Monitoring Carbon Dioxide Sequestration in Deep Geological … · 2017-12-05 ·...

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SPE102833,September 26, 2006 SPE ATCE, San Antonio, TX Monitoring Carbon Dioxide Sequestration in Deep Geological Formations for Inventory Verification and Carbon Credits Sally M. Benson Earth Sciences Division Lawrence Berkeley National Laboratory Berkeley, California, 94720 [email protected]

Transcript of Monitoring Carbon Dioxide Sequestration in Deep Geological … · 2017-12-05 ·...

Page 1: Monitoring Carbon Dioxide Sequestration in Deep Geological … · 2017-12-05 · SPE102833,September 26, 2006 SPE ATCE, San Antonio, TX Monitoring Carbon Dioxide Sequestration in

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Monitoring Carbon Dioxide

Sequestration in Deep Geological

Formations for Inventory Verification

and Carbon Credits

Sally M. Benson

Earth Sciences DivisionLawrence Berkeley National Laboratory

Berkeley, California, 94720

[email protected]

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Growing Awareness of the Urgency to Stop

Increasing Atmospheric CO2 Concentrations

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There Are Good Reasons to Begin

Doing Something Now

Ocean

Acidification

Stronger Hurricanes

Rising Sea Levels

Jeff Schmaltz, MODIS Rapid

Response Team NASA GSFC

Melting Glaciers

AP Photo: http://www.bafi.org

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Carbon Dioxide Capture and Storage

is an Important Part of the Solution

http://www.ipcc.ch/activity/csspm.pdf

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Options for Geological Storage

From IPCC Special Report

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Monitoring is a Key Enabling

Element of Geological Storage

Purposes for Monitoring

• Health and safety

• Environmental protection

• Natural resource protection

• Model calibration

• Performance assessment

• Verification of national inventories

• Carbon credit trading

• Regulatory compliance

• Establish a pre-injection baseline

• Designing remediation plans

• Etc…

Monitoring Methods

• Pressure

• Fluid sampling and analysis

• Seismic

• Electromagnetic

• Gravity

• Well logs

• Tracers

• Flux towers

• Soil gas

• Accumulation chambers

• Etc…

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Motivation for This Study

• More commercialprojects are coming online

• Good news– Lots of monitoring

techniques

• Bad news– Lots of monitoring

techniques

• Motivation: Simplify– Focus on two specific

purposes for monitoring

Purposes for Monitoring

• Health and safety

• Environmental protection

• Natural resource protection

• Model calibration

• Performance assessment

• Verification of national inventories

• Carbon credit trading

• Regulatory compliance

• Establish a pre-injection baseline

• Designing remediation plans

• Etc…

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Goals of the Study

1. What information is needed for inventoryverification and carbon trading credits?

2. What monitoring strategy and methods areavailable?

3. With what precision and detection levelsshould this information be provided?

4. Are satisfactory methods available?

5. What are the opportunities forimprovement?

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Verification of National Inventories

• Inventory verification is an essential component ofnational and international strategies to control andreduce CO2 emissions

• Annual accounting is performed based on sector-specific methodologies

• Newly developed guidelines have been published forCO2 capture and storage (IPCC, 2006)

… methodology for estimating national inventories of greenhouse

gas inventories of anthropogenic emissions by sources and

removals by sinks.

Good practice… neither over- nor under-estimates so far as can

be judged and which uncertainties are reduced as far as

practicable.Revised IPCC Guidelines, 2006

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Inventory Guidelines for CO2

Capture and StorageSystem 1. Capture and Compression

System 2. Transportation

System 3. Injection

System 4. Geological Storage Reservoir

Intermediate

System 1. Capture and Compression

From IPCC, 2006

CO2

Capture

Compression

System Components

for On-Shore Storage

Pipeline Transport

Geological Storage Reservoir

Injection System

(e.g. pumps)

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SPE ATCE, San Antonio, TX

Inventory Guidelines for CO2

Capture and StorageSystem 1. Capture and Compression

System 2. Transportation

System 3. Injection

System 4. Geological Storage Reservoir

Intermediate

System 1. Capture and Compression

From IPCC, 2006

CO2

Capture

Compression

System Components

for On-Shore Storage

Pipeline Transport

Geological Storage Reservoir

Injection System

(e.g. pumps)

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Key Question: Measure Emissions

Into the AtmosphereSystem 1. Capture and

Compression

System 2. Transportation

System 3. Injection

System 4. Geological Storage

Reservoir

On-Shore StorageGeological Storage Reservoir

CO2 emissions?

