Multimedia fate of oil spills in a marine environment—An integrated modelling approach

Abstract A fugacity-based methodology is presented to predict the fate of spilled oil in the marine environment. In the proposed methodology, oil weathering processes are coupled with a level IV (dynamic) fugacity-based model. A two-compartment system, comprised of water and sediment, is used to explore the fate of oil in a marine environment. During a spill, oil is entrained into the water column due to natural dispersion, which is considered as the primary input source to the water compartment. The direct input to the sediment compartment is assumed negligible. However, the water column acts as a source to the sediment compartment. Unlike the conventional multimedia modelling approach, the impact area is not predefined. Instead, the oil slick spreading process determines the contaminated area growth. Naphthalene is used as a representative oil compound (an indicator) to demonstrate the application of the methodology. The current study suggests that the water compartment response to the chemical input is faster than the sediment compartment. The major fate processes identified are advection in water and volume growth in the sediment.

[1]  Kevin C Jones,et al.  A dynamic level IV multimedia environmental model: Application to the fate of polychlorinated biphenyls in the United Kingdom over a 60‐year period , 2002, Environmental toxicology and chemistry.

[2]  D Mackay,et al.  Evaporation rate of spills of hydrocarbons and petroleum mixtures. , 1984, Environmental science & technology.

[3]  Rehan Sadiq,et al.  Drilling waste discharges in the marine environment : a risk based decision methodology , 2001 .

[4]  Oil and hydrocarbon spills, modelling, analysis and control , 1998 .

[5]  C. Guedes Soares,et al.  Modeling the fate of oil spills at sea , 1995 .

[6]  David P. Hoult,et al.  Oil Spreading on the Sea , 1972 .

[7]  J. Fay The Spread of Oil Slicks on a Calm Sea , 1969 .

[8]  Clayton D. McAuliffe,et al.  Fate of hydrocarbons discharged at sea , 1989 .

[9]  D. Mackay,et al.  A quantitative water, air, sediment interaction (QWASI) fugacity model for describing the fate of chemicals in rivers , 1983 .

[10]  R. Blackman,et al.  Oil in the sea: Inputs, fates, and effects: National Academy Press, Washington, DC. 1985. ISBN 0-309-03479-5. 601pp , 1986 .

[11]  David P. Hoult,et al.  Oil on the Sea , 1969 .

[12]  M. Mooney,et al.  The viscosity of a concentrated suspension of spherical particles , 1951 .

[13]  null null,et al.  State-of-the-Art Review of Modeling Transport and Fate of Oil Spills , 1996 .

[14]  Mark Reed,et al.  The physical fates component of the natural resource damage assessment model system , 1989 .

[15]  Hsiang Wang,et al.  Modeling of oil evaporation in aqueous environment , 1977 .

[16]  Matthew MacLeod,et al.  Evaluating and expressing the propagation of uncertainty in chemical fate and bioaccumulation models , 2002, Environmental toxicology and chemistry.

[17]  P. Sebastiao,et al.  Weathering of oil spills accounting for oil components , 1970 .

[18]  W. Shiu,et al.  Generic models for evaluating the regional fate of chemicals , 1992 .

[19]  Shinsuke Tanabe,et al.  PCBs and chlorinated hydrocarbon pesticides in Antarctic atmosphere and hydrosphere , 1983 .

[20]  Methods for predicting the physical changes in oil spilt at sea , 1988 .

[21]  Pavlo Tkalich,et al.  A multiphase oil spill model , 2003 .