readily converted to NH4+ in dew at night. Otherwise, it is possible that NH3 is dissolved easily in an acidic environment, whereby acidic dew accelerates the conversion of NH3 to NH4+ [29]. These scenarios all result in higher NH3 concentrations in dew.All ionic species in both airborne particles and dew decreased in transitions from normal to foggy conditions, but they increased in transitions from normal to hazy conditions. The origins of Ca2+, Na+, and Mg2+ are mainly from crustal sources such as resuspended road dust, soil dust, and construction dust, while SO42-, NO3-, and NH4+ represent secondary pollution sources. Usually, F− and Cl− are derived from coal combustion, while K+ is derived from biomass burning. The concentration ratios for normal/foggy conditions in airborne particles and dew for the main cations and anions were 1.40 and 1.30 for NH4+, 1.50 and 1.32 for Ca2+, 1.60 and 1.44 for Na+, 2.04 and 1.53 for K+, 1.82 and 1.49 for Mg2+, 1.19 and 1.18 for SO42-, 1.37 and 1.28 for NO3-, 1.69 and 1.13 for Cl−, and 1.57 and 1.47 for F−.The effect of haze on ions from different sources in both airborne particles and dew was significantly different. Haze concentrations of crustal ions (Ca2+, Na+, and Mg2+) in airborne particles were 1.87–5.05 times the normal particle levels; however, in dew, they were 3.26–3.69 times the normal dew levels. Haze concentrations of anthropogenic pollution species (SO42-, NO3-, and NH4+) were 3.89–5.98 times the normal particle levels and 4.78–7.99 times the normal dew levels. Haze concentrations of indicator ions (F−, Cl−, and K+) of coal and biomass burning were 2.27–6.05 times the normal particle levels and 3.93–8.96 times the normal dew levels. Throughout the sampling period, K+ showed the largest variation in airborne particles or dew. Haze caused serious air pollution. Clearly, this pollution was attributable to species from pollution and biomass burning sources. The chemical composition of the dew closely reflected the air quality of the near-surface atmosphere. Our results suggest that analyzing the chemical characteristics of dew can provide a reference for the assessment of air pollution and air quality. In particular, water-soluble ions from different sources were enhanced in dew compared with airborne particles collected simultaneously. We also observed that, under conditions of deteriorating air quality, the capability of dew to remove airborne pollutants increased.Dew condensation clearly had a purification effect on the near-surface atmosphere. In the process of vapor condensation, some airborne particles acted as dew condensation nuclei, while acidic or alkaline gas and solid particles dissolved directly in the dew. For instance,SO3- and HSO32- were partially oxidized to SO42- on oxidant surfaces, yielding the transformation of SO2 gas to SO42- solid, as outlined below in the following reactions:(5)O2a+SO2g⟶SO32-a,(6)OH-a+SO2g⟶HSO32-a/2OH-a+SO2g⟶SO42-a+H2O,where (a) and (g) represent aerosol and gas phases, respectively.Additionally, SO2 can also be absorbed by water in a liquid-phase reaction:(7)SO2+H2O⟷SO2·H2O,(8)SO2·H2O⟷H++HSO3-,(9)HSO3-⟷H++SO32-,where italics are used to show ionic species.Thus,SO42- in dew could originate from either homogeneous or heterogeneous chemical transformations of SO2 and SO42-. We suggest that part of the SO42- fraction might come from particles formed from gas or from gas absorption on particle surfaces. Clearly, conversion of SO2 to SO42- was accelerated by dew condensation. We conclude that condensation processes reduce pollutant concentrations of both gases and particulates in the near-surface atmosphere.


