Geophysical Monitoring for Geologic Carbon Storage. Группа авторов
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Название: Geophysical Monitoring for Geologic Carbon Storage

Автор: Группа авторов

Издательство: John Wiley & Sons Limited

Жанр: География

Серия:

isbn: 9781119156840

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СКАЧАТЬ pressure effects resulting from supercritical CO2 (scCO2) injection in a sandstone reservoir using 4D reflection seismic data and well logs. They use a 3D prestack seismic data set, two 3D seismic poststack volumes, and a wireline log from the sandstone reservoir, to perform forward modeling and predict reservoir seismic response of fluid substituted CO2 as a component of the pore‐filling fluid mix in a reservoir unit. They use time‐lapse 3D seismic data acquired before and after CO2 injection and postinjection common midpoint stacks to determine regions of possible fluid density and pore pressures signatures. The lateral changes in amplitude versus offset (AVO) can be an indicator of pore‐filling fluid changes. They implement the Aki‐Richards method to model reflected wave amplitudes at increasing offset angles on time‐lapse prestack seismic data from the Cranfield Field, Mississippi, USA. They present results on the effects of seismic‐wave reflectivity caused by the injection of CO2 in a sandstone reservoir at Cranfield, and predict the fluid effects of CO2 presence in the reservoir by applying fluid substitutions to produce reservoir property models and compare these effects with an actual 4D seismic survey.

      Migration of CO2 at a geologic carbon storage site causes subsurface mass redistribution. Lower density CO2 displaces higher density brine, which results in reduction of the bulk formation density. Time‐lapse gravity monitoring is sensitive to the bulk density changes. Gravity sensors can be deployed on the ground surface or in a borehole or on the seafloor. When CO2 is present at a subsurface depth of greater than 700 m, CO2 exists in a supercritical state and its density ranges from 0.25 to 0.70 g/cm3. The density contrast between brine and CO2 in a CO2 storage site is often less than 0.5 g/cm3.

      In Chapter 14, Appriou and Bonneville introduce the gravity method and discuss its modeling and application to various geologic carbon storage sites. Detection of gravity variations accompanying mass redistributions in the subsurface caused by fluid movements in reservoirs provides a unique means to monitor the dynamics of a carbon sequestration site. With the recent advancement in instrument capabilities, the gravity method provides a promising monitoring technique.

      Because a CO2 storage reservoir is often located at a large depth and spatial resolution of gravity surveys decreases with the depth, there are often limited applications that land surface gravity surveys can provide. To improve the plume resolution, a gravimeter must be located closer to a CO2 plume, either in a borehole or on the seafloor for an offshore geologic carbon storage site. There have been only two gravity monitoring applications at commercial‐scale CO2 storage sites. A seafloor gravity monitoring survey was performed at the Sleipner CO2 storage site in Norway. The high repeatability of 1.1–4.3 μGal in gravity measurements was achieved in a dynamic seafloor environment. Hydrocarbon production is another source of reservoir density change and complicates the gravity interpretation. The gravity anomaly reached tens of μGal after injection of 18 MMT CO2. Gravity monitoring estimated that the mass of CO2 in the storage reservoir agrees with the injected CO2 mass without leakage.

      Compared with seismic monitoring, gravity monitoring is more cost‐effective and may be deployed between repeated seismic surveys if the model predicts a measurable gravity response. Downhole and seafloor gravity monitoring of deep CO2 storage is more effective than surface gravity surveys, which may be better suited for monitoring shallow CO2 leakage.

      The injection of carbon dioxide results in increased resistivity, which may be detected by electrical and EM imaging techniques, such as electrical resistivity tomography, complex resistivity method, magnetotelluric method, controlled source EM, and other EM methods. In Chapter 15, Gasperikova and Morrison present the electrical and electromagnetic (EM) techniques to map the electrical resistivity of the subsurface for monitoring CO2 injection and migration. Both surface and borehole resistivity methods are relatively insensitive to horizontal resistive layers of CO2 plumes. Monitoring with electromagnetic sources at depth shows great promise for detecting and monitoring the emplacement of tabular zones or bodies of resistive CO2. Surface‐based EM techniques with an induction coil source are not suitable for detection of CO2 plumes deeper than 1,000 m.

      Electrical and EM methods can be used to monitor CO2 leakage into the shallow geologic formations. Gas‐phase CO2 increases the bulk electrical resistivity. On the other hand, brine leakage and dissolved CO2 in groundwater decrease the electrical resistivity. Electrical and EM monitoring should account for both effects of fluid salinity and CO2 saturation.

      Electrical resistivity tomography (ERT) is an alternative high‐resolution technique for the shallow aquifer and deep reservoir monitoring. In Chapter 16, Yang and Carrigan describe the ERT method for tracking migration of a supercritical CO2 plume in a deep storage reservoir and for detecting CO2 leakage in a shallow aquifer. With downhole electrodes close to the target of interest, ERT can characterize the temporal and spatial resistivity changes effectively. A resistive supercritical CO2 plume displaces conductive brine and increases the bulk resistivity of storage formation. However, brine leakage and CO2 dissolution in a shallow aquifer lower the bulk resistivity of the formation. They present two case histories to demonstrate the capability of ERT that provides daily tomographic images of CO2 distribution, which complements temporally sparse wireline logs and cross‐well seismic data. The surface ERT method is effective for monitoring shallower than 100 m in depth. The primary challenge of cross‐well ERT is the high cost of using two or more closely spaced monitoring wells to deploy vertical electrode arrays. Single‐well ERT may be used when closely spaced monitoring wells are not available.

      Fluid flow through a porous media can generate electrical potential gradient or streaming potential along the flow path. The self‐potential (SP) technique is a passive electrical monitoring method that measures spontaneous or natural electrical potential from the subsurface. In Chapter 18, Nishi and Ishido introduce the SP monitoring technique. Two SP mechanisms are studied with numerical simulations. The electrokinetic coupling mechanism produces SP caused by changing reservoir conditions such as pressure disturbance from results of reservoir simulation. The geobattery mechanism creates a galvanic cell caused by subsurface electrochemical conditions near a metallic well casing. CO2 injection alters deeper reducing environment and redox potential, which results in an SP anomaly. If a substantial amount of CO2 migrates upward into a shallow fresh water aquifer through a vertical fault and creates substantial pressure disturbances, observable self‐potential measurements caused by electrokinetic coupling would provide a cost‐effective monitoring method СКАЧАТЬ