size-segregated analysis of pm10 at a tandem urban – rural site combination j. k. gietl 1*, t....

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Size-segregated analysis of PM10 at a tandem urban – rural site combination J. K. Gietl 1* , T. Tritscher 1,2 , and O. Klemm 1 1 University of Münster, Institute for Landscape Ecology, Germany 2 now Paul Scherrer Institute, Laboratory of Atmospheric Chemistry, Switzerland Introduction In January 2006, size segregated measurements and analysis of the chemical composition of PM10 samples, collected twice daily with Berner type impactors, were made to determine its source patterns. The measurements were performed at two sites in Münster, NW Germany. One of the sites was located in the centre of Münster, next to a four- to six- lane main road. The second one was set up in a bird nature protection area 6 km to the North. Results The mean mass concentration, calculated as the sum of ions plus carbon, was clearly higher at the roadside than in the surrounding (31 µg/m³ to 24 µg/m³]). Between the two sites, there was no significant difference in ion mass concentration, correlation coefficient of 0.92. Analysis The carbon analysis was made with an OCEC Lab Analyser. The main ions (Cl - , NO 3 - , SO 4 2- ) were analyzed with an ion chromatograph. NH 4 + was detected with a flow injection analyser and Ca 2+ , Mg 2+ , and Na + with an atom-absorbing spectrometer. European Aerosol Conference 2007 - September 11, 2007, Salzburg, Austria Acknowledgement This study was financially and logistically supported by the municipality of Münster, the Biological Station, Rieselfelder Münster, gave logistic support, and data access was granted by the Landesamt für Natur, Umwelt und Verbraucherschutz NRW (former Landesumweltamt NRW). For further information please contact: [email protected] http:// kli.uni-muenster.de Method The samples were taken with two five stage Berner type impactors. They were collected on Tedlar® foils and on quartz fiber filters (Whatman) taken simultaneously, with sample integration time being 6 hours. Sample on impactor stage equipped with Tedlar® foil and quartz fibre filter on top 0 5 10 15 20 25 30 January 2006 [µg/m ³] Münstercity ruralsurrounding omparison of the total analysed ion concentration in January 2006 Conclusions Carbon made the main difference between the two sites in Münster. The difference between the two sites averages 7 µg/m³, meaning about 23 % coming from traffic and 77% originating from background concentration. In contrast, no clear difference was found between the mean ion concentrations. 0.0 8.0 16.0 24.0 32.0 urban rural concentration [µg/m ³] Am monium Calcium C hloride Magnesium N itrate Sodium Sulphate TotalC arbon 0 0.2 0.4 0.6 0.8 1 Calcium Chloride Magnesium Sodium [µg/m ³] urban day urban night rural day rural night 0 2 4 6 8 Ammonium Nitrate Sulphate [µg/m ³] urban day urban night rural day rural night The main difference between these sites was caused by carbon, due to traffic and other combustion processes like domestic heating. Daytime values were significantly higher than the concentrations during nighttime. There were slight differences in ion concentrations. Additional NaCl lead back to de-icing salt in the city. The accesorily calcium at the roadside is due to dust dispersion from road traffic. The secondary ions NH 4 - and NO 3 - increased during nighttime due to the light sensitive reactions of nitrogen. NO 2 is not photolyzed during night, and so can react with OH forming HNO 3 . Ammonium was high, compared to other components, which is typicall for sites near agricultual activitiy. Mean mass concentrations of the ions in January 2006

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Page 1: Size-segregated analysis of PM10 at a tandem urban – rural site combination J. K. Gietl 1*, T. Tritscher 1,2, and O. Klemm 1 1 University of Münster, Institute

Size-segregated analysis of PM10 at a tandem urban – rural site combination

J. K. Gietl1*, T. Tritscher1,2, and O. Klemm1

1University of Münster, Institute for Landscape Ecology, Germany2 now Paul Scherrer Institute, Laboratory of Atmospheric Chemistry, Switzerland

IntroductionIn January 2006, size segregated measurements and analysis of the chemical composition of PM10 samples, collected twice daily with Berner type impactors, were made to determine its source patterns. The measurements were performed at two sites in Münster, NW Germany. One of the sites was located in the centre of Münster, next to a four- to six- lane main road. The second one was set up in a bird nature protection area 6 km to the North.

ResultsThe mean mass concentration, calculated as the sum of ions plus carbon, was clearly higher at the roadside than in the surrounding (31 µg/m³ to 24 µg/m³]). Between the two sites, there was no significant difference in ion mass concentration, correlation coefficient of 0.92.

AnalysisThe carbon analysis was made with an OCEC Lab Analyser. The main ions (Cl-, NO3

-, SO42-) were analyzed

with an ion chromatograph. NH4+ was detected with a flow

injection analyser and Ca2+, Mg2+, and Na+ with an atom-absorbing spectrometer.

European Aerosol Conference 2007 - September 11, 2007, Salzburg, Austria

Acknowledgement This study was financially and logistically supported by the municipality of Münster, the Biological Station, Rieselfelder Münster, gave logistic support, and data access was granted by the Landesamt für Natur, Umwelt und Verbraucherschutz NRW (former Landesumweltamt NRW). For further information please contact: [email protected]://kli.uni-muenster.de

MethodThe samples were taken with two five stage Berner type impactors. They were collected on Tedlar® foils and on quartz fiber filters (Whatman) taken simultaneously, with sample integration time being 6 hours.

Sample on impactor stage equipped with Tedlar® foil and quartz fibre filter on top

0

5

10

15

20

25

30

January 2006

[µg/

m³]

Münster city

rural surrounding

Comparison of the total analysed ion concentration in January 2006

ConclusionsCarbon made the main difference between the two sites in Münster. The difference between the two sites averages 7 µg/m³, meaning about 23 % coming from traffic and 77% originating from background concentration. In contrast, no clear difference was found between the mean ion concentrations.

0.0

8.0

16.0

24.0

32.0

urban rural

con

cen

trat

ion

g/m

³]

Ammonium Calcium Chloride Magnesium Nitrate Sodium Sulphate Total Carbon

0

0.2

0.4

0.6

0.8

1

Calcium Chloride Magnesium Sodium

[µg

/m³]

urban day

urban night

rural day

rural night

0

2

4

6

8

Ammonium Nitrate Sulphate

[µg

/m³]

urban day

urban night

rural day

rural night

The main difference between these sites was caused by carbon, due to traffic and other combustion processes like domestic heating. Daytime values were significantly higher than the concentrations during nighttime.

There were slight differences in ion concentrations. Additional NaCl lead back to de-icing salt in the city. The accesorily calcium at the roadside is due to dust dispersion from road traffic.

The secondary ions NH4- and NO3

- increased during nighttime due to the light sensitive reactions of nitrogen. NO2 is not photolyzed during night, and so can react with OH forming HNO3. Ammonium was high, compared to other components, which is typicall for sites near agricultual activitiy.

Mean mass concentrations of the ions in January 2006