### 3.3. Carbonaceous Species

During this study, the concentrations of carbonaceous species showed similar trends to water-soluble species with the greatest levels in descending order recorded in hazy > normal > foggy conditions. The concentrations of OC and EC in airborne particles and the POC and PEC in dew were the highest in haze and the lowest in fog (Figure3). The average daily concentrations in airborne particles from hazy, foggy, and normal conditions were 40.75, 10.10, and 14.52 μg/m3 for OC and 7.91, 2.82, and 3.84 μg/m3 for EC, respectively. These values were 70.96, 7.38, and 10.85 mg/L for POC and 13.43, 2.73, and 3.51 mg/L for PEC in dew, under hazy, foggy, and normal conditions, respectively.Figure 3
Ionic concentrations of organic carbon (OC) and elemental carbon (EC) of air particles, as well as particulate organic carbon (POC) and particulate elemental carbon (PEC) of dew during normal (white), foggy (green), and hazy (red) conditions in Changchun, China.A ratio of OC/EC > 2 was used to identify the presence of secondary organic carbon (SOC) [21]. The average OC/EC ratio (5.16) in haze was about 1.43 times higher than in fog (3.60) and 1.35 times higher than on normal weather days (3.80). These ratios show that SOC formation was most serious during haze. In this study, average OC/EC ratios were 3.10, 2.72, and 5.33 for normal, foggy, and hazy conditions, respectively. The changes in OC and EC in dew and airborne particles were consistent (Figure 3), suggesting that analysis of POC and PEC in dew could be used to identify the presence of SOC.It is noted not only that OC is emitted from coal combustion, vehicle exhausts, and biomass burning, but also that it accumulates rapidly on fine particulate matter via photochemical reactions. Under low wind speeds and high atmospheric pressure, stagnation contributes to the accumulation of OC in haze as pollutants accumulate and form secondary aerosols.


## 3.1. Particulate Matter

Under normal conditions, in this study, most airborne particles comprised PM20–PM50 (diameter: 20–50 µm), accounting for 28.32% of the total particulate mass (Figure 1). Meanwhile, the proportions of PM2.5, PM10, and >PM10 were 11.83%, 25.69%, and 62.48%, respectively. Thus, coarse particles >PM10 formed the dominant fraction of the particulate matter. In fog, the particle size distributions changed little with proportions of PM2.5, PM10, and >PM10 established as 12.78%, 27.23%, and 59.99%, respectively. Because fog usually occurred after rainfall, air quality on such days was generally good. Thus, the coarse particle fraction PM20–PM50 declined under fog from normal levels (28.32%) to 18.58%. Air pollution is most serious during haze because of the much higher concentrations of fine particulate matter. In haze, the proportions of PM2.5 and PM10 increased from normal levels to 19.35% and 31.10%, respectively, while the proportion of >PM10 declined to 49.55%.Figure 1
Frequency size distributions of air particles and dew in normal, hazy, and foggy conditions in Changchun, China.Because airborne particles near the surface act as condensation nuclei for dew, the particle size distributions for both dew and airborne particles were concordant (Figure1). Under normal weather conditions, dew preferentially removed coarse airborne particles, resulting in a proportion of >PM10 of 67.14%. Particle size distributions in dew associated with foggy and normal weather were identical; however, during hazy weather, the fine particulate fraction in dew was clearly enhanced, increasing from 32.86% under normal weather conditions to 46.78% in haze. Removal of coarse airborne particles by dew is clearly a dominant process under normal, foggy, and hazy weather (Table 2).Table 2
