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Behavior of limestone in a large- scale pressurized fluidized bed combustor - attrition, fragmentation and SO 2 capture - T. Shimizu Niigata University S.Sakuno, N. Misawa, N. Suzuki, H. Ueda, H. Sasatsu, H. Gotou Electric Power Development Co., Ltd.

Behavior of limestone in a large- scale pressurized ... Shimizu Behavior... · Reaction mechanism (in TGA) CaCO 3 unreacted core CaSO 4 (product layer) SO 2 Reaction resistance at

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Behavior of limestone in a large-scale pressurized fluidized bed

combustor- attrition, fragmentation and SO2 capture -

T. ShimizuNiigata University

S.Sakuno, N. Misawa, N. Suzuki, H. Ueda, H. Sasatsu, H. Gotou

Electric Power Development Co., Ltd.

ABSTRACTCooperative research work between EPDC and Niigata Univ. on behavior of limestone in a 71MWe PFBC

Limestone attrition rateFragmentation of limestoneModel of SO2 capture by single limestone

particle under attrition conditionSO2 capture model in PFBC

Structure of this work

Ca in fly ash

Limestone attrition rate

Limestone fragmentation

Model of SO2 capture by CaCO3 under

attrition conditions

SO2 capture model of PFBC

This report summarizes the investigations on limestone behavior in 71MWe PFBC listed below:1. S. Sakuno et al., Nihon-Energy-Gakkai-Shi (J. Jpn. Inst.

Energy), 80, 747(2001)2. Ueda, H. et al., “Fluidization characteristics of PFBC,

attrition and fragmentation of limestone” Proc. 7th SCEJSymp. on Fluidization (Awaji, Japan), 524 (2001)

3. T. Shimizu, et al., Chemical Engineering Science, 56, 6719 (2001)

4. T. Shimizu et al., “A mathematical model of SO2 capture in PFBC”, Proc. 7th SCEJ Symp. on Fluidization (Awaji, Japan), 235 (2001)

5. T. Shimizu et al., To be presented at ISCRE 17 (Hong Kong, 2002)

EPDC’s Wakamatsu 71MWe PFBC Phase-1 test series: Without cyclone ash recirculation Phase-2 test series: With cyclone ash recirculation

MeasurementCoal feed rateLimestone feed rateLimestone size distributionAmount of bed material (limestone)Size distribution of bed materialFly ash drain rateCa content in fly ashSO2 emission

Size of fed limestoneSize<5mm

Fuel : coal

0

20

40

60

80

100

10 100 1000 10000

Dp [µm]

Cum

ulat

ive

wei

ght f

ract

ion

of li

mes

tone

(mea

sure

d) [%

]

Part.1

Evaluation of solid attrition rate and

fragmentation of limestone1)2)

Source of Ca in fly ash1)

(Ca in fly ash)>(fine limestone in feed)+(Ca in coal ash) fine formation by attrition

Run 1-15: Phase-1(W ithout fly ash recycle)Runs 16-33: Phase-2 (with fly ash recycle)

0%

20%

40%

60%

80%

100%1 4 7 10 13 16 19 22 25 28 31Run No.

Sou

rce

of C

ain

fly

ash

[%] F ines formed by attrition

Ca fines in fed limestoneCa in coal ash

Evaluation of limestone attrition rate(fine formation by attrition)=(Drain rate of Ca in fly ash)

- (fine limestone in feed)- (Ca in coal ash)

Surface area of bed material was calculated from size distribution and mass of bed material(Fine formation)/(Surface area) = Rate

Attrition rate

dR/dt = 1 - 2 µm/hr1)

No clear effect of coal type and load on rate.(R: radius)

0.0

0.5

1.0

1.5

2.0

30 40 50 60 70Plant power output [MWe]

Attr

ition

rat

e [

m/h

r]

A model of change in limestone particle size by attrition

A model of change in particle size due to attrition assuming constant attrition rate.

