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Carbon Dioxide Storage Research: a UK PerspectiveAndy Chadwick – British Geological Survey
Presentation to the Coal Authority, Mansfield, 14 April 2015© NERC All rights reserved
The UKCCS Research Centre (UKCCSRC)
The UK Carbon Capture and Storage Research Centre (UKCCSRC) leads and coordinates a programme of underpinning research on all aspects of carbon capture and storage (CCS) in support of basic science and UK government efforts on energy and climate change. The Centre brings together over 240 of the UK’s world-class CCS academics and provides a national focal point for CCS research and development.
http://www.ukccsrc.ac.uk
Centre funding
• Initial core funding for the UKCCSRC is provided by £10M from the Engineering and Physical Sciences Research Council (EPSRC) as part of the RCUK Energy Programme
• This is complemented by £3M in additional funding from the Department of Energy and Climate Change (DECC) to establish new capital facilities that will support innovative research
•• 10 partner institutions have contributed £2.5M
How the Centre works
The Centre is a virtual network where academics, industry, regulators and others in the sector collaborate to analyse problems, devise and carry out world-leading research, and share delivery.
• We do this by working through networksto deliver impact
• We bring people and projects togetherto shape capability
• We fund innovative research to develop leaders
Centre Membership
• Centre members are UK academics with a track record in CCS research: they are either• Principal Investigators or Co-Investigators on CCS research
grants, or• Have relevant CCS publications
• The Centre has Associate Membership for individuals from business/industry, government/policy and NGOs
• The Centre also has an Early Career Researcher (ECR) membership for postgraduate research students, post-doctoral staff and new lecturers, supported by a comprehensive ECR programme
www.ukccsrc.ac.uk/membership
UK offshore storage potential
Sleipner ~18 years storage> 15 million tonnes
(1 - 5 powerstation.years)Potentially giant storage facility
• Geology• CO2 sources
UK capacity and the DECC Commercialisation Programme
Peterhead - Goldeneye
Peterhead - Goldeneye
~1 Mt / year CO2 for 10 – 15 years
CO2 from existing 400 MW gas turbine (retrofitted capture unit)
Storage in Goldeneye FieldDepleted gas condensate field Captain Sandstone (+aquifer)Depth ~ 2600 m
[Images courtesy Shell]
UK capacity and the DECC Commercialisation Programme
White Rose
White Rose
~ 2 Mt / year CO2 for 10 years
CO2 from new oxyfuel power-plant adjacent to Drax
Storage in structural closure in the southern North Sea
Bunter Sandstone (saline aquifer)
Depth ~ 1000 m
Contents ………..
1. UK storage capacity / site characterisation
2. Storage performance research
• Monitoring and verification• Long-term stability
Contents ………..
1. UK storage capacity / site characterisation
2. Storage performance research
• Monitoring and verification• Long-term stability
© NERC All rights reserved
Building a static model
Seismic mapping
data courtesy Schlumberger
3D reservoir model (pore-space volumetrics)
Depleted fields
Saline aquifers
‘Supercritical fluid’Buoyant (density ~30 – 80% water)
Mobile (viscosity ~5% water)Immiscible with water
Compressible (25x water)
Various processes ……
• CO2 - water interactions (2-phase flow)• CO2 - rock interface interactions
• Control CO2 distribution…… and also pressure increase
Reservoir processes
CO2
water
CO2water
Free CO2
CO2 injection ends (50 Mt)CO2 injection starts
Formation pressure
Dynamic modelling of a single site
Stratigraphical complexity and scaling
Heterogeneity
• Horizontal bedding• Lateral pinch-outs• Cross-cutting structures• Faults
• Fluid flow modifiers
Rock heterogeneities on scales of mm, cm, m, kmDynamic model cells are metres to tens of metres across
Open aquifer
CO2
no water expulsion: ∆P largeaquifer water expelled: ∆P small
Structural complexity - flow boundaries
Closed aquifer
Flow boundaries in the Bunter Sandstone
Injection simulations
12 wells injecting 1650 Mt of CO2 over 50 years
CO2 saturation after 50 years
Injection simulations
open boundary
closed boundary
pressure limit75% lithostatic
pressure limit75% lithostatic
Vulnerable areas around injection wells and around shallow closures
Limiting pressures
∆P
Empirical Theory
Contents ………..