Summary of removal efficiency (%) of total dissolved solids (TDS), PM2.5, and PM10 by dew in Changchun during the study period.
Normal (n = 17)
Fog (n = 7)
Haze (n = 13)
TDS
PM2.5
PM10
TDS
PM2.5
PM10
TDS
PM2.5
PM10
Mean ± SD
28.2
±
3.6
21.5
±
3.8
25.9
±
2.5
23.7
±
3.1
15.2
±
3.5
18.1
±
4.1
18.5
±
3.9
13.7
±
1.1
15.7
±
1.2
Max.
32.3
25.9
28.5
27.4
19.5
25.4
24.1
14.5
18.4
Min.
17.5
18.7
19.5
18.4
10.5
14.1
15.2
11.8
12.7As shown in Table3, the mass concentrations of TSP, PM2.5, and PM10 in the atmosphere were 165.24, 40.22, and 72.34 μg/m3 on normal days. In contrast, the mass concentrations of TSP, PM2.5, and PM10 deceased 0.66–0.75 times in fog. Such decreases reflect the better air quality under fog conditions. In contrast, a reduction in air quality was obvious in hazy weather with mass concentrations of TSP, PM2.5, and PM10 having values 2.78–4.29 times those of normal weather. Mean concentrations of TDS, PM2.5, and PM10 in dew were all higher in haze compared with normal days, reflecting the higher total dissolved ions in dew produced on hazy days. Table 2 shows that dew can effectively remove airborne particles. In normal weather, the removal rates of TSP, PM10, and PM2.5 by dew were 28.2%, 25.9%, and 21.5%, respectively. In foggy and hazy weather, the capability of dew to remove airborne particles decreased significantly, especially in haze. The removal rates of TSP, PM10, and PM2.5 by dew decreased to 18.5%, 15.7%, and 13.7% under haze. Hazy and foggy weather limit the airborne particle removal capability of dew condensation.Table 3
Summary of total dissolved solids (TDS), PM2.5, and PM10 of dew, as well as total suspended particulates (TSP), PM2.5, and PM10 of air particles under normal (n = 17), fog (n = 7), and haze (n = 13) conditions in Changchun during the study period.
Dew (mg/L)
Air (µg/m3)
Normal (n = 17)
Fog (n = 7)
Haze (n = 13)
Normal (n = 17)
Fog (n = 7)
Haze (n = 13)
TDS
PM2.5
PM10
TDS
PM2.5
PM10
TDS
PM2.5
PM10
TSP
PM2.5
PM10
TSP
PM2.5
PM10
TSP
PM2.5
PM10
Mean ± SD
175 ± 31.54
24.39 ± 8.57
49.65 ± 12.86
95.28 ± 26.12
12.26 ± 5.32
31.65 ± 5.28
281.36 ± 29.86
61.22 ± 19.59
89.24 ± 29.19
165.24 ± 25.35
40.22 ± 8.25
72.34 ± 9.48
110.25 ± 20.24
29.85 ± 4.75
49.25 ± 7.42
458.67 ± 32.54
172.36 ± 21.26
205.31 ± 25.47
Max.
249.12
53.25
82.50
157.12
35.18
56.34
332.28
93.00
159.13
193.21
54.23
92.78
170.23
39.54
70.21
523.42
200.52
296.25
Min.
128.90
9.80
23.31
64.58
3.80
14.41
234.14
22.50
48.25
89.62
21.32
52.31
69.25
17.52
34.21
365.24
142.31
124.25
Note. PM2.5: particulate matter < 2.5 µm in diameter; PM10: particulate matter 2.5–10 µm in diameter; SD: standard deviation.Particle concentrations in dew were similar to those in the atmosphere under all conditions. Mass concentrations of TDS, PM2.5, and PM10 in dew were 175.31, 24.39, and 49.65 mg/L on normal days. Their values declined 0.50–0.63 times in fog but increased 1.60–2.54 times in haze. Therefore, the capability of dew to remove particulate matter appears to be diminished under fog and haze. This might reflect the more static meteorological conditions during fog and haze events, in which floating particles do not settle easily. Only a fraction of near-surface atmospheric particulate matter appeared to act as condensation nuclei, adsorbing water vapor. Under normal weather conditions, particles removed by dew include condensation nuclei and any airborne particles that would naturally undergo sedimentation.


