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Ensuring & Monitoring Secure Storage for Carbon Dioxide Storage for Carbon Dioxide Carbon Capture and Storage (CCS) Projects Susan D. Hovorka Gulf Coast Carbon Center Bureau of Economic geology Jackson School of Geosciences The University of Texas at Austin Presented to Carbon Capture & Sequestration Public Workshop, June 10, 2010 Sacramento, CA
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Ensuring & Monitoring Secure Storage for Carbon DioxideStorage for Carbon Dioxide

Carbon Capture and Storage (CCS) Projects

Susan D. HovorkaGulf Coast Carbon Center

Bureau of Economic geologyJackson School of GeosciencesThe University of Texas at Austin

Presented to Carbon Capture & SequestrationPublic Workshop, June 10, 2010 Sacramento, CA

Ensuring storage is permanent irequires..

• Characterization and predictiveCharacterization and predictive modeling to select a geologic site that will accept and retain CO2p 2

• Operation of the injection process to conserve site geologic integrity g g g y

Monitoring can be used to document fthe correctness of characterization,

modeling, and operationode g, a d ope at o

Characterization shows where and h CO ill b t d

Capture Land surfacehow CO2 will be stored

Pore scale trapping> 800 m

Pore-scale trapping

Confining system limits CO rise

CO2

limits CO2 rise

Brine displacedInjection ZoneInjection zone

p

Safe Operation of Injection wellsSafe Operation of Injection wells

• Management of wells to These activities areManagement of wells to insure that fluids are retained

These activities are required by federal law for all injection wellsretained

• Management of pressure to insure that

injection wells under the Safe Drinking Water Act of 1974 pressure to insure that

integrity of the geologic system is retainedsystem is retained

Monitoring to test the correctness of characterization modeling andof characterization, modeling, and

operation

• Imaging CO2 in the subsurfaceImaging CO2 in the subsurface• Measuring pressure changes

Tools to assess compositional changes• Tools to assess compositional changesMatch to predictive model

•Surveillance of protected resources

Settings that can be monitored• Atmosphere

– Ultimate receptor but dynamic

Settings that can be monitored

Complex!

Ultimate receptor but dynamic• Biosphere

– Assurance of no damage but dynamic

• Soil and Vadose Zone

AtmosphereBiosphere

V d & il – Integrator but dynamic• Aquifer and USDW

– Integrator, slightly isolated from ecological effects

Ab i j i i i

Aquifer and USDW

Vadose zone & soil

• Above injection monitoring zone– First indicator, monitor small

signals, stable. • In injection zone - plume

Oil field type technologies Will

Seal

Monitoring ZoneComplex!

– Oil-field type technologies. Will not identify small leaks

• In injection zone - outside plume– Assure lateral migration of CO2

Seal

Monitoring Zone

CO2 plume Assure lateral migration of CO2and brine is acceptable

2 p

Monitoring box

Gulf Coast Carbon Center Field Tests

SECARB Phase II&II

Frio I and II Test SiteTexas American Phase II&II

DenburyCranfield

Texas American Resources

SACROCSouthwestSouthwestPartnershipKinderMorganNM Tech

Other projects with strong monitoring programs providemonitoring programs provide

experience• Sleipner, North Sea• Weyburn SaskatchewanWeyburn, Saskatchewan• Nagaoka, Japan

K t i G• Ketzin, Germany• Gaylord, Michigan• In Salah, Algeria• Otway AustraliaOtway, Australia

Example of a research project DOE funded SECARB Phase III at Cranfield, MississippiPhase III at Cranfield, Mississippi

3,000 m depth (10,300 ft)Gas cap, oil ring, downdip water legOriginal production in 1950’sOriginal production in 1950 sStrong water driveShut in since 1965Returned to near initial pressureCO2-EOR initiated 2008 with coincident

pressure monitoringHosted by Denbury Resources

Southern States Energy BoardKen Nemeth Dir, Jerry Hill PI, yBruce Brown NETL manager

Research collaborators: Denbury Onshore LLC site hostLBNL, LLNL, ORNL, USGS NETL, Mississippi State,LBNL, LLNL, ORNL, USGS NETL, Mississippi State, University of Mississippi, Schlumberger, Sandia Technologies, Pinnacle, QEA

