source apportionment of prague aerosol from combined particle number size distribution and gaseous...

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SOURCE APPORTIONMENT OF PRAGUE AEROSOL FROM COMBINED PARTICLE NUMBER SIZE DISTRIBUTION AND GASEOUS COMPOSITION DATA BY BILINEAR POSITIVE MATRIX FACTORIZATION Devraj Thimmaiah 1 , Jan Hovorka 1 and Philip K. Hopke 2 1 Institute for Environmental Studies, Charles University in Prague, 12801, 2 Department of Chemical & Biomolecular Engineering, Clarkson Univ., Potsdam,13699,USA [email protected], [email protected], [email protected] Identify and apportion the sources of ambient aerosols in the urban atmosphere of Prague, Czech Republic using bilinear Positive Matrix Factorization (PMF2) model. European Aerosol Conference (EAC), September 9-14, 2007, Salzburg, Austria To help in interpreting and in knowing the directionality of the sources, Conditional Probability Function plots (CPF) (Ashbaugh et al., 1985) were used. The CPF plots of contributing sources and overall wind profile is shown in Figure 2-7. PMF technique was first introduced by Paatero & Tapper in 1993. A similar study for modeling source contributions to submicron particle number concentrations in Rochester, NY is performed by Ogulei et al., 2007. Fpeak Analysis between -1 and +1 was This work was supported by the Grant Agency, Czech Republic under GAUK Grant No. PřF/49707 /2007. 1. Objective 2. Experimental 3. Results & Discussion 5. Conclusion 6. Acknowledgement Figure 1. Location of sampling site Figure 2-7. Directionality of contributing sources and overall wind profile using CPF. Figure 8a,b. Wind roses for the sampling period Figure 10-15: Weekday and Weekend variations of 5 sources identified by PMF2. Sampling site Figure 16 and 17. Source profiles and contributions deduced from PMF2 analysis. Table 1. Summary of measured species Measurement Instrument Original time resolution before averaging to 1 h. Particle size SMPS-3936L25 10 min Size range: 14.6-736.5nm Meteorological data Vane type 15 min WS, WD, Temp, RH Gaseous data Horiba 15 min CO, SO 2 , NO X & O 3 Rain Intensity LNM Disdrometer 1 min PMF2 has identified 5 factors. They are: traffic, ozone influenced secondary particles, residential heating and two unidentified mixed sources 1 & 2 with directionality from all the sides. Work is in progress to identify these two sources. One of the mixed sources maybe background or long range transport, not known due to lack of tracers. 