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SUMMER SPRING PM , PM and PM acidity during spring and summer at one Po Valley site

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0 20 40 60 80 100 120 0 50 100 NO 3 - (n m o l/m 3 ) Excess NH4+ (nmol/m3)

PM1

spring summer

PM0.4

NH4+

NO3-

SO42-

Cl-minor ions

monocarb.

dicarb.

other

T (°C) RH % T (°C) RH %

PM2.5 12±5

72±19 21±5

72±17

PM1

12±4

72±18 23±5

69±15

PM0.4 12±1

77±9 26±1

61±3

SPRING

SUMMER

34%

31%

40%

22%

21%

5%

0

5

10

15

20

25

PM

2.

5

PM

1

PM

0.

4

PM

2.

5

PM

1

PM

0.

4

SPRING

SUMMER

Con

c.

tot H+

(nmol/m3)

free H+

(nmol/m3)

H2O

(µg/m3)

free H+/tot

H+ %

y = 1.00x + 1.56 R² = 0.97 y = 0.95x + 0.92 R² = 0.96 0 50 100 150 200 250 0 50 100 150 200 250 NH 4 + (n mol /m 3 ) Mol- (nmol/m3)

Ionic Balance

summer PM1

nitr.+sulf. nitr.+sulf.+carb.aci …

9.3%

6.3%

18.1%

0.3%

0.6%

0.4%

1.1%

63.9%

PM1

7.4%

17.2%

7.5%

0.3%

0.6%

0.4%

0.5%

66.2%

PM1

NH4+ NO3- SO42- Carb. MEAN 0.86 0.88 2.04 0.13 DEV.ST. 0.88 1.76 1.62 0.13 MEAN 1.37 0.80 2.95 0.23 DEV.ST. 0.97 0.99 2.34 0.18 MEAN 0.32 0.12 0.87 0.03 DEV.ST. 0.17 0.08 0.48 0.03 µg/m3 PM0.4 PM1 PM2.5 NH4+ NO3- SO42- Carb. MEAN 2.02 5.75 1.24 0.20 DEV.ST. 2.01 5.75 1.32 0.19 MEAN 1.17 2.94 0.99 0.11 DEV.ST. 1.10 3.18 0.84 0.10 MEAN 0.07 0.14 0.14 0.02 DEV.ST. 0.04 0.05 0.08 0.00 µg/m3 PM0.4 PM1 PM2.5

PM2.5 PM1 PM0.4 PM2.5 PM1 PM0.4

MEAN

21

12

3

13

12

5

DEV.ST.

14

8

1

8

7

1

MIN

3

3

2

2

1

3

MAX

59

32

4

49

26

7

SPRING

SUMMER

µg/m

3

0%

20%

40%

60%

80%

100%

SPRING

SUMMER

PM1-2.5

PM0.4-1

PM0.4

CONCLUSION

Seasonality trend of inorganic ions and carboxylic

acids in a rural site of Po Valley was showed.

The ionic balance was very close to neutrality (all the

samples were ammonium rich and tot H

+

and free H

+

concentrations were very low).

In summer there was a higher level of excess NH

4+

and carboxylic acids. Even if the tot H

+

concentration

was higher, the free H

+

was lower.

PM

2.5

, PM

1

and PM

0.4

acidity during spring and summer at one Po Valley site

European Aerosol Conference 2011 – 5-9 sep 2011 – Manchester, UK

G. Sangiorgi

1

, L. Ferrero

1

, M.G. Perrone

1

and E. Bolzacchini

1

1

POLARIS Research Centre, Department of Environmental Sciences, University of Milan - Bicocca, Milan, I-20126, Italy

contact author:

giorgia.sangiorgi1@unimib.it

 SAMPLING SITE:

SANNAZARO DE’ BURGONDI

(PAVIA)

typical rural site in the middle of the

Po Valley, Italy

 SAMPLING CAMPAIGN:

PM0.4 + PM1 + PM2.5

 ANALYSIS

PTFE filters extracted in ultra-pure water by ultrasonic bath and

analyzed by IC (Dionex®)

water soluble inorganic ions

Na

+

, NH

4+

, K

+

, Mg

2+

, Ca

2+

, F

-

, Cl

-

, NO

3-

,

PO

43-

, SO

4

2-mono-/dicarboxylic acids

acetic, propionic, formic, glutarric,

succinic, malonic, maleic, oxalic acids

SPRING

SPRING: 10 June – 2 July 2010 SUMMER: 24 March – 29 April 2010

Milano

Torino

Sannazaro

de’ Burgondi

High daily variations of PMx concentrations, low

seasonal variation of average PMx concentrations.

