Air pollution from ships in ports: The socio-economic benefit of cold-ironing technology

Abstract The global environmental impact of air pollution from international shipping is increasing despite regulatory measures to curb the rise. According to European Environmental Agency forecasts, NO x emissions from international shipping in European waters are projected to increase and could be equal to that of land-based sources by 2020. Since 2010, the sulphur content in fuel used by hoteling vessels in EU ports has been subject to EU directive 2005/33/EC, which requires a maximum sulphur content of 0.1%. For gas oil, this requirement has applied since 2008. This paper addresses the socioeconomic impact of harmful air emissions from hoteling cruise ships with special emphasis on NO x , SO x and Particulate Matter (PM). The aim of the paper is to quantify the socioeconomic benefit from the perspective of society in terms of external health cost by offering a cost-benefit analysis of the potential positive effect of introducing cold-ironing technology at the new cruise ship pier in Copenhagen, Denmark.

[1]  Carsten Ambelas Skjøth,et al.  Assessment of health-cost externalities of air pollution at the national level using the EVA model system , 2009 .

[2]  Ismir Fazlagic,et al.  Shore-side power supply - a feasibility study and a technical solution for an on-shore electrical infrastructure to supply vessels with electrical power while in port , 2008 .

[3]  J. Christensen,et al.  Investigating the sources of synoptic variability in atmospheric CO2 measurements over the Northern Hemisphere continents: a regional model study , 2004 .

[4]  Allan Gross,et al.  Assessment of past, present and future health-cost externalities of air pollution in Europe and the contribution from international ship traffic using the EVA model system , 2013 .

[5]  Martin Stendel,et al.  Impacts of climate change on air pollution levels in the Northern Hemisphere with special focus on Europe and the Arctic , 2008 .

[6]  Philippe Ciais,et al.  Comparing atmospheric transport models for future regional inversions over Europe - Part 1: mapping the atmospheric CO2 signals , 2006 .

[7]  Reinhard Mechler,et al.  The Extension of the RAINS Model to Greenhouse Gases , 2004 .

[8]  Fabio Ballini,et al.  The development of a decision making framework for evaluating the trade-off solutions of cleaner seaborne transportation , 2015 .

[9]  L. M. Frohn,et al.  Simulating spatiotemporal variations of atmospheric CO2 using a nested hemispheric model , 2002 .

[10]  Zahari Zlatev,et al.  Operational air pollution forecasts from European to local scale , 2001 .

[11]  Majid Ezzati,et al.  For Personal Use. Only Reproduce with Permission from the Lancet Publishing Group , 2022 .

[12]  R. Friedrich,et al.  Environmental external costs of transport , 2001 .

[13]  M. Benarie The RAINS model of acidification: edited by J. Alcamo, R. Shaw and L. Hordijk, Kluwer Academic Publishers, Dordrecht, Netherlands 1990, 402 pp. Price: Dfl. 200.00, US$ 117.50 , 1991 .

[14]  J. Christensen The Danish Eulerian Hemispheric Model : A three-dimensional air pollution model used for the Arctic , 1997 .

[15]  G. M. Hidy,et al.  The Health Relevance of Ambient Particulate Matter Characteristics: Coherence of Toxicological and Epidemiological Inferences , 2006, Inhalation toxicology.

[16]  Allan Gross,et al.  Modelling the impacts of climate change on tropospheric ozone over three centuries , 2011 .

[17]  L. M. Frohn,et al.  Modelling of Mercury in the Arctic with the Danish Eulerian Hemispheric Model , 2004 .

[18]  Bang Quoc Ho,et al.  Urban Air Pollution , 1994 .