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The experience from Stockholm city road tax Christer Johansson Lars Burman Tage Jonson Bertil Forsberg Umeå university www.stockholmsforsoket.se
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Exceedances of the PM10 limit value City of Stockholm
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PM10: Stockholm has highest levels in Europe?! PM10 90-percentil AirBase: >700 sites 19 countries CAFE-PM, 2003
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Stockholm trial goals Number of vehicle passages to the inner city should decrease by 10%-15% (morning and evening rush hours) Traffic flows should improve People residing or staying in the inner city should experience improved environment Emissions of NOx, CO2 and PM should be reduced
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Tax for driving in the inner city area 2 km 1 0
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Toll stations TAXES
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Evaluation steps Traffic change & emissions Air quality Environment quality standards 2006 Exposure & health effects Long term exposure if the trial is permanented Meteorology Air quality Calculations Measurements
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Substantial decline in traffic -22 % = -100 000 passages Inner city: 15 % less total vehicle kms Goal was achieved!
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Increased traffic on highway connecting north – south & tunnel connecting east – west
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Mean diurnal cycle in traffic flow with and without tax
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Results – Emissions Decrease in city centre 2006: tonnes/ year % Nitrogen oxides, NOx45-8,5 Carbon monoxide, CO670-14 Particles, PM10 total21-13 ” wear particles19-13 ” exhaust particles1,8-12 Hydrocarbons, VOC110-14 ” benzene3,4-14 Carbon dioxide, CO 2 38 000-13 Goal was achieved!
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Better air quality – particles, PM10 ca 0,5 % increase Street level, city centre 4-8 % decrease Roof level, city centre ca 2 % decrease
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Better air quality – exhaust particles Street level, city centre 5-10 % decrease Roof level, city centre 5-6 % decrease ca 1 % increase
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Better air quality – nitrogen oxides, NOx Street level, city centre 5-10 % decrease ca 1 % increase Roof level, city centre ca 6 % decrease
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Limit values for PM10 and NO2?
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PM10 Comparison w EU-directive STILL EXCEEDED
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NO2 Comparison w EU-directive STILL EXCEEDED
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Exposure calculations Living address, 2003 »Daytime pop have minor impact on mortality effects 100 meter resolution (35x35 km area) As if permanent system Long term exposure - mortality
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Small changes in population mean concentrations
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Expected health effects Exposure- response relations Consistent ER factors for mortality: –Holland, New Zeeland, France: 12%, 13%, 14 % increase per 10 ug/m3 NO2 –Norway (Oslo) 8 % increased mortality per 10 ug/m3 NOx ACS
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Long term mortality effects if Stockholm trials are permanented Reduced exposure based on population weighted decrease of NOx concentrations –Decrease of 0,23 ug/m3 –Expected to give 25 – 30 fewer premature deaths per year
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Cost benefit surplus Cost: SEK 2.6 billion Annual surplus: SEK 760 million Shorter travel times (SEK 600 mill) Increased road safety (SEK 125 mill) Health & Environment (SEK 90 mill) Revenues (SEK 550 mill) 4 years payback time
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Measurements –NO2 –NOx –PM10 Meteorol. Traffic Other –Studs –Road wetness
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Not possible to measure impact of congestion charge on air quality
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Lower PM10 due to meteorology
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PM10 levels 2003, 2004, 2005, 2006
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NOx levels 2003, 2004, 2005, 2006
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NOx Measured local street contributions SVEAVÄGEN HORNSGATAN Extra dieselbuses TRAFIK
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Big impact of congestion tax Compare with other measures Reducing studded tires from 70% to 60% –would give similar reduction in PM10 as congestion tax –But: Congestion tax also reduces ultrafine exhaust particles Increased petrol tax not as effective –Congestion tax reduces levels where most people are being exposed New western/eastern link –Similar reductions in exposure
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Other measures Parking: higher fees/taxes/restrictions Possibly similar effects as congestion charge Environmental zone Mainly exhaust emissions PM10 still a problem Dust binding (spring) Local and short effect on high levels High PM10 lowered Studded tire restrictions No effect on exhaust particles PM10 could be met…
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Conclusions Large traffic reduction Lower emissions Small effect on concentrations Expect big effect on health Cost-effective measure
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