General low PM2.5 concentrations, typical of a

rural site of the Po Valley.

SUMMER

Seasonality of the ions of

secondary origin: NO

3-

decreases

dramatically from spring to summer

(volatility of NH

4

NO

3

), SO

42-

and

carboxylic acids

increases(photoreactivity of

gaseous precursors). Very typical

trend for the Po Valley.

Very similar pattern of

ionic balance for both the

seasons and all the PMx:

R

2

very high (R

2

≥ 0.96

);

slope very close to 1

(slope ≥ 0.85) and slightly

lower by adding

carboxylic acids as

negative ions.

SPRING: the excess NH

4+

neutralizes NO

3-

.

SUMMER: NO

3-

is too low

concentrated to explain

excess NH

4+

. Likely, NH

4+

is

present in PM to neutralize

organic acids.

The same trends were result for

all the PMx

All the samples of PMx in spring

and summer are AMMONIUM RICH

(NH

4+

/SO

42-

>1.5).

Low levels of total H

+

and free H

+

(<

10 nmol/m

3

on average).

Free H

+

and H

2

O average

concentrations decrease in summer.

Lower % of free H

+

-to-tot H+ in

summer (~20%) than in spring (30%).

 Free H+: moles of free hydrogen ions in the aqueous phase of aerosols per unit of air (nmol/m3).

► H+free = output of E-AIM model-II  Total H+: total amount of H+

contributed by the strong acids, such as sulfuric and nitric acids, in the

aqueous extract of the aerosols. ► H+tot=2×[SO

42-]+[NO3-]−[NH4+]

Aerosol Inorganic Model (E-AIM):

It is a state-of-the-art aerosol

thermodynamic model that can

simulate free acidity (free H

+

), aerosol

water content, and activities of ionic

species in aqueous aerosols and the

solid- and liquid-phase compositions

(2)

0 20 40 60 80 100 120 0 50 100 NO 3 - (n m o l/m 3 ) Excess NH4+ (nmol/m3)

PM1

spring summer

PM0.4

NH4+

NO3-

SO42-

Cl-minor ions

monocarb.

dicarb.

other

T (°C) RH % T (°C) RH %

PM2.5 12±5

72±19 21±5

72±17

PM1

12±4

72±18 23±5

69±15

PM0.4 12±1

77±9 26±1

61±3

SPRING

SUMMER

34%

31%

40%

22%

21%

5%

0

5

10

15

20

25

PM

2.

5

PM

1

PM

0.

4

PM

2.

5

PM

1

PM

0.

4

SPRING

SUMMER

Con

c.

tot H+

(nmol/m3)

free H+

(nmol/m3)

H2O

(µg/m3)

free H+/tot

H+ %

y = 1.00x + 1.56 R² = 0.97 y = 0.95x + 0.92 R² = 0.96 0 50 100 150 200 250 0 50 100 150 200 250 NH 4 + (n mol /m 3 ) Mol- (nmol/m3)

Ionic Balance

summer PM1

nitr.+sulf. nitr.+sulf.+carb.aci …

9.3%

6.3%

18.1%

0.3%

0.6%

0.4%

1.1%

63.9%

PM1

7.4%

17.2%

7.5%

0.3%

0.6%

0.4%

0.5%

66.2%

PM1

NH4+ NO3- SO42- Carb. MEAN 0.86 0.88 2.04 0.13 DEV.ST. 0.88 1.76 1.62 0.13 MEAN 1.37 0.80 2.95 0.23 DEV.ST. 0.97 0.99 2.34 0.18 MEAN 0.32 0.12 0.87 0.03 DEV.ST. 0.17 0.08 0.48 0.03 µg/m3 PM0.4 PM1 PM2.5 NH4+ NO3- SO42- Carb. MEAN 2.02 5.75 1.24 0.20 DEV.ST. 2.01 5.75 1.32 0.19 MEAN 1.17 2.94 0.99 0.11 DEV.ST. 1.10 3.18 0.84 0.10 MEAN 0.07 0.14 0.14 0.02 DEV.ST. 0.04 0.05 0.08 0.00 µg/m3 PM0.4 PM1 PM2.5

PM2.5 PM1 PM0.4 PM2.5 PM1 PM0.4

MEAN

21

12

3

13

12

5

DEV.ST.

