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Abstract
The aim of this paper is to investigate the effects of CO2 sequestration on
groundwater abstraction above the storage formation. Large-scale (10Mt/yr) CO2
injection in underlying saline aquifers is considered using a fully
compositional simulator to study the pressure distribution, CO2 leakage and
inter-layer brine flow. Structural, residual and solubility CO2 trapping are
taken into account while the model domain is considered to have no-flow
boundaries to simulate CO2 injection under the context of either pressure not
being able to be dissipate quickly (due to other CO2 injection processes, for
instance) or the formation being self-contained. Changes in salinity are
affected by groundwater abstraction and although not caused by injection
itself, can be magnified by such processes. We also conclude that the time at
which CO2 leakage, pressure perturbations and upward brine flow are at their
peak in overlying aquifers (layers above the injection site) may be
signifi-cantly after injection has ceased (50-150 years in some cases) and
could potentially cause groundwater movements, land sur-face uplift or rock
fracturing long after the injection phase has ended.
Introduction
Current levels of CO2 are around 390ppm (parts per million) (NOAA, 2009)
and a further increase beyond 400-450ppm is likely to cause further climate
changes (Meinshausen, 2006). It has been suggested that carbon capture and
storage (CCS) can help to mitigate this adverse climatic impact (IPCC, 2005,
Houghton, 2001, Jepma & Munasinghe, 1998, Bryant, 1997, Holloway, 1996).
CO2 can be separated and captured from stationary sources such as coal-fired
power stations, transported to a suitable location and subsequently stored
underground as opposed to being emitted into the air.
Different geological storage locations have been considered in literature
such as basalt rocks (McGrail et al., 2006), salt caverns (Dusseault et al.,
2001) and former coal mines (Shi & Durucan, 2005, Wo & Liang, 2005).
The main focus of past and current research, however, has been on oil and gas
fields – either depleted or in the context of enhanced oil recovery (EOR) – and
deep saline formations or aquifers (Holloway et al., 2005) which this paper
will focus on.
A saline aquifer is a geological formation that contains water with dissolved
salts. Because of the high salinity in these formations they are not usually
used as a source of drinking water (U.S. Environmental Protection Agency, 2009)
and hence are considered to be a suitable target for CO2 storage, provided it
can be stored safely over long periods of time. When CO2 is injected into a
geological formation several trapping mechanisms occur at varying timescales,
namely structural and stratigraphic trapping (Lindeberg, 1997), residual or
capillary trapping (van der Meer, 1995, Holt et al., 1995, Law & Bachu,
1996, Spiteri et al., 2008), solubility trapping (Law & Bachu, 1996,
Spycher et al., 2003, Spycher & Pruess, 2005) and mineral trapping (Pruess
et al., 2003, Gunter et al., 2004, Xu et al., 2004, Kumar et al., 2005).
Another, more recent approach, suggested storing CO2 directly as a solid
through hydrate formation (Wright et al., 2008), a process requiring
significantly more research and therefore outside the scope of this paper.
Numerical modeling of CO2 storage has been performed since the early 1990’s
(Holloway, 1996, van der Meer, 1995, Holt et al., 1995, Law & Bachu, 1996,
van der Meer, 1992, van der Meer, 1993, van der Meer, 1996) and, although
computationally expensive, can capture phenomena not considered in analytical
solutions. More recently, researchers have studied near basin-scale systems and
long time frames, applicable to large storage sites (Kumar et al., 2005, Mo
& Akervoll, 2005, Ozah et al., 2005, Akaku, 2008). Research on the basis of
these numerical models has been extended to study the large-scale impact CO2
injection has on groundwater systems and up-dip or overlying fresh water
aquifers, suggesting that especially the pressure distribution and displacement
of brine could have an impact on a much larger scale than the CO2 plume itself
(Nicot, 2008, Birkholzer et al., 2009, Birkholzer & Zhou, 2009).
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