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25th International Meeting on Organic Geochemistry IMOG 2011

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O-61<br />

The significant impact of weathering <strong>on</strong> spilled gulf of Mexico<br />

mc252 oil chemistry and its fingerprinting of samples collected<br />

from the sea surface and shore between May and September<br />

2010<br />

Changrui G<strong>on</strong>g 1 , Alexei Milkov 2 , David Grass 1 , Michael Sullivan 1 , Tomieka Searcy 1 ,<br />

Le<strong>on</strong> Dzou 3 , Pierre-Andre Depret 1<br />

1 BP America, Houst<strong>on</strong>, United States of America, 2 BP Russia, Moscow, Russian Federati<strong>on</strong>, 3 BP Asia<br />

Pacific, Jakarta, Ind<strong>on</strong>esia (corresp<strong>on</strong>ding author:changrui.g<strong>on</strong>g@bp.com)<br />

The spilled Gulf of Mexico MC252 reservoir fluid (oil with<br />

dissolved gas) underwent tremendous changes to its<br />

physical and chemical properties through multiple<br />

processes, including, but not limited to, evaporati<strong>on</strong>,<br />

dissoluti<strong>on</strong>, dispersi<strong>on</strong>, photooxidati<strong>on</strong>, emulsificati<strong>on</strong>,<br />

biodegradati<strong>on</strong> and sedimentati<strong>on</strong>, as it moved al<strong>on</strong>g a path<br />

from the reservoir to the wellhead, then to the water column,<br />

to the sea surface, and in some cases, to the shoreline.<br />

As part of Gulf spill resp<strong>on</strong>se effort, over 1500 samples of<br />

source oil, sea surface slicks, emulsi<strong>on</strong>s, and tarballs were<br />

collected (beginning from early May) for geochemical<br />

fingerprinting (GC, MPLC, Isotope, GCMS, CSIR), and were<br />

interpreted as ―PROBABLY‖, ―MAY BE‖, or ―NOT‖ related to<br />

MC252 oil [1]. Five hundred and thirteen source oil, oil,<br />

emulsi<strong>on</strong>, and tarball samples ―PROBABLY‖ derived from<br />

the MC252 spill available as of Jan 18 th were studied to<br />

understand the relative importance of weathering processes,<br />

and their impact <strong>on</strong> the oil budget at the surface and to<br />

examine the effect of weathering <strong>on</strong> geochemical<br />

parameters of MC252 oil.<br />

In the first part of its path, from reservoir at 18,000 feet<br />

deep to the sea surface, MC252 fluid lost up to 40% of its<br />

weight (mostly gas range and soluble aromatic comp<strong>on</strong>ents).<br />

Phase separati<strong>on</strong> and dissoluti<strong>on</strong> in water were the main<br />

processes resp<strong>on</strong>sible for this mass loss. These processes<br />

substantially removed compounds smaller than C7. A<br />

subsea hydrocarb<strong>on</strong> plume formed by suspended small oil<br />

droplets was identified by multiple scientific survey ships [2]<br />

from the MC252 spill. Respirati<strong>on</strong> by methanotrophs and<br />

other indigenous oil-degrading psychrophilic bacteria has<br />

quickly removed dissolved hydrocarb<strong>on</strong> gas comp<strong>on</strong>ents [3,<br />

4] and higher molecular weight hydrocarb<strong>on</strong>s [5].<br />

Oil droplets that survived the trip from well head to surface<br />

appeared as surface slicks and emulsi<strong>on</strong>s. In the sec<strong>on</strong>d<br />

part of its path, from sea surface to landfall, evaporati<strong>on</strong>,<br />

and, less importantly, dispersi<strong>on</strong> and dissoluti<strong>on</strong>, caused<br />

further depleti<strong>on</strong> totaling up to ~63% of the oil weight<br />

affecting compounds up to C21. In the tar samples analyzed<br />

from the spill significant biodegradati<strong>on</strong> had affected a few<br />

samples at the time of the sample analyses, but will play a<br />

larger role in hydrocarb<strong>on</strong>‘s ultimate fate in the envir<strong>on</strong>ment.<br />

Weathering has a much bigger effect <strong>on</strong> aromatic<br />

comp<strong>on</strong>ents than <strong>on</strong> saturate comp<strong>on</strong>ents due to the higher<br />

solubility of aromatics in water and their susceptibility to<br />

photooxidati<strong>on</strong>. The impact of weathering <strong>on</strong> major aromatic<br />

compound groups decreases from biphenyls to<br />

naphthalenes, to dibenzothiophenes, and to phenanthrenes<br />

(Fig. 1). Higher molecular weight compounds, especially<br />

saturate biomarkers, were more resistant to these<br />

weathering processes. Natural weathering seems to shift<br />

isotopes of aromatic and asphaltene fracti<strong>on</strong>s to slightly<br />

more enriched in 13C, and isotopes of resins to more<br />

negative values (Fig. 2). The depleti<strong>on</strong> of resin isotopes with<br />

weathering might be due to c<strong>on</strong>tinued c<strong>on</strong>versi<strong>on</strong> of<br />

isotopically lighter saturate and aromatic fracti<strong>on</strong>s to resin<br />

fracti<strong>on</strong> during photooxidati<strong>on</strong> [6] and, to a lesser extent,<br />

biodegradati<strong>on</strong>. In additi<strong>on</strong> some comm<strong>on</strong>ly used<br />

geochemical indicator ratios, such as MPI and C23tri/C30H,<br />

are affected by the weathering processes.<br />

Total naphthalenes/total dibenzothiophenes<br />

100<br />

10<br />

1<br />

0.1<br />

Source oil Weathered oils<br />

0.01<br />

0.01 0.1 1 10 100<br />

nC17/nC35<br />

Figure 1. A decreasing ratio of total naphthalenes to total<br />

dibenzothiophenes with increasing weathering as indicated by<br />

decreasing nC17/nC35 ratios (nC35 c<strong>on</strong>servative during weathering)<br />

delta C13 of resin fracti<strong>on</strong><br />

-25.8<br />

-26<br />

-26.2<br />

-26.4<br />

-26.6<br />

-26.8<br />

-27<br />

-27.2<br />

-27.4<br />

Source oil Weathered oils<br />

-27.6<br />

0.01 0.1 1 10 100<br />

nC17/nC35<br />

Figure 2. A depleti<strong>on</strong> in C13 for resin fracti<strong>on</strong> isotope values with increasing<br />

weathering<br />

References<br />

[1] Milkov et al. (<strong>2011</strong>) <strong>IMOG</strong> abstract volume<br />

[2] Camilli et al. (2010) ScienceExpress. 19 Aug 2010<br />

[3] Valentine et al. (2010) ScienceExpress. 16 Sept 2010<br />

[4] Kessler et al. (<strong>2011</strong>) ScienceExpress. 6 Jan <strong>2011</strong><br />

[5] Hazen et al. (2010) ScienceExpress. 26 Aug 2010<br />

Dutta T.K. and S. Harayama, (2000) Envir<strong>on</strong>. Sci. Technol. 34, 1500-1505<br />

122

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