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25th International Meeting on Organic Geochemistry IMOG 2011

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P-343<br />

Effective diffusivities of CO2 and associated noble gases in<br />

impermeable shale caprocks of an EOR-CO2 field<br />

Caroline Magnier 1 , Alain Prinzhofer 1 , Eric Flauraud 1 , Sophie Giannesini 1,2<br />

1 IFP New Energy, Rueil Malmais<strong>on</strong>, France, 2 IPGP, Paris, France (corresp<strong>on</strong>ding<br />

author:caroline.magnier@ifpen.fr)<br />

Present research <strong>on</strong> CCS (Carb<strong>on</strong> Capture and<br />

Storage) is c<strong>on</strong>cerned <strong>on</strong> mitigati<strong>on</strong> opti<strong>on</strong>s for the<br />

increasing atmospheric CO2 c<strong>on</strong>centrati<strong>on</strong>s. The<br />

petroleum industry is studying different liabilities for<br />

the injecti<strong>on</strong> of acid gases in geological structures,<br />

deep saline aquifers or depleted petroleum reservoirs.<br />

Some of the opti<strong>on</strong>s are thought for permanent<br />

storage if and when a good efficiency of seal rocks is<br />

proven to acid gas mobility. In that respect, recent<br />

experimental studies have been described that<br />

estimate gas migrati<strong>on</strong> distances in overlying low<br />

permeability cap rocks when CO2 gas, dissolved or<br />

not, plumes upward in geological sediments by<br />

diffusi<strong>on</strong> or advecti<strong>on</strong> flow, through faults or leaking<br />

wells.<br />

If shales and limest<strong>on</strong>es sediments are mostly<br />

encountered as seals above hydrocarb<strong>on</strong><br />

accumulati<strong>on</strong>s and over CO2 potential storage<br />

reservoirs, it is because shales are impermeable<br />

natural barriers. This is <strong>on</strong>e of the reas<strong>on</strong>s why it is<br />

important to assess their capacity to remain<br />

impermeable to fluids, regardless of what is injected<br />

in the underlying cavities.<br />

Experiments <strong>on</strong> clays were c<strong>on</strong>ducted <strong>on</strong> different<br />

rock sediments of an EOR-CO2 field to investigate<br />

the transport by diffusi<strong>on</strong> of CO2 and noble gases in<br />

water saturated pore networks. Effective diffusivities<br />

for each gases were obtained by a model and<br />

compared as a functi<strong>on</strong> of the rock type.<br />

pressure<br />

gauge<br />

pressure<br />

gauge<br />

CO 2 +<br />

noble<br />

gases<br />

parent<br />

other gas<br />

daughter<br />

sampling<br />

z<strong>on</strong>e<br />

Rock sample<br />

sampling<br />

z<strong>on</strong>e<br />

sample<br />

primary / sec<strong>on</strong>dary<br />

vacuum<br />

sample<br />

primary / sec<strong>on</strong>dary<br />

vacuum<br />

Figure 1: The experimental setup for measuring effective<br />

diffusivities of gases in saturated pores<br />

The experimental setup c<strong>on</strong>sists of a stainless steel<br />

reactor with separate gas reservoirs (parent/daughter)<br />

with volumes of 175 cm 3 filled and put at near equal<br />

pressures.<br />

A gas is mobile with a same flow rate in a given rock<br />

type regardless of the porosity while a gas producti<strong>on</strong><br />

is inversely proporti<strong>on</strong>al to the thickness of the<br />

sample (Figure 2).A gas is mobile with a same flow<br />

rate in a given rock type regardless of the porosity<br />

while a gas producti<strong>on</strong> is inversely proporti<strong>on</strong>al to the<br />

thickness of the sample (Figure 2).<br />

The dissolved CO2 gas migrated differently in the<br />

natural clays. The lowest CO2 retenti<strong>on</strong> was found in<br />

caprocks 1 with a Dw/Deff ratio between 15-18 while<br />

caprock 2 or caprocks 3 (B-45) have greater CO2<br />

retenti<strong>on</strong>, with Dw/Deff ratios at 30 and 45 respectively.<br />

Noble gases followed a decreasing mobility from<br />

helium, ne<strong>on</strong>, arg<strong>on</strong> and krypt<strong>on</strong> respectively,<br />

krypt<strong>on</strong> being very much more retained.<br />

% CO2 PRODUCTION<br />

20<br />

15<br />

10<br />

5<br />

0<br />

Caprock 1 (B-419)<br />

B-419 5 mm<br />

B-419 10.2 mm<br />

B- 419 12.6 mm<br />

0 500 1000 1500 2000<br />

TIME (HRS)<br />

Figure 2: CO2 producti<strong>on</strong> vs. time in a shaly caprock sample<br />

The effective diffusivity of helium was found to<br />

be equal to the rocks tortuosity.<br />

From such results, larger scale simulati<strong>on</strong>s of<br />

gas flows of CO2 associated with inert tracers<br />

with effective diffusi<strong>on</strong> rates or ratios of diffusi<strong>on</strong><br />

rates between gas compounds in a given rock<br />

type are now c<strong>on</strong>sidered in order to attempt to<br />

quantify leakage amounts CO2 in aquifers.<br />

% CO2 PRODUCTION<br />

20<br />

15<br />

10<br />

5<br />

0<br />

0 20 40 60 8<br />

t Dw /L 2 (ADIMENSIONAL)<br />

474<br />

B-419 5 mm<br />

B-419 10.2 mm<br />

B- 419 12.6 mm

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