Cycle Integration - A Method to reduce Penalty due to Post-Combustion CO2 Capture

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Energy Research Center 36 th International Technical Conference on Clean Coal & Fuel Systems, Clearwater, June 5-9, 2011 Nenad Sarunac Carlos E. Romero Energy Research Center Lehigh University Bethlehem, PA Integration of Rankine and Brayton Cycles Reduces Penalty Due to Post-Combustion CO 2 Capture

Transcript of Cycle Integration - A Method to reduce Penalty due to Post-Combustion CO2 Capture

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36th International Technical Conference on Clean Coal & Fuel Systems, Clearwater, June 5-9, 2011

Nenad Sarunac

Carlos E. Romero Energy Research Center

Lehigh University

Bethlehem, PA

Integration of Rankine and Brayton Cycles Reduces Penalty Due to Post-Combustion

CO2 Capture

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Presentation Outline

◙ Introduction

◙ Post-Combustion CO2 Capture ◘ Conventional Thermal Integration of CO2 Capture

Process

◘ Advanced Thermal Integration of CO2 Capture Process

◙ Cycle Integration ◘ Hydrogen-Fueled Brayton Cycle

◘ Syngas-Fueled Brayton cycle

◙ Conclusions

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Introduction

◙ Atmospheric levels of CO2 have increased over the last 150 years from around 280 to 360 ppm.

◙ Regulations restricting CO2 emissions from existing and newly built emitting sources are looming on a horizon. ◘ Coal-fired utility boilers generate over 50% of the electricity in the

US.

◙ Oxy-fuel, IGCC, and post-combustion carbon capture technologies are viable options for new power plants.

◙ It is likely that a significant percentage of existing power plants will be retrofitted with the post-combustion CO2 capture process. ◘ The major barriers to implementation of post-combustion CO2

capture technology are significant reduction in power plant output and high performance penalty.

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Introduction

◙ Thermal integration can offset part of performance and capacity penalty incurred by retrofit or implementation of the post-combustion CO2 capture.

◙ The amine CO2 capture process was analyzed in this study.

◙ Results concerning thermal integration of Rankine and Brayton cycles are presented for a 640 MW subcritical unit firing bituminous coal. ◘ Rankine and Brayton cycles were modeled using commercial

program PEPSE provided by Scientech.

◙ The project was funded by the New York State Energy Research and Development Authority (NYSERDA).

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Schematic Diagram of a Post-Combustion CO2 Capture Process

100100--140F140F

4040--60C60C230230--250F250F

110110--120C120C

Steam forSteam for

RegenerationRegeneration

100100--140F140F

4040--60C60C230230--250F250F

110110--120C120C

Steam forSteam for

RegenerationRegeneration

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Conventional Thermal Integration of CO2 Capture Process

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Advanced Thermal Integration of CO2 Capture Process

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Advanced vs. Conventional Thermal Integration: Net Unit Efficiency

640 MW Subcritical Unit

11.96

10.62

9.83

9.42

8.82

8.22

7.43

11.70

10.42

9.66

9.25

8.67

8.08

7.31

0.750.56 0.49 0.47 0.43 0.40 0.35

0

2

4

6

8

10

12

14

5.47 GJ/tCO2 4.65 GJ/tCO2 4.19 GJ/tCO2 3.95 GJ/tCO2 3.60 GJ/tCO2 3.26 GJ/tCO2 2.79 GJ/tCO2

Reboiler Thermal Duty

De

cre

as

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ne

t R

ela

tiv

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o B

as

eli

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[%

-po

int]

Conventional Thermal Integration

Advanced Thermal Integration

Absolute Difference

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Cycle Integration

◙ Thermal integration of Rankine and Brayton cycles in combination with heat recovery from flue gas and CO2 compression was analyzed.

◙ Goal: Efficiency improvement of the Rankine cycle and reduction of capacity penalty incurred by implementation of the post-combustion CO2 capture.