!

!

!

? Abandoned

Wells Faults

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Confidence is Needed to Support

Carbon Trading Markets

• European Trading System (ETS)

• Clean Development Mechanism (CDM)

• Joint Implementation (JI)

ECX CFI futures Contract on ICE Futures : Price and Volume

0

1,000,000

2,000,000

3,000,000

4,000,000

5,000,000

6,000,000

7,000,000

8,000,000

22-Apr-0

5

3-Jun-05

13-Jul-05

22-Aug-0

5

30-Sep-0

5

9-Nov-0

5

19-Dec-0

5

30-Jan-06

9-Mar-0

6

20-Apr-0

6

31-May-0

6

10-Jul-06

17-Aug-0

6

To

nn

es C

O2

0.00

5.00

10.00

15.00

20.00

25.00

30.00

35.00

Eu

ro/t

on

ne

Total Volume

Dec06 Sett

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Goals

1. What information is needed for inventory

verification and carbon trading credits?

2. What monitoring strategies and methods

are available?

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Strategy: Storage Reservoir

• Geophysical methods– Seismic

– Electrical

– SP

– Gravity

– Tilt

• Reservoir pressure

• Well logs

• Fluid sampling

Methods

Benefits

• History match to calibrateand validate models

• Early warning of leakage

Drawbacks• Mass balance difficult to

monitor

• Dissolved and mineralizedCO2 difficult to detect

Storage Reservoir

Saline Formation

Primary Seal

Groundwater Aquifer

Vadose Zone

On-shore Storage

Terrestrial Ecosystem

Atmosphere

CO2

CO2 Plume

Groundwater Aquifer

Secondary Seal

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Examples: Seismic Data

Collected at Sleipner

From IPCC, 2005, after Chadwick, 2004

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Strategy: Secondary Accumulations

Storage Reservoir

Saline Formation

Primary Seal

Groundwater Aquifer

Vadose Zone

On-shore Storage

Terrestrial Ecosystem

Atmosphere

CO2

CO2 Plume

Groundwater Aquifer

Secondary Seal

• Geophysical methods– Seismic

– Electrical

– SP

– Gravity

– Tilt

• Formation pressure

• Well logs (e.g. RST)

• Fluid sampling

Methods

Benefits• Sensitivity to small

secondary accumulations(~103 tonnes) and leakagerates

• Early warning of leakage

Drawbacks• Detection difficult if secondary

accumulations do not occur

• Dissolved and mineralized CO2

difficult to detect

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Frio Formation: Vertical Seismic Profile Data