7. References Ashbaugh, L.L., Malm, W.C. & Sadeh, W.Z. (1985). Atmospheric Environment, 19, 1263-1270. Paatero, P., & Tapper, U. (1993). Chemometrics Intell. Lab Sys. , 18:183-194. Ogulei, D., Hopke, P.K., Chalupa, D.C., & Utell, M.J. (2007). Aerosol Sci. Technol. , 41,179 -201. Figure 9. Fpeak analysis to find lowest Q value The source profiles and the contributions deduced from PMF2 analysis in Prague is depicted in Figure 16 and 17 respectively. M ixed Source-1 0.0001 0.001 0.01 0.1 1 Traffic 0.0001 0.001 0.01 0.1 1 M ixed Source-2 0.0001 0.001 0.01 0.1 1 O 3 Secondary Particles 15.1 16.8 18.8 20.9 23.3 25.9 28.9 32.2 35.9 40 44.5 49.6 55.2 61.5 68.5 76.4 85.1 94.7 105.5 117.6 131 145.9 162.5 181.1 201.7 224.7 250.3 278.8 310.6 346 385.4 429.4 478.3 532.8 593.5 661.2 723.5 CO NOX SO2 O3 0.0001 0.001 0.01 0.1 1 Heating 0.0001 0.001 0.01 0.1 1 Concentration#/ # M ixed Source 1 0 2000 4000 6000 8000 10000 12000 14000 16000 18000 Traffic 0 200 400 600 800 Heating 0 2000 4000 6000 8000 10000 12000 M ixed Source-2 0 2000 4000 6000 8000 10000 12000 14000 16000 O 3 Secondary Particles 2/16/2007 2/17/2007 2/18/2007 2/19/2007 2/20/2007 2/21/2007 2/22/2007 2/23/2007 2/24/2007 2/25/2007 2/26/2007 2/27/2007 2/28/2007 3/1/2007 3/2/2007 3/3/2007 3/4/2007 3/5/2007 3/6/2007 3/7/2007 3/8/2007 3/9/2007 3/10/2007 3/11/2007 3/12/2007 3/13/2007 3/14/2007 3/15/2007 3/16/2007 3/17/2007 3/18/2007 3/19/2007 3/20/2007 3/21/2007 3/22/2007 3/23/2007 3/24/2007 3/25/2007 3/26/2007 3/27/2007 3/28/2007 3/29/2007 3/30/2007 3/31/2007 4/1/2007 4/2/2007 4/3/2007 4/4/2007 4/5/2007 4/6/2007 4/7/2007 4/8/2007 4/9/2007 4/10/2007 4/11/2007 0 200 400 600 800 1000 1200 1400 Num berconcentration #/cm 3 A series of CPF plots (Figure 18-25) for the meteorological data recorded at the receptor site were drawn to help in identifying and naming the sources deduced by PMF2, Figure 26-29 give the variation of Temp, RH, and Rain intensity recorded at the site. Tem p oC -2 -1 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 2 /1 6 /2 0 0 7 0 :30 2 /1 7 /2 0 0 7 0:30 2 /1 8 /2 0 0 7 0 :30 2 /1 9 /2 0 0 7 0 :30 2 /2 0 /2 0 0 7 0 :30 2 /2 1 /2 0 0 7 0 :30 2 /2 2 /2 0 0 7 0 :30 2 /2 3 /2 0 0 7 0 :30 2 /2 4 /2 0 0 7 0:3 0 2 /2 5 /2 0 0 7 0:30 2 /2 6 /2 0 0 7 0 :30 2 /2 7 /2 0 0 7 0 :30 2 /2 8 /2 0 0 7 0 :30 3 /1 /2 0 0 7 0 :30 3 /2 /2 0 0 7 0 :30 3 /3 /2 0 0 7 0:30 3 /4 /2 0 0 7 0 :30 3 /5 /2 0 0 7 0:3 0 3 /6 /2 0 0 7 0 :30 3 /7 /2 0 0 7 0 :30 3 /8 /2 0 