## 3.2. Ionic Composition

Air quality obviously decreases during haze. Mass concentrations of PM2.5 and PM10 are typically 4–6 times higher during haze than on normal days [21] with almost all concentrations of water-soluble ions (NH4+, Mg2+, Ca2+, K+, Na+, Cl−, NO3-, F−, and SO42-) showing increases during haze events [22, 23]. In particular, the concentrations of K+ and other secondary aerosol indicators (NH4+, NO3-, and SO42-) increase markedly in haze [21, 23]. This study focused on air quality during haze events (Table 1), when haze formed more than 10 m above ground level [21, 24, 25]. We found that ion concentrations in both dew and particulate matter of the atmosphere were similar (Figure 2). In decreasing order of ionic concentration, airborne particles comprised SO42- > NO3- >NH4+ > Ca2+ > Cl− > Na+ > F− > K+ > Mg2. Although ion concentrations in fog were reduced, this order did not change. In contrast, during haze, ion concentrations increased and the decreasing order of ionic concentrations in airborne particles changed to SO42- > NO3- > NH4+ > Cl− > Ca2+ > K+ > F− > Na+ > Mg2+. Ions from anthropogenic pollution sources were the highest contributors to airborne particles in normal, foggy, and hazy weather. In particular, Cl− from coal and K+ from biomass burning were most enhanced in haze events. In dew, the decreasing order of ionic concentrations under normal and foggy conditions was SO42- > NH4+ > Ca2+ > NO3- > Cl− > Na+ > F− > K+ > Mg2+. In addition to the finding that all ion concentrations in dew during hazy weather were enhanced considerably, their order was also changed to SO42- > NH4+ > Ca2+ >NO3- > K+ > Cl− > F−> Na+ > Mg2+.Figure 2
Ionic concentrations ofNH4+, Mg2+, Ca2+, K+, Na+, Cl−, NO3-, F−, and SO42- of air particles and dew under normal (white), foggy (green), and hazy (red) conditions in Changchun, China.At the study site, ammonia (NH3) constituted an important alkaline gas in the atmosphere. The secondary aerosol was NO3-, which results from the transformations of various precursors of NOx [22]. The concentration of NH4+ was higher than NO3- in dew but not in airborne particles. Furthermore, NH4+ showed strong correlations with SO42- and [SO42- + NO3-] (p<0.01) in both dew and particle samples. The slopes of the regression equations between NH4+ and [SO42- + NO3-] and NH4+ and SO42- in dew were both smaller than unity (0.76 and 0.85), indicating incomplete neutralization of acidic species (HNO3 and H2SO4) by ammonia during the study period. This suggests the dominance of (NH4)2SO4 and NH4HSO4 [26] in the urban atmosphere. Thus, excess ammonia could combine with chloride and oxalate to form NH4Cl and (NH4)2CO3. Diurnal variability was observed for gaseous NH3 in the surface layer, and its concentration was higher than NO2 during periods of dew condensation [27]. Meanwhile, the concentration of HNO3 was higher during daytime [28]. This suggests that NH3 is readily converted to NH4+ in dew at night. Otherwise, it is possible that NH3 is dissolved easily in an acidic environment, whereby acidic dew accelerates the conversion of NH3 to NH4+ [29]. These scenarios all result in higher NH3 concentrations in dew.All ionic species in both airborne particles and dew decreased in transitions from normal to foggy conditions, but they increased in transitions from normal to hazy conditions. The origins of Ca2+, Na+, and Mg2+ are mainly from crustal sources such as resuspended road dust, soil dust, and construction dust, while SO42-, NO3-, and NH4+ represent secondary pollution sources. Usually, F− and Cl− are derived from coal combustion, while K+ is derived from biomass burning. The concentration ratios for normal/foggy conditions in airborne particles and dew for the main cations and anions were 1.40 and 1.30 for NH4+, 1.50 and 1.32 for Ca2+, 1.60 and 1.44 for Na+, 2.04 and 1.53 for K+, 1.82 and 1.49 for Mg2+, 1.19 and 1.18 for SO42-, 1.37 and 1.28 for NO3-, 1.69 and 1.13 for Cl−, and 1.57 and 1.47 for F−.The effect of haze on ions from different sources in both airborne particles and dew was significantly different. Haze concentrations of crustal ions (Ca2+, Na+, and Mg2+) in airborne particles were 1.87–5.05 times the normal particle levels; however, in dew, they were 3.26–3.69 times the normal dew levels. Haze concentrations of anthropogenic pollution species (SO42-, NO3-, and NH4+) were 3.89–5.98 times the normal particle levels and 4.78–7.99 times the normal dew levels. Haze concentrations of indicator ions (F−, Cl−, and K+) of coal and biomass burning were 2.27–6.05 times the normal particle levels and 3.93–8.96 times the normal dew levels. Throughout the sampling period, K+ showed the largest variation in airborne particles or dew. Haze caused serious air pollution. Clearly, this pollution was attributable to species from pollution and biomass burning sources. The chemical composition of the dew closely reflected the air quality of the near-surface atmosphere. Our results suggest that analyzing the chemical characteristics of dew can provide a reference for the assessment of air pollution and air quality. In particular, water-soluble ions from different sources were enhanced in dew compared with airborne particles collected simultaneously. We also observed that, under conditions of deteriorating air quality, the capability of dew to remove airborne pollutants increased.Dew condensation clearly had a purification effect on the near-surface atmosphere. In the process of vapor condensation, some airborne particles acted as dew condensation nuclei, while acidic or alkaline gas and solid particles dissolved directly in the dew. For instance,SO3- and HSO32- were partially oxidized to SO42- on oxidant surfaces, yielding the transformation of SO2 gas to SO42- solid, as outlined below in the following reactions:(5)O2a+SO2g⟶SO32-a,(6)OH-a+SO2g⟶HSO32-a/2OH-a+SO2g⟶SO42-a+H2O,where (a) and (g) represent aerosol and gas phases, respectively.Additionally, SO2 can also be absorbed by water in a liquid-phase reaction:(7)SO2+H2O⟷SO2·H2O,(8)SO2·H2O⟷H++HSO3-,(9)HSO3-⟷H++SO32-,where italics are used to show ionic species.Thus,SO42- in dew could originate from either homogeneous or heterogeneous chemical transformations of SO2 and SO42-. We suggest that part of the SO42- fraction might come from particles formed from gas or from gas absorption on particle surfaces. Clearly, conversion of SO2 to SO42- was accelerated by dew condensation. We conclude that condensation processes reduce pollutant concentrations of both gases and particulates in the near-surface atmosphere.


