Characterization of sea surface chemical contamination after shipping accidents.

A contamination survey was conducted after the beaching of the stricken cargo ship MSC Napoli in Lyme Bay on the south coast of Devon (UK). A grid of 22 coastal and offshore stations was sampled to investigate the extent of spilled oil and to screen for chemical contamination, as well as to evaluate the behavior of the oil at the air-sea interface. Samples were collected from the sea surface microlayer (SML) and from subsurface waters (SSW) at each station. The fuel oil spilled (IFO 380) was also analyzed. The determination of oil-related hydrocarbons (aliphatic hydrocarbons, polycyclic aromatic hydrocarbons (PAHs), terpanes, and steranes) and the screening for other harmful chemicals on the inventory of the MSC Napoli in the seawater samples, was performed by PTV-GC/ MS using large volume injection (LVI) techniques. Screening did not reveal the presence of any harmful chemicals other than petroleum-related compounds. Results afforded investigation of oil sources and spatial distributions of total PAH concentrations and enrichments in the sea surface microlayer (SML). Rather than a single source, oil fingerprinting analyses of the samples revealed a mixture of three types of oil: heavy fuel oil, lubricating oil, and a lighter oil (probably diesel oil). Enrichment factors (EF) in the SML (EF = C(SML)/C(SSW)) were calculated and, in the vicinity of the ship, approached 2000, declining with distance away from the wreck. These factors represent approximately a 1000-fold enrichment over typical coastal total PAH enrichments in the SML and reflected a clear petrogenic origin of the contamination (as demonstrated, for example, by a Fl/Pgamma ratio < 1). In addition, the spatial transport and fate (i.e., air-sea exchange processes and water column diffusion) of the oil-related hydrocarbons in the sea surface were investigated. Essentially, near the wreck, the SML was highly enriched in oil forming a visible sheen, both disrupting the normal air-seawater exchange processes and generating a downward diffusion flux of contaminants from the SML to the SSW. This was reflected by a higher occurrence of naphthalene relative to alkyl-naphthalenes in the SSW compared to the SML. The higher concentrations and different sources of oil found in the SML in comparison to those found in the SSW indicate that, if only subsurface water samples are investigated in isolation, the true extent and impact of a spill could be underestimated. It is important to simultaneously evaluate contamination in the sea surface during emergency response.

[1]  J. Albaigés,et al.  Prestige oil spill. III. Fate of a heavy oil in the marine environment. , 2007, Environmental science & technology.

[2]  J. Albaigés,et al.  Occurrence and fate of polycyclic aromatic hydrocarbons in the coastal surface microlayer. , 2007, Marine pollution bulletin.

[3]  M. Fingas,et al.  Forensic fingerprinting of diamondoids for correlation and differentiation of spilled oil and petroleum products. , 2006, Environmental science & technology.

[4]  W. A. Burns,et al.  Optimizing detection limits for the analysis of petroleum hydrocarbons in complex environmental samples. , 2004, Environmental science & technology.

[5]  M. Fingas,et al.  Characterization and identification of the Detroit River mystery oil spill (2002). , 2004, Journal of chromatography. A.

[6]  Oliver Wurl,et al.  A review of pollutants in the sea-surface microlayer (SML): a unique habitat for marine organisms. , 2004, Marine pollution bulletin.

[7]  J. Albaigés,et al.  Evaluation of sampling devices for the determination of polycyclic aromatic hydrocarbons in surface microlayer coastal waters. , 2004, Marine Pollution Bulletin.

[8]  Merv Fingas,et al.  Formation of water-in-oil emulsions and application to oil spill modelling. , 2004, Journal of hazardous materials.

[9]  J. Albaigés,et al.  Fast solid-phase extraction-gas chromatography-mass spectrometry procedure for oil fingerprinting. Application to the Prestige oil spill. , 2004, Journal of chromatography. A.

[10]  M. Fingas,et al.  Development of oil hydrocarbon fingerprinting and identification techniques. , 2003, Marine pollution bulletin.

[11]  S. Stout Applications of petroleum fingerprinting in known and suspected pipeline releases—two case studies , 2003 .

[12]  A. O. Barakat,et al.  Application of Petroleum Hydrocarbon Chemical Fingerprinting in Oil Spill Investigations––Gulf of Suez, Egypt , 2002 .

[13]  Alessandra Cincinelli,et al.  Organic pollutants in sea-surface microlayer and aerosol in the coastal environment of Leghorn—(Tyrrhenian Sea) , 2001 .

[14]  M. Hennion,et al.  Picogram determination of "earthly-musty" odorous compounds in water using modified closed loop stripping analysis and large volume injection GC/MS. , 2001, Analytical chemistry.

[15]  S. Feinstein,et al.  Weathering of fuel oil spill on the east Mediterranean coast, Ashdod, Israel , 2000 .

[16]  K. Burns,et al.  Non-volatile Hydrocarbon Chemistry Studies Around a Production Platform on Australia's Northwest Shelf , 1999 .

[17]  M. Reed,et al.  Oil Spill Modeling towards the Close of the 20th Century: Overview of the State of the Art , 1999 .

[18]  C. Reddy,et al.  GC-MS analysis of total petroleum hydrocarbons and polycyclic aromatic hydrocarbons in seawater samples after the North Cape oil spill , 1999 .

[19]  R. Law,et al.  Polycyclic aromatic hydrocarbons (PAH) in seawater around England and Wales , 1997 .

[20]  Peter S. Liss,et al.  The sea surface and global change , 1997 .

[21]  J. Short,et al.  Introduction to studies on the effects of the (Exxon Valdez) oil spill on early life history stages of Pacific herring, (Clupea pallasi), in Prince William Sound, Alaska , 1996 .

[22]  J. Hellou,et al.  Petroleum biomarkers as tracers of lubricating oil contamination , 1996 .

[23]  Mervin F. Fingas,et al.  A literature review of the physics and predictive modelling of oil spill evaporation , 1995 .

[24]  E. Pelletier,et al.  Environmental factors influencing the biodegradation of petroleum hydrocarbons in cold seawater , 1995 .

[25]  A. Ōkubo,et al.  Turbulence, diffusion and patchiness in the sea , 1994 .

[26]  M. Bícego,et al.  Sunlight-induced compositional alterations in the seawater-soluble fraction of a crude oil , 1992 .

[27]  W. Asher,et al.  The interaction of mechanically generated turbulence and interfacial films with a liquid phase controlled gas/liquid transport process , 1986 .

[28]  J. Hardy The sea surface microlayer: Biology, chemistry and anthropogenic enrichment , 1982 .