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25th International Meeting on Organic Geochemistry IMOG 2011

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P-060<br />

Biomarkers parameters used to assessment of petroleum<br />

biodegradati<strong>on</strong> under laboratory c<strong>on</strong>diti<strong>on</strong>s<br />

Georgiana Feitosa da Cruz 1 , Eugênio Vaz dos Santos Neto 2<br />

1 North Fluminense State University/Petroleum Engineering and Explorati<strong>on</strong> Laboratory (UENF/LENEP),<br />

Macaé, Brazil, 2 Leopoldo Américo Miguez de Mello Center for Research and Development (CENPES), Rio<br />

de Janeiro, Brazil (corresp<strong>on</strong>ding author:geofec@gmail.com)<br />

Biodegradati<strong>on</strong> geochemical parameters based <strong>on</strong><br />

the sequential removal of biomarkers are comm<strong>on</strong>ly<br />

applied to indicate the preference metabolic of<br />

degradati<strong>on</strong> of the aerobic and anaerobic<br />

microorganisms 1 . The reliable biomarker<br />

interpretati<strong>on</strong> about these informati<strong>on</strong> are usually<br />

based <strong>on</strong> multiple biomarker parameters which should<br />

be resistant to sec<strong>on</strong>dary processes, such as<br />

biodegradati<strong>on</strong> 2 . In this sense, the aim of this study<br />

was to investigate the biomarker parameters that are<br />

influenced by biodegradati<strong>on</strong> process under<br />

laboratory c<strong>on</strong>diti<strong>on</strong>s. For this we use the following<br />

ratios: Carb<strong>on</strong> Preference Index (CPI), pristane/nC17<br />

and phytane/nC18, pristane/phytane (Pr/Ph), C28 and<br />

C29 tricyclic terpanes (22R + 22S) to C35 17�(H),<br />

21�(H)-homohopane (22R + 22S) (C28TT/C35Ho and<br />

C29TT/C35Ho ), C35 17�,21�(H)-homohopane (22R +<br />

22S) to C30 17�,21�(H)-hopane (C35Ho/C30H), C27<br />

18�(H)-22,29,30-trisnorneohopane (Ts) to C27<br />

17�(H)-22,29,30-trisnorhopane (Tm) (Ts/Tm), C35 to<br />

C31-C35 homohopane (22R + 22S) (Homohopane<br />

Index, HI), C27, C28,C29 ��� (20R + 22S) and ���<br />

(20R + 22S) steranes to C29-C33 17�(H)-hopanes<br />

(20R + 22S) (sterane/hopane) and C30-C34 25norhopanes<br />

to C31-C35 hopanes ( 25-NH ratio).<br />

The samples were collected from the Pampo field in<br />

the southern part of the Campos Basin. They were<br />

generated from the Lagoa Feia Formati<strong>on</strong> source rock<br />

in differ temperature and depth, allowing a variable<br />

level of oil degradati<strong>on</strong> (oil A, 82 ºC; 2405–2588 m<br />

and oil B, 71 ºC; 1988–2222 m).<br />

The results showed that in aerobic c<strong>on</strong>diti<strong>on</strong>s<br />

occurred progressive removal of even carb<strong>on</strong><br />

numbered n-alkanes, increase of ratio Pr/nC17<br />

Ph/nC18 and decrease in the ratio Pr/Ph. It is<br />

comm<strong>on</strong>ly accepted that odd number n-alkane<br />

preference is associated with low oil thermal maturity,<br />

however these experimental data reveal that the<br />

alkane carb<strong>on</strong> number predominance can change<br />

with the type of biodegradati<strong>on</strong> and should be<br />

interpreted with cauti<strong>on</strong>. In additi<strong>on</strong>, there was an<br />

increase of ratios C28 and C29TT/C35Ho, (Fig. 1),<br />

sterane/hopane, 25-NH, revealing a preferential<br />

depleti<strong>on</strong> of R C35 hopane in relati<strong>on</strong> to tricyclic<br />

terpane, of hopane in relati<strong>on</strong> to sterane and<br />

enrichment of 25-NH.<br />

Fig. 1. Plot of C28TT/C35Ho ratio during biodegradati<strong>on</strong><br />

process.<br />

The homohopane index decrease showing that C35<br />

is more biodegradable than C31-C34 homohopanes.<br />

Unlike what occurred under aerobic c<strong>on</strong>diti<strong>on</strong>s,<br />

anaerobic c<strong>on</strong>sortium showed greater susceptibility to<br />

biodegradati<strong>on</strong> of odd numbered n-alkanes, decrease<br />

of ratios C28 and C29TT/C35Ho, sterane/hopane, 25-<br />

NH and increased of homohopane index. The<br />

geochemical parameters calculated from mixed<br />

c<strong>on</strong>sortium revealed that there was joint acti<strong>on</strong><br />

between aerobic and anaerobic c<strong>on</strong>sortia, as<br />

expected.<br />

A comparative biodegradati<strong>on</strong> of terpanes,<br />

hopanes, 25-norhopanes and steranes under aerobic<br />

and anerobic c<strong>on</strong>diti<strong>on</strong>s indicated that some of the<br />

c<strong>on</strong>troversial biomarker parameters can be easily<br />

explained by taking into c<strong>on</strong>siderati<strong>on</strong> the microbiota<br />

and oxygen c<strong>on</strong>tent.<br />

Acknowledgment<br />

Unicamp, Capes, Finep, Petrobrás and Profa Dra Anita J.<br />

Marsaioli.<br />

[1] da Cruz, G. F., Santos Neto, E. V. & Marsaioli, A. J.<br />

(2008) <strong>Organic</strong> <strong>Geochemistry</strong> 39, 1204-1209.<br />

[2] Peters, K.E., Walters, C.C., Moldowan, J.M., 2005. The<br />

Biomarker Guide, sec<strong>on</strong>d ed. Cambridge University Press,<br />

Cambridge, UK.<br />

206

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