## 3.3. Carbonaceous Species

During this study, the concentrations of carbonaceous species showed similar trends to water-soluble species with the greatest levels in descending order recorded in hazy > normal > foggy conditions. The concentrations of OC and EC in airborne particles and the POC and PEC in dew were the highest in haze and the lowest in fog (Figure3). The average daily concentrations in airborne particles from hazy, foggy, and normal conditions were 40.75, 10.10, and 14.52 μg/m3 for OC and 7.91, 2.82, and 3.84 μg/m3 for EC, respectively. These values were 70.96, 7.38, and 10.85 mg/L for POC and 13.43, 2.73, and 3.51 mg/L for PEC in dew, under hazy, foggy, and normal conditions, respectively.Figure 3
Ionic concentrations of organic carbon (OC) and elemental carbon (EC) of air particles, as well as particulate organic carbon (POC) and particulate elemental carbon (PEC) of dew during normal (white), foggy (green), and hazy (red) conditions in Changchun, China.A ratio of OC/EC > 2 was used to identify the presence of secondary organic carbon (SOC) [21]. The average OC/EC ratio (5.16) in haze was about 1.43 times higher than in fog (3.60) and 1.35 times higher than on normal weather days (3.80). These ratios show that SOC formation was most serious during haze. In this study, average OC/EC ratios were 3.10, 2.72, and 5.33 for normal, foggy, and hazy conditions, respectively. The changes in OC and EC in dew and airborne particles were consistent (Figure 3), suggesting that analysis of POC and PEC in dew could be used to identify the presence of SOC.It is noted not only that OC is emitted from coal combustion, vehicle exhausts, and biomass burning, but also that it accumulates rapidly on fine particulate matter via photochemical reactions. Under low wind speeds and high atmospheric pressure, stagnation contributes to the accumulation of OC in haze as pollutants accumulate and form secondary aerosols.


## 4. Conclusions

Concentrations and compositions of dew and airborne particles in the near surface are closely related. The particle size distributions in dew and airborne particles were concordant under variable weather conditions. Air quality changes were most pronounced in haze with mass concentrations of TSP, PM2.5, and PM10 of around 2.78–4.29 times the normal levels. Similarly, TDS, PM2.5, and PM10 values in dew declined 0.50–0.63 times in fog, but they increased 1.60–2.54 times in haze compared with normal dew. Ion concentrations in dew and airborne particles also had synchronous patterns. Water-soluble ions from different sources were enhanced more in dew than in airborne particles. In particular, the concentrations of crustal ions (Ca2+, Na+, and Mg2+) in haze were 1.87–5.05 times the normal particle levels and 3.26–3.69 times the normal dew levels, while concentrations of anthropogenic pollution species (SO42-, NO3-, and NH4+) were 3.89–5.98 times the normal particle levels and 4.78–7.99 times the normal dew levels. Similarly, the concentrations of indicator species (F−, Cl−, and K+) of coal and biomass burning were 2.27–6.05 times the normal particle levels and 3.93–8.96 times the normal dew levels. With deterioration of air quality, the capability of dew to remove pollutants was decreased. The PM2.5 removal rates were 21.5%, 15.2%, and 13.7% in normal, foggy, and hazy conditions, respectively. It appears that condensation processes reduce pollutant concentrations of gases and particulates in the near-surface atmosphere. Dew is helpful for the settlement of atmospheric particulates, and its rate of removal of coarse particulates is better than for fine material. The TSP removal rates were 28.2%, 13.7%, and 18.5% in normal, foggy, and hazy weather. The changes in POC and PEC of dew and of OC and EC of airborne particles were consistent; therefore, analyzing the POC and PEC of dew could be used to identify SOC in the atmosphere. Dew composition can also be used to determine pollutant sources. Clearly, dew purifies urban air, and during hazy weather in particular, when air quality deteriorates dramatically, dew reduces local atmospheric pollution.



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*Source: 3514743-2017-08-06.xml*