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CFD modelling of fluidised bed combustion plants - … · CFD modelling of fluidised bed combustion...

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CFD modelling of fluidised bed combustion plants IEA Workshop: CFD aided design and other design tools for industrial biomass combustion plants Thursday, 6th June 2013 Marko Huttunen, Perttu Jukola VTT Technical Research Centre of Finland
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Page 1: CFD modelling of fluidised bed combustion plants - … · CFD modelling of fluidised bed combustion plants ... UDF’s + built-in sub-models of Fluent . 3’ry 2’ry 1’ry+FGR .

CFD modelling of fluidised bed combustion plants

IEA Workshop: CFD aided design and other design tools for industrial biomass combustion plants Thursday, 6th June 2013 Marko Huttunen, Perttu Jukola VTT Technical Research Centre of Finland

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Outline

CFD Modelling Activities on Combustion at VTT CFD Modelling of Fluidised Bed Combustion Plants- An Overview

Modelling of Combustion in BFB furnaces

Modelling Approach Examples of Case Studies Some On-going and Planned Activities at VTT

Concluding Remarks

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CFD Modelling Activities on Combustion at VTT

CFD Applied to Combustion Modelling since 1984 Major Applications:

BFB Boiler Furnaces PF- Combustion

Boilers and Burners Coal, Peat, Co-firing, Oil shale

Grate Fired Furnaces

Recovery Boilers CFB Boiler Furnaces

Staff: 9 researchers

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CFD Modelling of Fluidised Bed Combustion Plants- An Overview (1/2)

Roughly 15 to 20 Boilers Analysed During Last Ten Years

Boiler Size Range: Fuel Power from 10 to 300 MW

Fuel and Fuel Mixtures: Fresh wood (chips, bark, forest residue) Peat Sludge REF

Furnace Models Employed as a Design Tool in Close Co-Operation with

Boiler Operators and Designers (mostly confidential contract work)

Furnace Models Developed Simultaneously with Practical Cases Implementation of new sub-models (mainly from literature) Fine-tuning of existing models Finding best practises (e.g. definition of BC’s,

combination of sub-models)

3’ry

2’ry

1’ry+FGR

SNCR

SNCR

Fuel

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CFD Modelling of Fluidised Bed Combustion Plants- An Overview (2/2)

Furnace Model Development Based on

Feedback from customer (plant data, practical observations) Furnace measurements, if available Predictions of more detailed models of separate sub-processes

Some Issues Considered by Modelling: Reduction of NOx by primary methods and SNCR Combustion efficiency (CO, UBC) Furnace availability (tendency for fouling, slagging, corrosion)

By in-direct methods (control of furnace gas temperature, solid fuel and gaseous conditions near furnace walls)

Bed behaviour (bed temperature) Heat transfer to water walls Criteria for incineration of wastes (2 sec. /850 ºC)

FLUENT as Solver

UDF’s + built-in sub-models of Fluent

3’ry

2’ry

1’ry+FGR

SNCR

SNCR

Fuel

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Modelling of Combustion in BFB furnaces- A Modelling Approach (1/2)

FREEBOARD Model: solve fluid and particle flow, combustion, heat transfer

BED Model: Solve heat and mass balance

Exchange of mass and heat

H(FGR) H(1’ry air)

Q (particle heat)

∆H (latent heat)

1. ∆H (char burning)

2. ∆H (volatiles burning)

Q (rad + convection)

Bed heat balance

DOM-radiation (built-in), Eddy dissipation (EDCM or EDC), 2-eqs. turbulence models (built-in),

Langrangian particles + UDF’s for particle conversion, 2(3) –step global schemes for main chemistry, NOx sub-model for BFB combustion

(global chemistry + mixing)

User-implemented or built-in sub-models of Fluent, if stated above

Sand, ∆H

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Particle Mixing and Conversion in Bed Non-Splash model

Particles ‘trapped’ as they reach bed surface Remaining moisture and volatiles of particles

released at or close to location of particle landing

Splash Model Track particles in splash zone and in freeboard

Bed (Mean) Temperature Fixed or Estimated

Fix Bed Temperature, Estimate Heat of

Combustion in Bed by Bed Heat Balance

Fix Heat of Combustion in Bed, Estimate Bed Temperature by Bed Heat Balance

Modelling of Combustion in BFB furnaces- A Modelling Approach (2/2)

Non-Splash

Splash

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0.92

0.94

0.96

0.98

1

1.02

1.04

1.06

1.08

Bed Temp

CASE #

Bio/Peat =70/30 (by heat, 175 MW,f )

0

0.2

0.4

0.6

0.8

1

1.2

1.4

1.6

00.20.40.60.8

11.21.41.6

NOx

CASE #

CO

Bio/Peat =70/30 (by heat, 175 MW,f ) CO, w-ppm,nose

NOx[mg/m3,n,6% o2]

0.88

0.9

0.92

0.94

0.96

0.98

1

1.02

0.88

0.9

0.92

0.94

0.96

0.98

1

1.02

FEGT, meanFEGT, max

CASE #

Bio/Peat =70/30 (by heat, 175 MW,f ) FEGT,maxFEGT,mean

Modelling of Combustion in BFB furnaces- Examples of Case Studies (1/5)