◙ Fueling options considered for the Brayton cycle: ◘ Hydrogen

◘ Syngas (Biogas) produced by gasification of biomass

■ Leftover chair burned in boiler

◙ Both fueling options result in zero CO2 emissions from the Brayton cycle. ◘ Brayton cycle power output and heat provided to the Rankine cycle

through thermal integration do not contribute to plant CO2 emissions.

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Hydrogen-Fueled Brayton Cycle

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Sources of Hydrogen

◙ Hydrogen can be produced from diverse domestic feedstocks using a variety of process technologies.

◙ Hydrogen from natural gas: ◘ Viable near-term option, it is not viewed by DOE as a long-term solution

because it does not help solve the green house gas or energy security issues.

◙ Hydrogen from coal: ◘ Hydrogen will be produced from coal-derived synthesis gas in a zero

emissions, high-efficiency co-production power plant that will produce hydrogen from coal along with electricity.

◙ Hydrogen from nuclear power: ◘ Hydrogen will be produced using heat from a nuclear energy system

(high-temperature thermo-chemical cycle or high-temperature electrolysis).

◙ Hydrogen from renewable resources: ◘ Hydrogen will be produced from domestic renewable energy resources

that minimize environmental impacts using electrolysis, thermo-chemical conversion of biomass, photolytic and fermentative micro-organism systems, photo-electrochemical systems, and high-temperature chemical cycle water splitting.

◙ Hydrogen turbines being developed by DOE under Advanced Turbine System program. ◘ Commercialization expected by 2020?

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Cycle Integration

Hot Cooling Water Cold Cooling Water

D

FWH A

FD Fan

Flue Gas

FUEL

SAPH

BFP

Main

Condenser

To Post-Combustion

CO 2 Capture

ID Fan

Extr

acti

on

E

Ex

tra

cti

on

D

Ex

tra

cti

on

C

LP Turbine LP Turbine

Ex

tra

cti

on

A

Ex

tra

cti

on

B

Generator

Main Steam

Hot Reheat Steam

Cold Reheat Steam

HP

Turbine IP Turbine

FWH BFWH C FWH D FWH E

PA Fan

PAPH

SCR

Extr

acti

on

F

SSR

FWH F FWH G

Extr

acti

on

GBFP

To Condenser

FGD

LSTG

Reboiler

Desuperheater

Reboiler Steam

Make-up

10 k

g/s

PA SAH

SA SAH

3.24 bar (47 psia)

3.10 bar (45 psia)

Ambient Air at T amb

M SAH = 0 kg/s

Q SAH = 0 MW th

FGRHT

X

C T G

F uel (H 2)

HRSG

Compressor

Steam

670 oC (1,238

oF )

188 oC (370

oF )

TSteam, PSteam, MSteam

LP HXE

HP HXE

Pump

QR eb

Brayton cycle sized to provide heat for HP FWHs A and B.

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Optimal Cycle Integration

Rankine-Brayton Cycle Integration

0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

4.0

4.5

020406080100

HRSG Thermal Duty Supplied to HP FWH [%]

Incre

ase in

Co

mb

ined

Cycle

Heat

Rate

Rela

tive t

o

Fu

ll H

RS

G T

he

rmal

Du

ty S

up

pli

ed

to

HP

FW

H [

%] Advanced MEA thermal integration

Modification C

Modification D

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Basic Features of Analyzed Thermal Integrations Options

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S ourc e of

Heat for HP

F WHs

HR S G S team

HR S G E xhaust

F lue G as

C O 2

C ompress ion Heat

L P S team F lue G as

C onventional Desuperheat by reboiler condensate x x x

Advanc ed x x xModific ation A x x x xModific ation B x x x xModific ation C x x x x xModific ation D x x x x x

S ourc es of R eboiler

Heat

C ooling by reboiler condensate

Thermal

Integ ration

C ontrol of S team Temperature into

R eboiler

S ourc es of Heat for L P F WHs

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Rankine - Brayton Cycle Integration