Cranfield DAS MonitoringgInjectorCFU 31F1

Obs CFU 31 F2

Obs CFU 31 F3

Above-zonemonitoringF1 F2 F3Closely spaced well

array to examine Above Zone Monitoring

10,500 feet BSL

flow in complex reservoir

Injection Zone

68m

112 m

Cross Well ERT tells us how flow doccurred

sx ec

trode

s

elec

trode

Secondx

x

x

wel

l F3

ele

on w

ell F

2 Resistive plume out of section migration

Direction of CO2 plume x

x serv

atio

n w

Obs

erva

tio

migration

Injectorx 50ft

ObsO

Resistive plume = CO2 in reservoir

Charles Carrigan, LLNL

Fluid flow observed falls in the modeled range

Breakthrough time at F20.4

Set #1 at Ly14 (12/16/2009)

Set #2 at Ly17(12/20/2009)

Set #3 at Ly17(12/8/2009)

Set #4 at Ly10(12/15/2009)Observed CO2 movement

0.2

0.3

atur

atio

n

y ( )

Set #5 at Ly19(12/29/2009)

Set #6 at Ly10(12/23/2009)

Set #7 at Ly10(12/23/2009)

Set #8 at Ly10(12/7/2009)

0.1

Gas

sa y ( )

Set #9 at Ly7(12/7/2009)

Set #10 at Ly10(12/11/2009)

0

12/1/09

12/3/09

12/5/09

12/7/09

12/9/09

12/11/09

12/13/09

12/15/09

12/17/09

12/19/09

12/21/09

12/23/09

12/25/09

12/27/09

12/29/09

12/31/09

1/2/10

1/4/10

1/6/10

Date

Jong-won Choi and JP Nicot BEG

Frio Brine Pilot Sit t tSite tests

Near Houston TX

• High Fresh water (USDW) zoneprotected by surface casing

Permeability – 4.4 to 2.5 Darcys

• Steeply dipping – 11 to 16 degrees

Injection zones:First experiment

2004: Frio “C”Second experiment 11 to 16 degreesp

2006 Frio “Blue”

Oil productionOil production

Injection well

Observation well

Frio Test Site Houston Texas 2004 -2006Frio Test Site, Houston Texas, 2004 -2006

CO2 Saturation Observed with Cross-well S i i T h M d l dSeismic Tomography vs. Modeled

Tom Daley and Christine Doughty LBNL

Pressure as a powerful tool for monitoringp g

Start injection at DAS Dec 1, 2009

I j t BHP Ob ti

e

bar psi

Injector BHP Observation well BHP

e pr

essu

re 400

otto

m h

ole

340Bo

Dec 1

340

It’s all about pressure

Elapsed time

Real-time data from DASReal time data from DAS• Mass flow increased to 507

Injection well BHP 5 818 psiInjection well BHP 5,818 psi BPT injection well 162 degrees F (252 F original)degrees F (252 F original)

Fluid Displacement as a Limit on CapacityCapacity

D d• Depends on boundary

diticonditions

Model –history match pressure at real-time monitoring well

BEG Observation well

at real-time monitoring well14,000 CFU 29-10 CFU 29-12

CFU 26-1 CFU 25-2

CFU 24 2 CFU 29 2Injection ratesResults of 1 year model6000

6,000

8,000

10,000

12,000

ectio

n ra

te (M

scfd

)

CFU 24-2 CFU 29-2CFU 28-1 CFU 27-1CFU 29-4 CFU 48-1

CFU 29-7

jcontinuous pressure data

5500

e (p

si)

-

2,000

4,000

,

7/1/2008 8/20/2008 10/9/2008 11/28/2008 1/17/2009 3/8/2009 4/27/2009 6/16/2009

CO

2 in

je

5000

Pres

sure

Measurement

Date

Rock and fluid properties in simulator

Obs well EGL7

Simplified CO2 injection rate4000

4500Calculated

Modeled pressureMeasured pressure4000

2/22/2008 11/18/2010 8/14/2013 5/10/2016 2/4/2019

Date

p

7/2008 12/2009JP Nicot Jong Won Choi BEG

Assurance Permanence via Phase Trapping the power of capillaryTrapping – the power of capillary

pressure2

of C

O2 Phase-trapped

CO2

ject

ion

G i B i fill d

Inj

Grains Brine – filled pores

Measurement at a Well:Saturation logging (RST ) Observation well to measure

changes in CO saturation – match to modelchanges in CO2 saturation – match to model