1. UK storage capacity / site characterisation
2. Storage performance research
• Monitoring and verification• Long-term stability
Monitoring for conformance and containment
• Conformance: that the storage site is behaving as predicted and site-specific processes are sufficiently well-understood to rule out significant adverse future outcomes.
• Containment: no evidence that the storage site is leaking in the subsurface or emitting CO2 to the surface.
sea-bed
container
leakage
emission
top of the Storage Complex
Storage at Sleipner
1994 (pre‐injection) 2006 (8.4 Mt)
reservoirCO2 plume
Operated by Statoil and partners
World’s longest running CO2 storage project
Injecting since 1996• 15 million tonnes now stored
Reservoir similar to many central and northern North Sea aquifers
1994 2006
Monitoring at Sleipner
3D time-lapse seismic
1994 (baseline)1999 2001 2002 2004200620082010
Seabed gravimetry
2002200520092012
1994 2006
seabed
reservoir CO2 plume
1000 m
3D time-lapse seismic provides spatially continuous and spatially uniform coverage of the subsurface volume of the storage footprint
~ 3000 m
~ 25
0 m
Reservoir top
Reservoir base
Reservoir sand
Sleipner time-lapse 3D seismics
vertical section
plan view
Conformance – CO2 distribution
Demonstrated realistic representation of CO2 in situQuantitatively robust (~95% of known injected free CO2)
Calculated CO2 distribution (3D)Plume image 1999
2004
2008
2006
Mass of CO2 injected (Mt)
Inte
grat
ed v
eloc
ity p
ushd
own
(m2 s
)
20011999
Conformance – CO2 distribution
CO2 separated from natural gasRe-injected into saline aquifer Commenced 1996~ 12 Mt now stored
~ 1000 metres
2006
CO2 plume
2006 zoom
topmost CO2 layer
Time-lapse 3D seismics
Conformance - observed vs modelled
seabed
top reservoir Topmost CO2 layer
Buoyant gravity flow
2001200420062008
Growth of topmost layer
CO2
Conformance - observed vs modelled
2001200420062008
observed layer growth
simulated layer growth
Requires high CO2 mobility
• Very high reservoir permeability?• Warmer CO2?
observed layer growth
Conformance - observed vs modelled
>100000 seismic traces
No down-hole pressure measurement at Sleipner
For simple reservoir with no lateral flow barriers modelled ∆P ~ 1 bar by 2006
Conformance - pressure
fluid pressure increase
∆P
Bulk/shear modulusdecrease
Vp, Vs decrease
[thickness increase
- pore compressibility] tr
avel
-tim
e T
Seismic pressure response of a clastic reservoir
T +∆
T
t1
1994
t2
2006
∆T = t2 – t1
For noise-free data, travel-time resolution for a single trace <1 ms
~116500 traces
Measuring ∆T
∆T 2006 – 1994
>100000 seismic traces
repeatability mismatches (noise)
Calculating ∆T (noise-free)
+0.1MPa
+ 0.5 MPa
+ 1 MPa
Pressure from time-shifts
+ 0.1 MPa
+ 0.5 MPa
+ 1.0 MPa
‘noise-free’ responsesto pressure increase….. convolved with
repeatability noise
∆P < 0.1 MPa (1 bar)
Pressure monitoring at Snøhvit
Pressure non-conformance …..lowside capacity
Faulted reservoir
Snøhvit time-lapse seismics
Pressure footprint from spectral response
2006
CO2 plume
overburden
seabed
Containment monitoring at Sleipner
Statistical analysis of changes in overburden due to out-of-reservoir CO2
Detectability:
~ 2000 tonnes at top reservoir (dense-phase)~ 300 tonnes in shallow overburden (gas)
< 0.01% of 20 Mt storage project
Containment monitoring at and above the seabed
1. Bubbles
2. Chemical changes in the water-column (e.g. pH)
3. Changes of seabed character (new pockmarks, algal mats etc)
[Images courtesy CO2ReMoVe and ECO2 projects]
Containment monitoring at and above the seabed
Stationary and mobile monitoring options
Seabed ‘lander’ for in situ gas analysis
Remotely-operated vehicle (ROV)
[Images courtesy CO2ReMoVe and ECO2 projects]
partiallydetected
sampling station
detected
storage footprint
not detected
Containment monitoring at and above the seabed
Possible requirement for large-area coverage (>100 km2)
ETI-MMV Project
Cost-effective large-area surveillance
QICS offshore release experiment
Monitoring tools
Sampling methods
Environmental impacts
Impacts research
Thankyou