14

8

1

8

7

1

MIN

3

3

2

2

1

3

MAX

59

32

4

49

26

7

SPRING

SUMMER

µg/m

3

0%

20%

40%

60%

80%

100%

SPRING

SUMMER

PM1-2.5

PM0.4-1

PM0.4

CONCLUSION

Seasonality trend of inorganic ions and carboxylic

acids in a rural site of Po Valley was showed.

The ionic balance was very close to neutrality (all the

samples were ammonium rich and tot H

+

and free H

+

concentrations were very low).

In summer there was a higher level of excess NH

4+

and carboxylic acids. Even if the tot H

+

concentration

was higher, the free H

+

was lower.

PM

2.5

, PM

1

and PM

0.4

acidity during spring and summer at one Po Valley site

European Aerosol Conference 2011 – 5-9 sep 2011 – Manchester, UK

G. Sangiorgi

1

, L. Ferrero

1

, M.G. Perrone

1

and E. Bolzacchini

1

1

POLARIS Research Centre, Department of Environmental Sciences, University of Milan - Bicocca, Milan, I-20126, Italy

contact author:

giorgia.sangiorgi1@unimib.it

 SAMPLING SITE:

SANNAZARO DE’ BURGONDI

(PAVIA)

typical rural site in the middle of the

Po Valley, Italy

 SAMPLING CAMPAIGN:

PM0.4 + PM1 + PM2.5

 ANALYSIS

PTFE filters extracted in ultra-pure water by ultrasonic bath and

analyzed by IC (Dionex®)

water soluble inorganic ions

Na

+

, NH

4+

, K

+

, Mg

2+

, Ca

2+

, F

-

, Cl

-

, NO

3-

,

PO

43-

, SO

4

2-mono-/dicarboxylic acids

acetic, propionic, formic, glutarric,

succinic, malonic, maleic, oxalic acids

SPRING

SPRING: 10 June – 2 July 2010 SUMMER: 24 March – 29 April 2010

Milano

Torino

Sannazaro

de’ Burgondi

High daily variations of PMx concentrations, low

seasonal variation of average PMx concentrations.

General low PM2.5 concentrations, typical of a

rural site of the Po Valley.

SUMMER

Seasonality of the ions of

secondary origin: NO

3-

decreases

dramatically from spring to summer

(volatility of NH

4

NO

3

), SO

42-

and

carboxylic acids

increases(photoreactivity of

gaseous precursors). Very typical

trend for the Po Valley.

Very similar pattern of

ionic balance for both the

seasons and all the PMx:

R

2

very high (R

2

≥ 0.96

);

slope very close to 1

(slope ≥ 0.85) and slightly

lower by adding

carboxylic acids as

negative ions.

SPRING: the excess NH

4+

neutralizes NO

3-

.

SUMMER: NO

3-

is too low

concentrated to explain

excess NH

4+

. Likely, NH

4+

is

present in PM to neutralize

organic acids.

The same trends were result for

all the PMx

All the samples of PMx in spring

and summer are AMMONIUM RICH

(NH

4+

/SO

42-

>1.5).

Low levels of total H

+

and free H

+

(<

10 nmol/m

3

on average).

Free H

+

and H

2

O average

concentrations decrease in summer.

Lower % of free H

+

-to-tot H+ in

summer (~20%) than in spring (30%).

 Free H+: moles of free hydrogen ions in the aqueous phase of aerosols per unit of air (nmol/m3).

► H+free = output of E-AIM model-II  Total H+: total amount of H+

contributed by the strong acids, such as sulfuric and nitric acids, in the

aqueous extract of the aerosols. ► H+tot=2×[SO

42-]+[NO3-]−[NH4+]

Aerosol Inorganic Model (E-AIM):

It is a state-of-the-art aerosol

thermodynamic model that can

simulate free acidity (free H

+

), aerosol

water content, and activities of ionic

species in aqueous aerosols and the

solid- and liquid-phase compositions

Riferimenti

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