0 7 0 :30 3 /9 /2 0 0 7 0:30 3 /1 0 /2 0 0 7 0:30 3 /1 1 /2 0 0 7 0 :30 3 /1 2 /2 0 0 7 0:30 3 /1 3 /2 0 0 7 0 :30 3 /1 4 /2 0 0 7 0 :30 3 /1 5 /2 0 0 7 0:30 3 /1 6 /2 0 0 7 0 :30 3 /1 7 /2 0 0 7 0 :30 3 /1 8 /2 0 0 7 0:30 3 /1 9 /2 0 0 7 0 :30 3 /2 0 /2 0 0 7 0 :30 3 /2 1 /2 0 0 7 0 :30 3 /2 2 /2 0 0 7 0 :30 3 /2 3 /2 0 0 7 0:30 3 /2 4 /2 0 0 7 0 :30 3 /2 5 /2 0 0 7 0:30 3 /2 6 /2 0 0 7 0 :30 3 /2 7 /2 0 0 7 0 :30 3 /2 8 /2 0 0 7 0 :30 3 /2 9 /2 0 0 7 0 :30 3 /3 0 /2 0 0 7 0 :30 3 /3 1 /2 0 0 7 0:30 4 /1 /2 0 0 7 0:30 4 /2 /2 0 0 7 0:3 0 4 /3 /2 0 0 7 0 :30 4 /4 /2 0 0 7 0 :30 4 /5 /2 0 0 7 0 :30 4 /6 /2 0 0 7 0:30 4 /7 /2 0 0 7 0:3 0 4 /8 /2 0 0 7 0:3 0 4 /9 /2 0 0 7 0 :30 4 /1 0 /2 0 0 7 0:30 Tem p oC RH % 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 2 /1 6 /2 0 0 7 0:30 2 /1 7 /2 0 0 7 0:30 2 /1 8 /2 0 0 7 0:30 2 /1 9 /2 0 0 7 0:30 2 /2 0 /2 0 0 7 0:30 2 /2 1 /2 0 0 7 0:30 2 /2 2 /2 0 0 7 0:30 2 /2 3 /2 0 0 7 0:30 2 /2 4 /2 0 0 7 0:30 2 /2 5 /2 0 0 7 0:30 2 /2 6 /2 0 0 7 0:30 2 /2 7 /2 0 0 7 0:30 2 /2 8 /2 0 0 7 0:30 3 /1 /2 0 0 7 0:30 3 /2 /2 0 0 7 0:30 3 /3 /2 0 0 7 0:30 3 /4 /2 0 0 7 0:30 3 /5 /2 0 0 7 0:30 3 /6 /2 0 0 7 0:30 3 /7 /2 0 0 7 0:30 3 /8 /2 0 0 7 0:30 3 /9 /2 0 0 7 0:30 3 /1 0 /2 0 0 7 0:30 3 /1 1 /2 0 0 7 0:30 3 /1 2 /2 0 0 7 0:30 3 /1 3 /2 0 0 7 0:30 3 /1 4 /2 0 0 7 0:30 3 /1 5 /2 0 0 7 0:30 3 /1 6 /2 0 0 7 0:30 3 /1 7 /2 0 0 7 0:30 3 /1 8 /2 0 0 7 0:30 3 /1 9 /2 0 0 7 0:30 3 /2 0 /2 0 0 7 0:30 3 /2 1 /2 0 0 7 0:30 3 /2 2 /2 0 0 7 0:30 3 /2 3 /2 0 0 7 0:30 3 /2 4 /2 0 0 7 0:30 3 /2 5 /2 0 0 7 0:30 3 /2 6 /2 0 0 7 0:30 3 /2 7 /2 0 0 7 0:30 3 /2 8 /2 0 0 7 0:30 3 /2 9 /2 0 0 7 0:30 3 /3 0 /2 0 0 7 0:30 3 /3 1 /2 0 0 7 0:30 4 /1 /2 0 0 7 0:30 4 /2 /2 0 0 7 0:30 4 /3 /2 0 0 7 0:30 4 /4 /2 0 0 7 0:30 4 /5 /2 0 0 7 0:30 4 /6 /2 0 0 7 0:30 4 /7 /2 0 0 7 0:30 4 /8 /2 0 0 7 0:30 4 /9 /2 0 0 7 0:30 4 /1 0 /2 0 0 7 0:30 R H % 4. Supplementary material 0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 4.50 5.00 5.50 6.00 6.50 7.00 7.50 8.00 8.50 9.00 9.50 2/16/07 5:4 2 2/16/07 8 :15 2/19/07 8:05 2/19/07 8:25 2/19/07 8:45 2/19/07 9 :05 2/19/07 9:2 5 2/19/07 9 :45 2/19/07 1 0:0 5 2/19/07 1 0:2 5 2/19/07 10:45 2/19/07 11:05 2/19/07 1 1:2 5 2/19/07 1 2:0 4 2/22/07 4:54 2/22/07 5:14 2/22/07 5:3 4 2/22/07 5:54 2/22/07 6:14 2/25/07 1 4:1 6 2/25/07 1 7:5 3 2/25/07 1 8:1 3 2/26/07 11:55 2/27/07 0:13 2/27/07 4:59 2/27/07 5:19 2/27/07 5:39 2/27/07 5:59 2/27/07 6:45 2/27/07 7 :05 2/27/07 7:38 2/27/07 7:58 2/27/07 8:1 