Characteristics and ship traffic source identification of air pollutants in China's largest port

Abstract To characterize the air pollutants in Shanghai Port and identify the contribution from ship traffic emission, field measurements have been conducted in 2011. The trace gases SO 2 , NO 2 and O 3 were monitored and aerosol samples of TSP, PM 2.5 and size-segregated particles were collected in a working area of Shanghai Port. Elements including V, Ni, Al, Fe, Si, Ca, Na, Mg, Mn, Zn, Co, Cr in aerosol samples and heavy fuel oil samples were analyzed. The results revealed that average hourly SO 2 and NO 2 concentrations in Shanghai Port were respectively 29.4 and 63.7 μg m −3 , average daily concentrations of TSP and PM 2.5 were 114.39 and 62.60 μg m −3 , comparable with the ones in Shanghai land area. Ni and V were found enriched in fine particles with averaged concentrations of 80.0 and 14.8 ng m −3 in PM 2.5 respectively. Also ratio of V/Ni in aerosol under summertime airflow was 3.4, very close to the ratio of averaged V and Ni content in international heavy fuel oils used in Shanghai Port. The backward trajectory analysis further revealed that SO 2 , NO 2, and V under coastal airflows were mainly from ship traffic emission. The mean concentration of V was 15.84 ng m −3 under hybrid coastal airflows, much higher than that of 9.84 ng m −3 under continental airflows. Furthermore, V was found to be highly correlated with ship fluxes, and was selected as an indicator of ship traffic emission in Shanghai. The estimated primary PM 2.5 contribution from ship traffic ranged from 0.63 to 3.58 μg m −3 , with an average of 1.96 μg m −3 . This PM 2.5 fraction accounted for 4.23% of the total PM 2.5 in an average level, and reached to a maximum of 12.8%. Furthermore, there could be 64% of primary PM 2.5 contributed by ships in Shanghai Port transported to inland region. Our results suggest that ship traffic has a non-negligible contribution on ambient levels of fine particles and secondary contribution of SO 2 and NO 2 emitted by ships need to be estimated on local and regional scale in future.

[1]  J. Corbett,et al.  Particulate emissions from commercial shipping: Chemical, physical, and optical properties , 2008 .

[2]  Giovanni Lonati,et al.  Air quality impact assessment of at-berth ship emissions: Case-study for the project of a new freight port. , 2010, The Science of the total environment.

[3]  J Wayne Miller,et al.  Primary particulate matter from ocean-going engines in the Southern California Air Basin. , 2009, Environmental science & technology.

[4]  Weichun Ma,et al.  Influence of Continental Outflows on Marine Aerosols over Xiaoyangshan Island in the East China Sea: An Episode of Heavy Air Pollution , 2010 .

[5]  F Belosi,et al.  The direct influence of ship traffic on atmospheric PM2.5, PM10 and PAH in Venice. , 2011, Journal of environmental management.

[6]  J. Fung,et al.  Identification and spatiotemporal variations of dominant PM10 sources over Hong Kong , 2006 .

[7]  D. Dabdub,et al.  Modeling the effects of ship emissions on coastal air quality: A case study of southern California , 2008 .

[8]  Kazuhiko Ito,et al.  Cardiovascular Effects of Nickel in Ambient Air , 2006, Environmental health perspectives.

[9]  Min Hu,et al.  Seasonal variation of ionic species in fine particles at Qingdao, China , 2002 .

[10]  X. Querol,et al.  Source apportionment of PM10 and PM2.5 at multiple sites in the strait of Gibraltar by PMF: impact of shipping emissions , 2011, Environmental science and pollution research international.

[11]  Kan Huang,et al.  Characteristics and sources of air-borne particulate in Urumqi, China, the upstream area of Asia dust , 2008 .

[12]  Daniel Wang,et al.  Identification and characterization of inland ship plumes over Vancouver, BC , 2006 .

[13]  Hiroshi Furutani,et al.  Impact of emissions from the Los Angeles port region on San Diego air quality during regional transport events. , 2009, Environmental science & technology.