23.26

19.59

17.44

16.32

14.67

13.04

10.8811.52

7.62

5.53

4.48

3.00

1.58

0.26

8.35

4.75

2.87

1.98

0.70 0.62

2.24

19.83

16.47

14.20

13.16

11.65

10.21

8.40

0

5

10

15

20

25

5.47 4.65 4.19 3.95 3.60 3.26 2.79

Reboiler Thermal Duty [GJ/tonne CO2]

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Cy

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Ou

tpu

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tiv

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as

eli

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[%

]

Conventional Thermal Integration, No Cycle Integration

Conventional Thermal Integration

Advanced Thermal Integration

Modification A

Modification B

Modification C

Modification D

Modification D, No Cycle Integration

Gross Rankine Cycle Power Output:

Comparison to Baseline

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State of the art amines Baseline: Rankine Cycle no CO2 Capture

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Rankine - Brayton Cycle Integration

-23.26

-19.59

-17.44-16.32

-14.67-13.04

-10.88

10.64

14.53

16.6317.68

19.1620.57

22.42

13.81

17.4119.29

20.1821.46

22.7824.39

-19.83

-16.47

-14.20-13.16

-11.65-10.21

-8.40

-30

-25

-20

-15

-10

-5

0

5

10

15

20

25

30

5.47 4.65 4.19 3.95 3.60 3.26 2.79

Reboiler Thermal Duty [GJ/tCO2]

Ch

an

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in

Co

mb

ine

d C

yc

le P

ow

er

Ou

tpu

t R

ela

tive

to

Bas

eli

ne [

%]

Conventional Thermal Integration, No Cycle Integration

Conventional Thermal Integration

Advanced Thermal Integration

Modification A

Modification B

Modification C

Modification D

Modification D, No Cycle Integration

Gross Combined Cycle Power Output:

Comparison to Baseline

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State of the art amines

Baseline: Rankine Cycle no CO2 Capture

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Rankine - Brayton Cycle Integration

11.96

10.62

9.839.42

8.82

8.22

7.43

6.95

5.82

5.214.91

4.484.07

3.53

5.98

4.94

4.404.14

3.773.39

2.92

10.71

9.48

8.658.26

7.71

7.19

6.52

0

2

4

6

8

10

12

14

5.47 4.65 4.19 3.95 3.60 3.26 2.79

Reboiler Thermal Duty [GJ/tonne CO2]

De

cre

as

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om

bin

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Cy

cle

Ne

t E

ffic

ien

cy

Re

lati

ve

to

Ba

se

lin

e [

%-p

oin

t]

Advanced Thermal Integration, No Cycle Integration

Conventional Thermal Integration

Advanced Advanced Thermal Integration

Modification A

Modification B

Modification C

Modification D

Modification D, No Cycle Integration

Combined Cycle Net Efficiency: Comparison to

Baseline

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State of the art amines Baseline: Rankine Cycle no CO2 Capture

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Comparison to Baseline

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Thermal Integration % % %-point

Conventional w/o Cycle Integration -14.67 34.04 8.82

Advanced 19.82 14.44 4.38

Modification D 21.46 12.19 3.77

Baseline = Rankine Cycle, No CO2 Capture

Integrated Combined Rankine-Brayton Cycle

State-of-the-Art Amines

Change in Gross

Power Output

Relative to

Baseline

Decrease in Net

Unit Efficiency

Relative to

Baseline

Increase in Net

Unit Heat Rate

Relative to

Baseline

Hydrogen-Fired Turbine, HP FWHs A and B

Thermal Integration % % %-point

Conventional w/o Cycle Integration -14.67 34.04 8.82

Advanced 8.35 19.06 5.56

Modification D 10.61 16.21 4.84

Baseline = Rankine Cycle, No CO2 Capture

Increase in Net

Unit Heat Rate

Relative to

Baseline

Hydrogen-Fired Turbine, HP FWH A

State-of-the-Art Amines

Integrated Combined Rankine-Brayton Cycle

Change in Gross

Power Output

Relative to

Baseline

Decrease in Net

Unit Efficiency

Relative to

Baseline

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Syngas-Fueled Brayton Cycle

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Gasification of Biomass

◙ EIA estimates there are 590 million wet tons of biomass available in the US on an annual basis.