8 2/27/07 11:15 2/27/07 1 1:5 7 2/27/07 1 2:1 7 2/27/07 1 2:3 7 2/27/07 1 2:5 7 2/27/07 15:25 2/27/07 16 :2 8 2/27/07 1 6:4 8 2/27/07 17:08 2/27/07 21:08 2/27/07 2 1:2 8 2/27/07 21:48 2/27/07 2 2:0 8 2/27/07 2 2:2 8 2/27/07 2 2:4 8 2/27/07 2 3:0 8 2/27/07 2 3:2 8 2/27/07 2 3:4 8 2/28/07 0 :08 2/28/07 0:28 2/28/07 0:48 2/28/07 1:0 8 2/28/07 1:28 2/28/07 1:48 2/28/07 2 :08 2/28/07 2 :28 2/28/07 2:48 2/28/07 3:0 8 2/28/07 3:28 2/28/07 3:55 2/28/07 4:1 5 2/28/07 4 :47 2/28/07 6:20 2/28/07 15:05 2/28/07 15:25 FEB Intensity 0.00 0.25 0.50 0.75 1.00 1.25 1.50 1.75 2.00 2.25 2.50 2.75 3.00 3.25 3.50 3.75 4.00 4.25 4.50 4.75 5.00 5.25 5.50 5.75 3/1/07 11:25 3/1/07 1 2 :2 7 3/2/07 1:32 3 /3 /0 7 7 :33 3/3/07 8:33 3 /3 /0 7 9 :33 3 /3 /0 7 1 0 :3 3 3/3/07 1 1:3 3 3/3/07 15:12 3 /3 /0 7 1 8 :3 5 3/3/07 21 :0 4 3 /3 /0 7 2 2 :0 4 3/3/07 23 :0 4 3/4/07 2:00 3/4/07 3:01 3/4/07 4:02 3/4/07 5:02 3/4/07 6:02 3/4/07 7:10 3 /5 /0 7 1 7 :4 6 3/8/07 4 :02 3 /8 /0 7 5 :0 2 3/8/07 6 :05 3/8/07 7:05 3/8/0 7 8 :05 3/8/07 9:05 3/8/07 10 :0 5 3/8/07 11:05 3/8/07 1 2:0 5 3/10 /0 7 4 :4 8 3/10 /0 7 6 :41 3/10/07 7 :4 1 3/10 /0 7 8 :41 3/10 /0 7 9 :4 1 3/10/07 10 :4 1 3/17/07 9 :56 3/17/07 21 :1 8 3/18 /0 7 1 0 :53 3/18/0 7 1 8 :1 5 3/18 /0 7 2 1:57 3/18 /0 7 2 2 :5 7 3/20/07 11:59 3 /2 0 /0 7 1 3:04 3/20/07 16:41 3/20/07 17:41 3/20 /0 7 2 0 :2 3 3/20/07 21:23 3/20/07 22:23 3/20 /0 7 2 3 :2 3 3/21/07 0:23 3/21/07 1:23 3/21/07 2 :23 3/21/07 3 :2 3 3/21/07 9 :49 3/21/07 11:00 3/22/07 3:42 3/22/07 4:42 3/22/07 5 :42 3/22 /0 7 6 :4 2 3/22/07 8 :47 3/23 /0 7 1 5 :0 9 3/23 /0 7 1 6 :0 9 3/23/07 17:09 3/23 /0 7 1 8 :0 9 3/23 /0 7 1 9 :0 9 3/23/07 20 :0 9 3/23/07 2 1 :0 9 3/23/07 22:09 3 /2 3 /0 7 2 3:27 3/24 /0 7 1 :56 3/24/07 3:25 3/24 /0 7 8 :1 4 3/24/07 9 :14 3/24 /0 7 1 8 :0 6 3/24/07 1 9 :1 9 M arch Intensity Figure 26-29. Variation of Temp., RH and Rain intensity recorded at receptor site. Sampling site: All the data were recorded at roof-top (at height 25m) station at the receptor site, University Botanic garden in the Prague city center (50 0 4`17.29”N, 14 0 25`46.52”E) (Figure 1). Apparatus: Particle number size concentrations, ambient gaseous concentrations, meteorological data and rain intensity measured at the receptor site, instrumentation used is summarized in Table 1. Sampling period: Feb 16-28, March and April 01-10, 2007. Data Analysis: All the data obtained were normalized and averaged to hourly concentrations and used in data matrix preparation