Particle size distribution of fed limestone

Particle size distribution of bed material (BM)

attrition

Bed material size distribution, comparison between model and experimental results1)

Some agreed but the others not. Why?1999/3/18Fuel: BASorbent:T5

0

20

40

60

80

100

100 1000 10000Dp [µm]

Cum

ulat

ive

wei

ght f

ract

ion

ofbe

d m

ater

ial [

%]

ExperModel

1999/12/10Fuel: BA(7)+PC(3)Sorbent:F1(8)+T1.5(2)

0

20

40

60

80

100

100 1000 10000Dp [µm]

Cum

ulat

ive

wei

ght f

ract

ion

ofbe

d m

ater

ial [

%]

ExperModel

Effect of coarse particle content on discrepancy between model and experimental results 1)

With increasing content of coarse particles, the discrepancy became larger.

Fragmentation of coarse particles by thermal shock

0.0

0.2

0.4

0.6

0.8

1.0

1.2

0 0.2 0.4 0.6 0.8

Wt-frac. >1.19mm in feed sorbent [-]

dp50

(est

)/dp5

0 (m

eas)

[-] Model = Experiment

Fragmentation of coarse particlesFragmentation of coarse particles was estimated by a model.

Particle size distribution of fed limestone

Particle size distribution of bed material

attrition

Estimated particle size distribution of limestone after fragmentation

Estimation of fragmentation

Fragmentation of coarse particles2)

Fragmentation of coarse particles was estimated by the model. Approx. 80% of coarse (3.4- 5.7 mm) particles was broken into small particles.

0.0

0.2

0.4

0.6

0.8

1.0

20 40 60 80

Plant power output [MW e]

Res

idua

l rat

io3.

36-5

.66m

m [-

]

Formation of smaller particles(0.25-0.5mm)

Phase-1: Only little formation of 0.25 – 0.5mmPhase-2: Nearly all of the fragments 0.25- 0.5mm

BA coal, Open symbols: Phase-1,Closed symbols: Phase-2

-0.6-0.4-0.20.00.20.40.60.81.01.21.4

20 40 60 80

Plant power output [MW e]

For

mat

ion

ratio

0.25

-0.5

0mm

[-]

Formation of smaller particles(0.5-1mm)Phase-1: Nearly all of the fragments 0.5- 0.1 mmPhase-2: Only little formation of 0.5 – 1 mm

BA coal, Open symbols: Phase-1,Closed symbols: Phase-2

-0.5

0.0

0.5

1.0

1.5

2.0

20 40 60 80Plant power output [MW e]

For

mat

ion

ratio

0.5-

1.19

mm

[-]

Summary of Part 1Considerable attrition of limestoneAttrition rate = 1 – 2 µm/hrFragmentation of coarse (>1.2mm ) limestoneSize of smaller particles formed by fragmentation was affected by cyclone ash recycle.

Part.2

A model of SO2 capture by limestone under solid attrition

conditions3)4)5)

Reaction mechanism (in TGA)

CaCO3unreactedcore CaSO4

(product layer)

SO2

Reaction resistance at unreacted core surface

Diffusion resistance through CaSO4 layer

TGA results (in literature): shrinking unreacted core model controlled by both reaction resistance and diffusion resistance through CaSO4 layer.

In actual PFBCs, attrition occurs.Role of attrition in SO2 capture by limestone -unknown. Two possible effects of attrition:

Attrition increases reaction rate by removing CaSO4 layer (diffusion resistance)

Attrition decreases solid utilization efficiency by removal of unreacted CaCO3

→Modeling work is necessary to evaluate the effect of attrition on SO2 capture rate and limestone utilization efficiency

Attrition model

Time

Radius Average slope = -α

Continuous attrition: α=average attrition rateRe= R0 –αt

Two different attrition modes:

0 τ 2τ 3τ

Intermittent (periodical) attrition: Re = R0 – int(t/τ)ατ (ατ<<particle

size)

Results: Initial reaction rate5)

At low SO2 concentrations (<100ppm), attrition mode affects reaction rate.

Conversion = 0 - 0.1

0.001

0.01

0.1

10 100 1000SO2 conc. [ppm]

aver

age

conv

ersi

on ra

tedX

/dt| a

v [1/

hr]

Continuous2hr period5hr period10hr period20hr period

Effect of attrition mode on removal of product layer at low SO2 concentration 5)

Continuous:Only CaSO4 is removed.Intermittent: CaCO3 is also removed.