Post Injection

Control

Reflection

CO2

Reflection

Tw

o-w

ay t

ravel tim

e

Data from Tom Daley, LBNL

Pre Injection

1,600 tonnes CO2

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Strategy: Groundwater

Storage Reservoir

Saline Formation

Primary Seal

Groundwater Aquifer

Vadose Zone

On-shore Storage

Terrestrial Ecosystem

Atmosphere

CO2

CO2 Plume

Groundwater Aquifer

Secondary Seal

• Geophysical methods– Seismic– Electrical– SP– Gravity– Tilt

• Formation pressure

• Well logs

• Fluid sampling

Methods

Benefits• Sensitivity to small secondary

accumulations (~102-103 tonnes)and leakage rates

• More monitoring methodsavailable

• Detection of dissolved CO2 lesscostly with shallow wells

Drawbacks• Detection after significant leakage

has occurred

• Detection after potential groundwaterimpacts have occurred

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Strategy: Vadose Zone

Storage Reservoir

Saline Formation

Primary Seal

Groundwater Aquifer

Vadose Zone

On-shore Storage

Terrestrial Ecosystem

Atmosphere

CO2

CO2 Plume

Groundwater Aquifer

Secondary Seal

• Geophysical methods

– Electrical

• Soil gas and vadose zone

sampling

• Vegetative stress

Methods

Benefits• High concentrations of CO2 occur

with small leaks

• Early detection could triggerremediation to avoid atmosphericemissions

Drawbacks• Significant effort for null result

• Detection only after some seepage isimminent

• Detection after potentialecosystem impacts have occurred

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SPE ATCE, San Antonio, TX

Strategy: Vadose Zone

Storage Reservoir

Saline Formation

Primary Seal

Groundwater Aquifer

Vadose Zone

On-shore Storage

Terrestrial Ecosystem

Atmosphere

CO2

CO2 Plume

Groundwater Aquifer

Secondary Seal

• Geophysical methods

– Electrical

• Soil gas and vadose zone

sampling

• Vegetative stress

Methods

Benefits• High concentrations of CO2 occur

with small leaks

• Early detection could triggerremediation to avoid atmosphericemissions

Drawbacks• Significant effort for null result

• Detection only after some seepage isimminent

• Detection after potentialecosystem impacts have occurred

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Strategy: Atmosphere

Storage Reservoir

Saline Formation

Primary Seal

Groundwater Aquifer

Vadose Zone

On-shore Storage

Terrestrial Ecosystem

Atmosphere

CO2

CO2 Plume

Groundwater Aquifer

Secondary Seal

• Eddy covariance

• Flux accumulation chamber

• Soil gas and vadose zone flux

monitoring

• Optical methods (lidar)

Methods

Benefits• Direct measurement of

seepage

• Detection, location andquantification of seepage flux

Drawbacks• Distinguishing storage related

fluxes from natural ecosystem andindustrial sources necessitatescomprehensive monitoring

• Significant effort for null result

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Atmospheric Monitoring Methods

Willow Creek

-2000

-1000

0

1000

2000

3000

0 60 120 180 240 300 360

Time (days)

µg

/m2/s

Barrow Island

-500

-300

-100

100

300

150 180 210 240

Time (days)

µg

/m2/s

Flux accumulation chamber

Eddy

Covariance

Tower

Courtesy of Walter Oechel

Courtesy of Ken Davis and Paul Bolstad

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Goals

1. What information is needed for inventoryverification and carbon trading credits?

2. What monitoring strategy and methodsare available?

3. With what precision and detection levelsshould this information be provided?

- What is the best strategy for setting detectionlevels?

- What is an appropriate detection level?

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Attributes: Practicable Detection Levels

• Simple… both with regard toexplaining and implementingthe approach

• Defensible… sufficientlystringent to ensure thatgeological storage will beeffective as a GHG mitigationtechnique

• Verifiable… the value ofcarbon credits can be assignedwith confidence and certainty

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Detection Approaches

!10 using µ

g/m2/s eddy

covariance

towers

Instrument- based

method

!!50 µg/m2/sPrescribed CO2

flux

!!!5,000

tonnes/year

Specified CO2

emission per year

!!0.01%/year% CO2 stored

!50% of

background

Fraction of

background CO2

flux

VerifiableDefensibleSimpleExampleMethod

!!!

Page 28: Monitoring Carbon Dioxide Sequestration in Deep Geological … · 2017-12-05 · SPE102833,September 26, 2006 SPE ATCE, San Antonio, TX Monitoring Carbon Dioxide Sequestration in

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SPE ATCE, San Antonio, TX

Goals

1. What information is needed for inventory

verification and carbon trading credits?

2. What monitoring strategy and methods

are available?

3. With what precision and detection levels

should this information be provided?- What is the best strategy for setting detection levels?

- What is an appropriate detection level?