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Page 1: SOURCE APPORTIONMENT OF PRAGUE AEROSOL FROM COMBINED PARTICLE NUMBER SIZE DISTRIBUTION AND GASEOUS COMPOSITION DATA BY BILINEAR POSITIVE MATRIX FACTORIZATION

SOURCE APPORTIONMENT OF PRAGUE AEROSOL FROM COMBINED PARTICLE NUMBER SIZE DISTRIBUTION AND GASEOUS COMPOSITION

DATA BY BILINEAR POSITIVE MATRIX FACTORIZATIONDevraj Thimmaiah1, Jan Hovorka1 and Philip K. Hopke2

1Institute for Environmental Studies, Charles University in Prague, 12801, Prague, Czech Republic

2Department of Chemical & Biomolecular Engineering, Clarkson Univ., Potsdam,13699,USA

[email protected], [email protected], [email protected] and apportion the sources of ambient aerosols in the urban atmosphere of Prague, Czech Republic using bilinear Positive Matrix Factorization (PMF2) model.

European Aerosol Conference (EAC), September 9-14, 2007, Salzburg, Austria

To help in interpreting and in knowing the directionality of the sources, Conditional Probability Function plots (CPF) (Ashbaugh et al., 1985) were used. The CPF plots of contributing sources and overall wind profile is shown in Figure 2-7. PMF technique was first introduced by Paatero & Tapper in 1993. A similar study for modeling source contributions to submicron particle number concentrations in Rochester, NY is performed by Ogulei et al., 2007. Fpeak Analysis between -1 and +1 was performed and the lowest Q value was when the Fpeak was set to 0.0. (Figure 9).

This work was supported by the Grant Agency, Czech Republic under GAUK Grant No. PřF/49707 /2007.

1. Objective

2. Experimental

3. Results & Discussion

5. Conclusion

6. Acknowledgement

Figure 1. Location of sampling site

Figure 2-7. Directionality of contributing sources and overall wind profile using CPF.

Figure 8a,b. Wind roses for the sampling period

Figure 10-15: Weekday and Weekend variations of 5 sources identified by PMF2.

Sampling site

Figure 16 and 17. Source profiles and contributions deduced from PMF2 analysis.

Table 1. Summary of measured species

 Measurement Instrument Original time resolution   before averaging to 1 h.Particle size SMPS-3936L25 10 minSize range: 14.6-736.5nmMeteorological data Vane type 15 minWS, WD, Temp, RHGaseous data Horiba 15 minCO, SO2, NOX & O3

Rain Intensity LNM Disdrometer 1 min

PMF2 has identified 5 factors. They are: traffic, ozone influenced secondary particles, residential heating and two unidentified mixed sources 1 & 2 with directionality from all the sides. Work is in progress to identify these two sources. One of the mixed sources maybe background or long range transport, not known due to lack of tracers.

7. ReferencesAshbaugh, L.L., Malm, W.C. & Sadeh, W.Z. (1985). Atmospheric Environment, 19, 1263-1270.Paatero, P., & Tapper, U. (1993). Chemometrics Intell. Lab Sys., 18:183-194. Ogulei, D., Hopke, P.K., Chalupa, D.C., & Utell, M.J. (2007). Aerosol Sci. Technol., 41,179 -201.

Figure 9. Fpeak analysis to find lowest Q value

The source profiles and the contributions deduced from PMF2 analysis in Prague is depicted in Figure 16 and 17 respectively.

Mixed Source-1

0.0001

0.001

0.01

0.1

1

Traffic

0.0001

0.001

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Mixed Source-2

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O3 Secondary Particles

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16.8

18.8

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23.3

25.9

28.9

32.2

35.9 40

44.5

49.6

55.2

61.5

68.5

76.4

85.1

94.7

105.

511

7.6 131

145.

916

2.5

181.

120

1.7

224.

725

0.3

278.

831

0.6 346

385.

442

9.4

478.

353

2.8

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566

1.2

723.