Lithology

DEPTHFEET

RST gas sat

Model gas sat.V/V1 0

RST gas satV/V1 0

RST gas satV/V1 0

RST gas satV/V1 0

RST gas satV/V1 0

RST gas sat Log porosity

Model porosityV/V0.4 0

Model permmD10000 1

Day 4 Day 10 Day 29 Day 69 Day 142 Day 474Model gas sat. Model gas sat. Model gas sat. Model gas sat.

LithologyV/V0 1

5010

5000

RST gas sat.V/V1 0

RST gas sat.V/V1 0

RST gas sat.V/V1 0

RST gas sat.V/V1 0

RST gas sat.V/V1 0

RST gas sat.V/V1 0

Log porosityV/V0.4 0

5010

5020

5030

5040

Shinichi Sakurai, Jeff Kane, Christine Doughty

5050

How CO2 dissolved in aquifers ld d licould damage water quality

CO2 dissolves in water = dissolution trappingCO2 dissolves in water = dissolution trappingCO2(g) + H2O ↔ H2CO3(aq) H2CO3(aq) ↔ HCO3(aq)– + H+

HCO (aq)– ↔ CO (aq)-– + H+(aq) Acid= tang in HCO3(aq) ↔ CO3(aq) + H+(aq) gcarbonated water

Acid is buffered by rock-water interactionincrease Ca Mg Fe Na Si HCO SO etc in solutionincrease Ca, Mg, Fe, Na, Si, HCO3, SO4, etc. in solution

What could the etc. be?Mn, As, Pb, Sr, Ni, Zn, Ag, U, Ni, Cd……, , , , , , g, , ,

SACROC- testing fresh water after 35 years large-scale injectiony g j

Smyth, BEG 2009

Fresh water quality at SACROC d dundamaged

• CO2 injection at 6000-7000 ftCO2 injection at 6000 7000 ft • Fresh water at <1000 feet

N t ti iti l h i• No systematic compositional changes in fresh water through time or by comparison t ito region

• However, complex natural and manmade processes in fresh water limit ability to detect CO2, should it leak into fresh water.

Goals of monitoring at a long term, f ll l i l jfull scale commercial project

• Confirm that the predictions of containment made based pon site characterization at the time of permitting are valid

• Confidence to continue injection is gained from monitoring observations that are reasonably close tomonitoring observations that are reasonably close to model predictions

• Confirm that no unacceptable consequences result from injectioninjection.

• Monitoring during injection should be designed to prove-up confinement so that monitoring frequency could be di i i h d th h th lif f th j t d t lldiminished through the life of the project and eventually stopped, allowing the project to be closed.

Gulf Coast Carbon Center (GCCC)Collaborators IA sponsors

BEG Team

Collaborators

BEG Team Scott TinkerIan DuncanSue Hovorka

BEG- CEELBNLLLNL

Tip MeckelJ. P. Nicot

Rebecca SmythRamon Trevino

ORNLUSGSNew Mexico TechMississippi State URamon Trevino

Katherine RomanakChangbing Yang

Dave Carr

Mississippi State UU of MississippiSECARBSWP

Jiemin LuJong Won ChoiWoodong Yung

Carey King students

UT-PGEUT- CCEPUT- DoGSUniv EdinburghCarey King students

and othersUniv Edinburgh

If you use carbon .. Put it backIf you use carbon .. Put it backTo reduce CO2 emissionsto air from stationary (point) sourcesy (p )

is currently burned and emitted to air

CO2 is captured as concentratedhigh pressure fluid by one of severalmethods..emitted to air methods..CO2 is shipped as supercritical fluid via pipeline to a selected, permitted injection site

Carbon extractedfrom a coal or other

CO2 injected at pressure intopore space at depths below and isolated (sequestered)

fossil fuel…below and isolated (sequestered)from potable water.

CO2 stored in pore space over geologicallyover geologicallysignificant time frames.

www.gulfcoastcarbon.org


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