[14]  María Cruz Minguillón,et al.  Seasonal and spatial variations of sources of fine and quasi-ultrafine particulate matter in neighborhoods near the Los Angeles–Long Beach harbor , 2008 .

[15]  J. Sodeau,et al.  Sources of ambient concentrations and chemical composition of PM2.5–0.1 in Cork Harbour, Ireland , 2010 .

[16]  Xingying Zhang,et al.  The ion chemistry;seasonal cycle;and sources of PM2.5 and TSP aerosol in Shanghai , 2006 .

[17]  M. Quante,et al.  The contribution of ship emissions to air pollution in the North Sea regions. , 2010, Environmental pollution.

[18]  Paul S. Fischbeck,et al.  Emissions from Ships , 1997, Science.

[19]  J. Kukkonen,et al.  A modelling system for the exhaust emissions of marine traffic and its application in the Baltic Sea area , 2009 .

[20]  Gianni Tinarelli,et al.  Application of a Lagrangian particle model to assess the impact of harbour, industrial and urban activities on air quality in the Taranto area, Italy , 2007 .

[21]  Jeremy Firestone,et al.  Improving spatial representation of global ship emissions inventories. , 2008, Environmental science & technology.

[22]  Alexis K.H. Lau,et al.  Tracking emission sources of sulfur and elemental carbon in Hong Kong/Pearl River Delta region , 2012, Journal of Atmospheric Chemistry.

[23]  Stig Hellebust,et al.  Characterisation of single particles from in-port ship emissions , 2009 .

[24]  Kan Huang,et al.  Chemical characterization of aerosols at the summit of Mountain Tai in Central East China , 2011 .

[25]  Axel Lauer,et al.  Emissions from international shipping: 1. The last 50 years , 2005 .

[26]  Gjermund Gravir,et al.  Emission from international sea transportation and environmental impact , 2003 .

[27]  M. Lippmann,et al.  Residual oil combustion: a major source of airborne nickel in New York City , 2009, Journal of Exposure Science and Environmental Epidemiology.

[28]  James J. Corbett,et al.  Effects of ship emissions on sulphur cycling and radiative climate forcing over the ocean , 1999, Nature.

[29]  Mar Viana,et al.  Chemical tracers of particulate emissions from commercial shipping. , 2009, Environmental science & technology.

[30]  Paul S. Fischbeck,et al.  Emissions from Waterborne Commerce Vessels in United States Continental and Inland Waterways , 2000 .

[31]  Yong-Chil Seo,et al.  Formation of fine particles enriched by V and Ni from heavy oil combustion: Anthropogenic sources and drop-tube furnace experiments , 2007 .

[32]  E. S. Lindgren,et al.  Identification and assessment of ship emissions and their effects in the harbour of Göteborg, Sweden , 2001 .

[33]  Eliseo Monfort,et al.  Source origin of trace elements in PM from regional background, urban and industrial sites of Spain , 2007 .

[34]  P. Hopke,et al.  Source characterization of ambient fine particles at multiple sites in the Seattle area , 2008 .

[35]  Robert McLaren,et al.  Impact of fuel quality regulation and speed reductions on shipping emissions: implications for climate and air quality. , 2011, Environmental science & technology.

[36]  M. Lippmann,et al.  Residual oil combustion: 2. Distributions of airborne nickel and vanadium within New York City , 2010, Journal of Exposure Science and Environmental Epidemiology.

[37]  Wu Ming-yang Site selection and planning of Yangshan deepwater port , 2011 .

[38]  K. H. Wedepohl The Composition of the Continental Crust , 1995 .

[39]  Erin H. Green,et al.  Mortality from ship emissions: a global assessment. , 2007, Environmental science & technology.

[40]  David R. Cocker,et al.  In-use gaseous and particulate matter emissions from a modern ocean going container vessel , 2008 .

[41]  David G. Streets,et al.  An emission inventory of marine vessels in Shanghai in 2003. , 2007, Environmental science & technology.