5 CONO

XSO

2 O3

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tion

# / #

Mixed Source 1

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1000012000140001600018000

Traffic

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3

A series of CPF plots (Figure 18-25) for the meteorological data recorded at the receptor site were drawn to help in identifying and naming the sources deduced by PMF2, Figure 26-29 give the variation of Temp, RH, and Rain intensity recorded at the site.

Temp oC

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3/1

5/2

00

7 0

:30

3/1

6/2

00

7 0

:30

3/1

7/2

00

7 0

:30

3/1

8/2

00

7 0

:30

3/1

9/2

00

7 0

:30

3/2

0/2

00

7 0

:30

3/2

1/2

00

7 0

:30

3/2

2/2

00

7 0

:30

3/2

3/2

00

7 0

:30

3/2

4/2

00

7 0

:30

3/2

5/2

00

7 0

:30

3/2

6/2

00

7 0

:30

3/2

7/2

00

7 0

:30

3/2

8/2

00

7 0

:30

3/2

9/2

00

7 0

:30

3/3

0/2

00

7 0

:30

3/3

1/2

00

7 0

:30

4/1

/20

07

0:3

0

4/2

/20

07

0:3

0

4/3

/20

07

0:3

0

4/4

/20

07

0:3

0

4/5

/20

07

0:3

0

4/6

/20

07

0:3

0

4/7

/20

07

0:3

0

4/8

/20

07

0:3

0

4/9

/20

07

0:3

0

4/1

0/2

00

7 0

:30

RH %

4. Supplementary material

0.00

0.50

1.00

1.50

2.00

2.50

3.00

3.50

4.00

4.50

5.00

5.50

6.00

6.50

7.00

7.50

8.00

8.50

9.00

9.50

2/1

6/0

7 5

:42

2/1

6/0

7 8

:15

2/1

9/0

7 8

:05

2/1

9/0

7 8

:25

2/1

9/0

7 8

:45

2/1

9/0

7 9

:05

2/1

9/0

7 9

:25

2/1

9/0

7 9

:45

2/1

9/0

7 1

0:0

5

2/1

9/0

7 1

0:2

5

2/1

9/0

7 1

0:4

5

2/1

9/0

7 1

1:0

5

2/1

9/0

7 1

1:2

5

2/1

9/0

7 1

2:0

4

2/2

2/0

7 4

:54

2/2

2/0

7 5

:14

2/2

2/0

7 5

:34

2/2

2/0

7 5

:54

2/2

2/0

7 6

:14

2/2

5/0

7 1

4:1

6

2/2

5/0

7 1

7:5

3

2/2

5/0

7 1

8:1

3

2/2

6/0

7 1

1:5

5

2/2

7/0

7 0

:13

2/2

7/0

7 4

:59

2/2

7/0

7 5

:19

2/2

7/0

7 5

:39

2/2

7/0

7 5

:59

2/2

7/0

7 6

:45

2/2

7/0

7 7

:05

2/2

7/0

7 7

:38

2/2

7/0

7 7

:58

2/2

7/0

7 8

:18

2/2

7/0

7 1

1:1

5

2/2

7/0

7 1

1:5

7

2/2

7/0

7 1

2:1

7

2/2

7/0

7 1

2:3

7

2/2

7/0

7 1

2:5

7

2/2

7/0

7 1

5:2

5

2/2

7/0

7 1

6:2

8

2/2

7/0

7 1

6:4

8

2/2

7/0

7 1

7:0

8

2/2

7/0

7 2

1:0

8

2/2

7/0

7 2

1:2

8

2/2

7/0

7 2

1:4

8

2/2

7/0

7 2

2:0

8

2/2

7/0

7 2

2:2

8

2/2

7/0

7 2

2:4

8

2/2

7/0

7 2

3:0

8

2/2

7/0

7 2

3:2

8

2/2

7/0

7 2

3:4

8

2/2

8/0

7 0

:08

2/2

8/0

7 0

:28

2/2

8/0

7 0

:48

2/2

8/0

7 1

:08

2/2

8/0

7 1

:28

2/2

8/0

7 1

:48

2/2

8/0