Continuous IntermittentContinuous, SO2 20ppm

244

246

248

250

0 100 200 300Time [min]

Re,

Rc [

µm]

Re Rc

10hr period, SO2 20ppm

210

220

230

240

250

0 1000 2000Time [min]

Re,

Rc [

µm]

Re Rc

CaSO4

CaCO3

removed byattrition

Effect of attrition rate on limestone utilization efficiency 5)

Continuous: No changeIntermittent: Attrition decreases efficiency.

SO2 100 ppm, Conv. = 0 - 0.1

0.0

0.2

0.4

0.6

0.8

1.0

0 1 2a [µm/hr]

Max

imum

con

vers

ion 

[-]

ContinuousPeriod 2hrPeriod 5hrPeriod 10hr

Effect of attrition rate on apparent reaction rate 5)

Continuous: Attrition increases rate.Intermittent: No change in reaction rate.

SO2 100 ppm, Conv. = 0 - 0.1

0.00

0.01

0.02

0.03

0 1 2a [µm/hr]

dX/d

t| av 

[1/h

r]

ContinuousPeriod 2hrPeriod 5hrPeriod 10hr

IF continuous attrition occurs in PFBC …Attrition rate = SO2 capture rate

However, in 71MWe PFBC SO2 capture rate was only 1/3 of attrition rate 3).

SO2 capture=attrition rate

0

0.5

1

0 1 2 3 4

Total Ca attrition rate in PFBC[mol/s]

Tota

l SO

2 ca

ptur

e ra

tein

71M

We

PF

BC

[mol

/s]

SO2 capture=0.3x(attrition)

Intermittent attrition model is applied.

Simplified SO2 capture model for intermittent attrition model 3)

Assumptions:

Diffusion resistance >> Reaction resistanceControlled by diffusion through CaSO4

Fresh surface appears when attrition occurs Product layer thickness = 0 when attrition

occurs

Product layer thickness << Particle sizeFlat surface

Simplified rate expression of SO2capture for intermittent attrition model 4)

SO2 capture rate per unit external surface area of limestone:

rS = (2Deρ/Mτ)1/2 C1/2

De: Effective diffusivity

τ: Period of attritionC: Concentration of SO2

ρ/M: Molar density of CaCO3 in limestone

Simplified SO2 capture model in PFBC 4)

Assumptions:

Char-S forms SO2 uniformly in bedSO2 formation rate per unit volume of bed

Bed consists of Geldart’s “D” particlemass transfer resistance from bubble to

emulsion is sufficiently small plug flow model

VM-S forms SO2 at the bottomSO2 concentration at the bottom

Comparison between model and experimental results 4)

Attrition interval was given as a fitting parameter.By giving τ=5 hr, model agreed well with experimental results.

τ =18000s = 5h

0

10

20

30

40

0 10 20 30 40SO2 (calc.) [ppm]

SO

2 (e

xper

.) [p

pm]

Is τ=5 hr appropriate?Best fit between model and experiments was obtained at τ=5 hr.ατ = (1- 2 µm/hr)x(5 hr) = 5 - 10 µm<< Particle size (>250 µm)

For further analysis, measurement of size distribution of Ca-rich fines in fly ash by CC-SEM is necessary.

CONCLUSION Behavior of limestone in 71 MWe PFBC was analyzed.

Attrition rate of limestone was 1-2 µm/hr. Limestone particles greater than 1.2 mm was broken when they are fed into PFBC.Limestone attrition mode (continuous or intermittent) plays significant role in SO2

capture. Continuous attrition model over-estimates SO2 capture in PFBC.

CONCLUSION (continued)Intermittent attrition model agreed PFBC results when period of attrition was given as τ=5hr.To establish complete model, period of attrition should be experimentally determined. Size distribution of Ca-rich particles in the fly ash is necessary for further study.

AcknowledgementT. Shimizu thanks The Ministry of Education, Culture, Sports, Science and Technology for Grant-in-Aids (No.11218204).

The authors express their thanks to The Ministry of International Trade and Industry, Agency of Natural Resources and Energy, and Center for Coal Utilization, Japan, for the financial support for 71MWe PFBC project.