◙ Dedicated biomass and biomass co-firing are used in the electricity generation sector.

◙ Biomass gasification is the conversion of an organically derived, carbonaceous feedstock by partial oxidation into a gaseous product, synthesis gas “syngas” or biogas consisting primarily of H2 and CO2.

◙ New dedicated biomass capacity is represented in the National Energy Modeling System as biomass integrated gasification combined-cycle (BIGCC) technology. ◘ The reactions in a gasifier are carried out at elevated temperatures, 500-1400 oC,

and atmospheric or elevated pressures up to 33 bar (480 psia).

◘ The oxidant can be air, pure oxygen, or a mixture of these gases with steam. ■ Air-blown gasifiers typically produce a product gas containing a relatively high

concentration of nitrogen with a low heating value.

◘ The syngas leaving the gasifier has to be cleaned to remove particulates and tar by employing either a low-temperature or high-temperature gas cleaning.

◘ In low-temperature cleaning, the gas is cooled with water, and particulates are removed in a series of cyclone vessels.

◘ Hot gas cleanup technology is relatively new, and DOE and many industrial partners are conducting tests to demonstrate the technology.

◘ There are advantages and disadvantages associated with both gas cleanup processes.

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Cycle Integration

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Hot Cooling Water Cold Cooling Water

D

FWH A

FD Fan

Flue Gas

FUEL

SAPH

BFP

Main

Condenser

To Post-Combustion

CO 2 Capture

ID Fan

Extr

ac

tio

n E

Extr

acti

on

D

Extr

acti

on

C

LP Turbine LP Turbine

Extr

acti

on

A

Extr

acti

on

B

Generator

Main Steam

Hot Reheat Steam

Cold Reheat Steam

HP

Turbine IP Turbine

FWH BFWH C FWH D FWH E

PA Fan

PAPH

SCR

Extr

ac

tio

n F

SSR

FWH F FWH G

Extr

ac

tio

n GBFP

To Condenser

FGD

LSTG

Reboiler

Desuperheater

Reboiler Steam

Make-up

10 k

g/s

PA SAH

SA SAH

3.24 bar (47 psia)

3.10 bar (45 psia)

Ambient Air at T amb

M SAH = 0 kg/s

Q SAH = 0 MW th

FGRHT

X

C T GG as ifier

HP HXE A1

A ir

S yng as

C har

B iomas s

A ir

HP HXE B 1

L P HXE 1

HT HR L T HR 1 L T HR 2

900 o

C

90 to 120 o

C

HP HXE HP HXE B 2

1 2 3 4

2

1 3

4

QR eb

L P HX E 2

518 o

C

Gasifier sized taking biomass availability into consideration.

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Gross Rankine Cycle Power Output: Comparison to Baseline

Rankine - Syngas-Fueled Brayton Cycle Integration

23.26

19.59

17.44

16.32

14.67

13.04

10.88

13.65

9.96

7.90

6.88

5.46

4.10

2.35

10.53

7.32

5.33

4.41

3.11

1.88

0.18

19.83

16.47

14.20

13.16

11.65

10.21

8.40

0

5

10

15

20

25

5.47 4.65 4.19 3.95 3.60 3.26 2.79

Reboiler Thermal Duty [GJ/tonne CO2]

Re

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cti

on

in

Ra

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Cy

cle

Gro

ss

Po

we

r

Ou

tpu

t R

ela

tiv

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eli

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[%

]