7 2

:08

2/2

8/0

7 2

:28

2/2

8/0

7 2

:48

2/2

8/0

7 3

:08

2/2

8/0

7 3

:28

2/2

8/0

7 3

:55

2/2

8/0

7 4

:15

2/2

8/0

7 4

:47

2/2

8/0

7 6

:20

2/2

8/0

7 1

5:0

5

2/2

8/0

7 1

5:2

5

FEB Intensity

0.00

0.25

0.50

0.75

1.00

1.25

1.50

1.75

2.00

2.25

2.50

2.75

3.00

3.25

3.50

3.75

4.00

4.25

4.50

4.75

5.00

5.25

5.50

5.75

3/1

/07 1

1:2

5

3/1

/07 1

2:2

7

3/2

/07 1

:32

3/3

/07 7

:33

3/3

/07 8

:33

3/3

/07 9

:33

3/3

/07 1

0:3

3

3/3

/07 1

1:3

3

3/3

/07 1

5:1

2

3/3

/07 1

8:3

5

3/3

/07 2

1:0

4

3/3

/07 2

2:0

4

3/3

/07 2

3:0

4

3/4

/07 2

:00

3/4

/07 3

:01

3/4

/07 4

:02

3/4

/07 5

:02

3/4

/07 6

:02

3/4

/07 7

:10

3/5

/07 1

7:4

6

3/8

/07 4

:02

3/8

/07 5

:02

3/8

/07 6

:05

3/8

/07 7

:05

3/8

/07 8

:05

3/8

/07 9

:05

3/8

/07 1

0:0

5

3/8

/07 1

1:0

5

3/8

/07 1

2:0

5

3/1

0/0

7 4

:48

3/1

0/0

7 6

:41

3/1

0/0

7 7

:41

3/1

0/0

7 8

:41

3/1

0/0

7 9

:41

3/1

0/0

7 1

0:4

1

3/1

7/0

7 9

:56

3/1

7/0

7 2

1:1

8

3/1

8/0

7 1

0:5

3

3/1

8/0

7 1

8:1

5

3/1

8/0

7 2

1:5

7

3/1

8/0

7 2

2:5

7

3/2

0/0

7 1

1:5

9

3/2

0/0

7 1

3:0

4

3/2

0/0

7 1

6:4

1

3/2

0/0

7 1

7:4

1

3/2

0/0

7 2

0:2

3

3/2

0/0

7 2

1:2

3

3/2

0/0

7 2

2:2

3

3/2

0/0

7 2

3:2

3

3/2

1/0

7 0

:23

3/2

1/0

7 1

:23

3/2

1/0

7 2

:23

3/2

1/0

7 3

:23

3/2

1/0

7 9

:49

3/2

1/0

7 1

1:0

0

3/2

2/0

7 3

:42

3/2

2/0

7 4

:42

3/2

2/0

7 5

:42

3/2

2/0

7 6

:42

3/2

2/0

7 8

:47

3/2

3/0

7 1

5:0

9

3/2

3/0

7 1

6:0

9

3/2

3/0

7 1

7:0

9

3/2

3/0

7 1

8:0

9

3/2

3/0

7 1

9:0

9

3/2

3/0

7 2

0:0

9

3/2

3/0

7 2

1:0

9

3/2

3/0

7 2

2:0

9

3/2

3/0

7 2

3:2

7

3/2

4/0

7 1

:56

3/2

4/0

7 3

:25

3/2

4/0

7 8

:14

3/2

4/0

7 9

:14

3/2

4/0

7 1

8:0

6

3/2

4/0

7 1

9:1

9

March Intensity

Figure 26-29. Variation of Temp., RH and Rain intensity recorded at receptor site.

Sampling site: All the data were recorded at roof-top (at height 25m) station at the receptor site, University Botanic garden in the Prague city center (5004`17.29”N, 14025`46.52”E) (Figure 1).

Apparatus: Particle number size concentrations, ambient gaseous concentrations, meteorological data and rain intensity measured at the receptor site, instrumentation used is summarized in Table 1.

Sampling period: Feb 16-28, March and April 01-10, 2007.

Data Analysis: All the data obtained were normalized and averaged to hourly concentrations and used in data matrix preparation