Abstract

Abstract. Land-based emissions of air pollutants in Europe have steadily decreased over the past two decades, and this decrease is expected to continue. Within the same time span emissions from shipping have increased in EU ports and in the Baltic Sea and the North Sea, defined as SECAs (sulfur emission control areas), although recently sulfur emissions, and subsequently particle emissions, have decreased. The maximum allowed sulfur content in marine fuels in EU ports is now 0.1%, as required by the European Union sulfur directive. In the SECAs the maximum fuel content of sulfur is currently 1% (the global average is about 2.4%). This will be reduced to 0.1% from 2015, following the new International Maritime Organization (IMO) rules. In order to assess the effects of ship emissions in and around the Baltic Sea and the North Sea, regional model calculations with the EMEP air pollution model have been made on a 1/4° longitude × 1/8° latitude resolution, using ship emissions in the Baltic Sea and the North Sea that are based on accurate ship positioning data. The effects on depositions and air pollution and the resulting number of years of life lost (YOLLs) have been calculated by comparing model calculations with and without ship emissions in the two sea areas. In 2010 stricter regulations for sulfur emissions were implemented in the two sea areas, reducing the maximum sulfur content allowed in marine fuels from 1.5 to 1%. In addition ships were required to use fuels with 0.1 % sulfur in EU harbours. The calculations have been made with emissions representative of 2009 and 2011, i.e. before and after the implementation of the stricter controls on sulfur emissions from 2010. The calculations with present emissions show that per person, an additional 0.1–0.2 years of life lost is estimated in areas close to the major ship tracks with current emission levels. Comparisons of model calculations with emissions before and after the implementation of stricter emission control on sulfur show a general decrease in calculated particle concentration. At the same time, however, an increase in ship activity has resulted in higher emissions of other components, and subsequently air concentrations, in particular of NOx, especially in and around several major ports. Additional model calculations have been made with land-based and ship emissions representative of year 2030. Following a decrease in emissions from all sectors, air quality is expected to improve, and depositions to be reduced. Particles from shipping are expected to decrease as a result of emission controls in the SECAs. Further controls of NOx emissions from shipping are not decided, and calculations are presented with and without such controls.

Highlights

  • Maritime transport is an important sector in Europe that enables trade and contacts between all the European nations

  • In order to calculate the effects of ship emissions in the Baltic Sea and the North Sea, several model runs have been made with the EMEP model

  • Our model calculations show that these emission reductions already have had positive effects on air pollution and deposition

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Summary

Introduction

Maritime transport is an important sector in Europe that enables trade and contacts between all the European nations. In the same time span modest regulations have been implemented for emissions from international sea shipping Both the North Sea and the Baltic Sea are defined by IMO (International Maritime Organization) as SECAs (sulfur emission control areas). Brandt et al (2013) looked at the effects of air pollution from international shipping on air pollution and health on Northern Hemisphere scale to regional northern European scales They calculate a 36 % reduction in health-related external costs from between the years 2000 and 2020 as a result of emission reductions in the North Sea and the Baltic Sea. Within the same time frame, health-related external costs will increase in Europe as a whole due to an expected increase in ship traffic. The cold and dry winter resulted in PM2.5 and PM10 concentrations somewhat higher than expected from the long-term trend alone (Tsyro et al, 2012)

Present and future emissions
EMEP model runs – model setup
Ship emissions in the Baltic Sea and the North Sea
Model results
Present situation
Effects of North Sea and Baltic Sea 2009 ship emissions
Calculated effects of changes in ship emissions from 2009 to 2011
Calculated effects of Baltic Sea and North Sea ship emissions in 2030
Conclusions
Findings
Cost and effects: some final remarks
Full Text
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