Conventional Thermal Integration, No Cycle Integration

Advanced Thermal Integration

Modification C

Modification D

Modification D, No Cycle Integration

Baseline: Rankine Cycle no CO2 Capture State of the art amines

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Gross Combined Cycle Power Output:

Comparison to Baseline

Rankine - Syngas-Fueled Brayton Cycle Integration

-23.26

-19.59

-17.44-16.32

-14.67

-13.04

-10.88

8.45

4.75

2.691.67

0.261.10

2.85

5.32

2.12

0.120.79

2.103.32

5.02

-19.83

-16.47

-14.20-13.16

-11.65-10.21

-8.40

-30

-25

-20

-15

-10

-5

0

5

10

15

5.47 4.65 4.19 3.95 3.60 3.26 2.79

Reboiler Thermal Duty [GJ/tonne CO2]

Ch

an

ge

in

Co

mb

ine

d C

yc

le P

ow

er

Ou

tpu

t R

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tiv

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eli

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[%

]

Conventional Thermal Integration, No Cycle Integration

Advanced Thermal Integration

Modification C

Modification D

Modification D, No Cycle Integration

Baseline: Rankine Cycle no CO2 Capture

State of the art amines

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Combined Cycle Net Efficiency: Comparison to

Baseline

Rankine - Syngas-Fueled Brayton Cycle Integration

11.96

10.62

9.839.42

8.82

8.22

7.43

9.60

8.40

7.737.40

6.946.50

5.93

8.55

7.54

6.896.59

6.175.77

5.21

10.71

9.48

8.658.26

7.71

7.19

6.52

0

2

4

6

8

10

12

14

5.47 4.65 4.19 3.95 3.60 3.26 2.79

Reboiler Thermal Duty [GJ/tonne CO2]

De

cre

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om

bin

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Cy

cle

Ne

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ffic

ien

cy

Re

lati

ve

to

Ba

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%-p

oin

t]

Advanced Thermal Integration, No Cycle Integration

Advanced Thermal Integration

Modification C

Modification D

Modification D, No Cycle Integration

Baseline: Rankine Cycle no CO2 Capture State of the art amines

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Comparison to Baseline

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Thermal Integration % % %-point

Conventional w/o Cycle Integration -14.67 34.04 8.82

Advanced 0.26 24.98 6.94

Modification D 2.10 21.59 6.17

Baseline = Rankine Cycle, No CO2 Capture

Syngas (Biogas)-Fired Turbine

Integrated Combined Rankine-Brayton Cycle

State-of-the-Art Amines

Change in Gross

Power Output

Relative to

Baseline

Decrease in Net

Unit Efficiency

Relative to

Baseline

Increase in Net

Unit Heat Rate

Relative to

Baseline

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Conclusions

◙ Coal will remain a significant part of the U.S. and worldwide power generation fuel mix for the foreseeable future.

◙ Regulations restricting CO2 emissions from existing and newly built emitting sources are looming on a horizon.

◙ It is likely that a significant percentage of existing power plants will be retrofitted with the post-combustion CO2 capture process. ◘ The major barriers to implementation of post-combustion CO2 capture

technology are significant reduction in power plant output and high performance penalty.

◙ Cycle and thermal integration offset part of performance and capacity penalty incurred by retrofit or implementation of post-combustion CO2 capture. ◘ For the state-of-the art amines (3.60 GJ/tCO2):

■ Rankine and H2-fueled Brayton cycle integration: Decrease in net unit efficiency incurred by implementation of post-combustion CO2 capture is reduced from 8.8 to 3.8%; gross power output is increased by 36%.

■ Rankine and Syngas-fueled Brayton cycle: Decrease in net unit efficiency incurred by implementation of post-combustion CO2 capture is reduced from 8.8 to 6.2%; gross power output is increased by 17%.

◙ Cycle and thermal integration should be implemented to power plants retrofitted or designed with post-combustion CO2 capture technology.

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