4. Are satisfactory methods available?

Page 29: Monitoring Carbon Dioxide Sequestration in Deep Geological … · 2017-12-05 · SPE102833,September 26, 2006 SPE ATCE, San Antonio, TX Monitoring Carbon Dioxide Sequestration in

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Hypothetical Storage Project• Annual Injection Rate

– 5 Mt/year

• Project Duration

– 50 years

• Reservoir Thickness

– 100 m

• In Situ CO2 Density

– 600 kg/m3

• Porosity

– 25%

• Average CO2 Saturation

– 10%

600 MW Coal-fired

power plant

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Detection Limit: Specified Mass Flux

• 3 Emission Detection Limits

– 1,000 t/yr

– 5,000 t/yr

– 10,000 t/yr

• Is it simple?

• Is it defensible?

• Is it verifiable?

Willow Creek

-2000

-1000

0

1000

2000

3000

0 60 120 180 240 300 360

Time (days)

µg

/m2/s

Courtesy of Ken Davis and Paul Bolstad

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Is This Approach Defensible?

50 years x 5 Mt/year = 250 Mt

96%10,000 t/yr

98%5,000 t/yr

99%1,000 t/yr

Detection LevelRetention Rate

Over 1,000 Years

!

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Is the approach verifiable?

• Secondary

accumulations

– Seismic

– Pressure

monitoring

• Atmospheric

monitoring

Storage Reservoir

Saline Formation

Primary Seal

Groundwater Aquifer

Vadose Zone

On-shore Storage

Terrestrial Ecosystem

Atmosphere

CO2

CO2 Plume

Groundwater Aquifer

Secondary Seal

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Sensitivity of Seismic Methods

Detection Limits at Reservoir DepthMyer et al, 2002: 10,000 tonnes

Chadwich et al.: Sleipner, 1,600 tonnes

White el al., 2004: Weyburn, 2,500 tonnes

Daley et al., 2005: Frio Formation, 1,600 tonnes

Conceptual

Model

0 500 1000

-1500

-1000

-750

-500D

epth

(m

)

Plume Radius (m)

10,000 t5,000 t1,000 t

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Sensitivity of Pressure Monitoring

Injection/Monitoring Well

Injection Tubing

Well Casing

Packer

PressureTransducer

CO2 CO2

CO2 CO2

xx

xx

x

x

x

Injection wells

Abandoned wells

Fault

1 km

1 km

For favorable permeability-thickness product:

measurable pressure increases within a year.

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Sensitivity of Atmospheric

Monitoring

21923.6-0.80-15.4-22.810,000

96.8-0.80-13.0-20.3-24.05,000

-0.8-20.3-22.8-24.2-25.01,000

1%5%10%25%100%

Emission Rate

(tonnes/year)

Footprint of CO2 Emissions Sources as a Fraction of

the Plume Footprint

Average Annual CO2 Fluxes (!g/m2/s)

The average annual baseline flux is -25.2 !g/m2/s for Willow Creek

Page 36: Monitoring Carbon Dioxide Sequestration in Deep Geological … · 2017-12-05 · SPE102833,September 26, 2006 SPE ATCE, San Antonio, TX Monitoring Carbon Dioxide Sequestration in

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SPE ATCE, San Antonio, TX

Goals

1. What information is needed for inventory

verification and carbon trading credits?

2. What monitoring strategy and methods are

available?

3. With what precision and detection levels

should this information be provided?- What is the best strategy for setting detection levels?

- What is an appropriate detection level?

4. Are satisfactory methods available?

5. What are the opportunities for improvement?

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Opportunities for Improvement

• Direct emission measurements from existing CO2-EOR

projects

• Controlled release experiments for demonstrating the

ability to detect, locate and quantify emissions

• Optical techniques with path lengths of ~1 km

• Approaches to distinguish natural ecosystem fluxes

and other anthropogenic emissions from geological

storage reservoir emissions

• Improve detection of small secondary accumulations of

CO2

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Conclusions• Geological storage reservoirs will be treated as an

emission source

• Monitoring methods are available today

• Detection limits need to be determined– Simple, defensible and verifiable

– Specified mass flux per year appears robust (range of 1,000 to10,000 tonnes per year)

• Detect, locate, then quantify

• Maintain flexibility– Different strategies for different locations

• Opportunities for improvement– Experience, verification and innovation