Trends in NOx and NO2 emissions from road traffic in Great Britain

Abstract In this paper we have compared detailed road traffic NOx emissions with the equivalent trends in ambient roadside NOx measurements. This was undertaken separately in Great Britain and London, for all of the major roads, and by road type and location. The emissions trends were created using different emissions factors, those used in UK emissions inventories (Base case), the Swiss-German handbook (HBEFA), and those created from recent remote sensing measurements in the UK (RSD). An alternative assumption for use of Selective Catalytic Reduction (SCR) in the articulated Heavy Goods Vehicle (HGV) fleet was also tested. For all scenarios traffic flows, speeds and vehicle age were kept constant. Comparison between the emissions scenarios in Great Britain showed that by 2009, NOx emissions estimates from road traffic could be as much as 25% greater than current UK estimates and 31% greater in London. The RSD emissions inventory gave the smallest downward trend in NOx emissions, from 2004 to 2009, of between 3 and 4%/year and this compared with a reduction of ∼6%/year from the Base Case and HBEFA scenarios. All scenarios compared poorly with roadside NOx measurement trends from UK sites, which typically reduce by between 1% and 2%/year. We have shown that the differences in NOx emissions trends were driven, partially at least, by the relative contribution from light duty diesel vehicles. An analysis from 2700 NOx measurement sites throughout Europe has shown that this problem is unlikely to be limited to the UK, and identifies a difficulty in meeting EU limit values for NO2, obligations under the National Emission Ceilings Directive ( NECD, 2001 ) and the Gothenburg Protocol ( UNECE, 1999 ) and for forecasting future changes in PM2.5.

[1]  G. Velders,et al.  Higher than expected NOx emission from trucks may affect attainability of NO2 limit values in the Netherlands , 2011 .

[2]  L. Cárdenas,et al.  UK greenhouse gas inventory 1990 to 2006: annual report for submission under the Framework Convention on Climate Change , 2006 .

[3]  J. Stedman,et al.  Recent trends and projections of primary NO2 emissions in Europe , 2009 .

[4]  S Latham,et al.  Emission factors 2009: Report 1 - a review of methods for determining hotexhaust emission factors for road vehicles , 2009 .

[5]  James Tate,et al.  Recent evidence concerning higher NOx emissions from passenger cars and light duty vehicles , 2011 .

[6]  Stefan Hausberger,et al.  Trend of vehicle emission levels until 2020 – Prognosis based on current vehicle measurements and future emission legislation , 2009 .

[7]  D. Carslaw Evidence of an increasing NO2/NOX emissions ratio from road traffic emissions , 2005 .

[8]  Karl Ropkins,et al.  openair - An R package for air quality data analysis , 2012, Environ. Model. Softw..

[9]  W. Cleveland Robust Locally Weighted Regression and Smoothing Scatterplots , 1979 .

[10]  Ian Mudway,et al.  The impact of the congestion charging scheme on air quality in London. Part 1. Emissions modeling and analysis of air pollution measurements. , 2011, Research report.

[11]  Robert Joumard,et al.  Characterizing real unit emissions for light duty goods vehicles , 2003 .

[12]  Rf Phalen,et al.  Cleaning the Air , 2020, Methods in Inhalation Toxicology.

[13]  D. Parrish Critical evaluation of US on-road vehicle emission inventories , 2006 .

[14]  Kenth Andréasson,et al.  Evaluation of the COPERT III emission model with on-road optical remote sensing measurements , 2004 .

[15]  Stefan Hausberger,et al.  Emission factors for heavy-duty vehicles and validation by tunnel measurements , 2003 .

[16]  Michel André,et al.  Analysis and modelling of the pollutant emissions from European cars regarding the driving characteristics and test cycles , 2009 .

[17]  S Latham,et al.  Emission factors 2009: Final summary report , 2009 .

[18]  Michel André,et al.  The ARTEMIS European driving cycles for measuring car pollutant emissions. , 2004, The Science of the total environment.