Reduce Emissions (CO, NOx) of Existing Boiler Design (175 MWf; Bio/Peat = 70% / 30 % of Fuel Power) Arrangement and Positioning of Air Nozzles, Nozzle Damper

Positioning and Air Staging are Considered Furnace Exit Gas Temperature [FEGT] at Nose Elevation

Monitored to Assess Risks for Upper Furnace Corrosion and Fouling Tendency

Bed Heats Monitored to Assess Risk of Bed Sintering

NEW DESIGN VS. EXISTING DESIGN:

Reduction of NOx: ~ 30 % Reduction of CO: ~ 30-70 %

Peaks of FEGT (at nose elevation) lowered due

to enhanced mixing

Rise of Bed Temperature a Concern

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400

500

600

700

800

900

1000

1100

1200

1300

1400

2BR 2FR 2FL

Tem

p [C

]

Rauma, Bark

Ave

Measured

Max

Min

400

500

600

700

800

900

1000

1100

1200

1300

1400

3RC

Tem

p [C

]

Rauma, Bark

Ave

Measured

Max

Min

400

500

600

700

800

900

1000

1100

1200

1300

1400

4RF 4FC 4LB

Tem

p [C

]

Rauma, Bark

Ave

Measured

Max

Min

400

500

600

700

800

900

1000

1100

1200

1300

1400

5RF 5RC 5FC 5LB

Tem

p [C

]

Rauma, Bark

Ave

Measured

Max

Min

400

500

600

700

800

900

1000

1100

1200

1300

1400

6RF 6RC 6LF

Tem

p [C

]

Rauma, Bark

Ave

Measured

Max

Min

Comparison of Measured and Predicted In-furnace Gas Temperature (107 MWf; Bark)

Good Agreement in Upper Furnace Unbalanced Temperature in Upper Furnace

(Cf. 6RF To 6RC And 6LF) Captured Also by the Model

Most Discrepancies for Gas Temperatures Exist at Lower Part of Furnace

Large Gradients of Temperature

in Lower Furnace Predicted by Model

Minor Changes at Expected Measuring Locations May Yield Better (or Worse) Agreement

Modelling of Combustion in BFB furnaces- Examples of Case Studies (2/5)

Part of the work has been carried out within the project ChemCom 2.0 (2008-2010)

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50

70

90

110

130

150

170

190

210

Incid

ent H

eat F

lux [

kW/m

2]

Rauma, Bark Simulated

Measured

Sim-Max

Sim-min

LHSW RW RHSW FW

Floor 2 +11.500 m (+13.000m)

Floor 3 +15.500 m (+16.000m)

Floor 4 +18.700 m (+19.500m)

Floor 5 +23.000 m (+23.800m)

Floor 6 +27.500 m (+29.000m)

Floor 2 +11.500 m (+13.000m)

Floor 3 +15.500 m (+16.000m)

Floor 4 +18.700 m (+19.500m)

Floor 5 +23.000 m (+23.800m)

Floor 6 +27.500 m (+29.000m)

Modelling of Combustion in BFB furnaces- Examples of Case Studies (3/5)

Predictions of Incident Radiation and Measured Values are Compared (107 MWf; Bark)

Most Intense Measured Heat Fluxes Exist at Floors 3 And 4, and This is also Realised by the Model

Part of the work has been carried out within the project ChemCom 2.0 (2008-2010)

Model, Surface Incident Radiation [kW/m2]

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1

10

100

1000

10000

100000

600

700

800

900

1000

1100

1200

1300

1400

1500

1600

10 15 20 25 30 35 40

CO Volume Fraction

In-Furnace Gas Temperature

furnace elevation [m]

RAUMA, Bark, Day 1

Tave [C]

Tmax [C]

COave (ppm)

Nose Secondary

Modelling of Combustion in BFB furnaces- Examples of Case Studies (4/5)

Furnace Profiles (107 MWf; Bark)

High Temperature Regions at Secondary Air Level, where Most Intense Combustion Takes Place

Peaks of In-Furnace Gas Temperatures ~ 1400-1500 C

Low Emission of CO Predicted by the Model Measured 25-30 v-ppm

Part of the work has been carried out within the project ChemCom 2.0 (2008-2010)

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REDUCE FURNACE SLAGGING Particle concentration near walls

Old New

Modelling of Combustion in BFB furnaces- Examples of Case Studies (5/5)

REDUCE SUPERHEATER /REHEATER SLAGGING Combustion rate of char in freeboard)

Old New

(178 MWf; Bio/Peat = 45% / 55 % of Fuel Power) (294 MWf; Bio/Peat = 30% / 70 % of Fuel Power)

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Incorporation of Ash Chemistry into CFD Ash Melting Behaviour, Slagging, Heat Transfer

Fuel Particles

Fragmentation, Mixing in Bed

Improved Understanding of Bed Processes Utilize multiphase CFD Simulations of Bed

Integration of CFD Furnace Model with Process Modelling

Linking of Furnace and Water/Steam Cycles

Transient Simulation e.g. Load Changes

Modelling of Combustion in BFB furnaces- Some On-going and Planned Activities at VTT

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Concluding Remarks Furnace Models Employed to Analyse Real Processes

Design of New Furnace Concepts Retrofitting

Simultaneous Development of Furnace Models Based on Experiences of Modelling of Real processes

Combustion Modelling Motivated Largely by Reduction of Emissions (IED) and Furnace Availability Issues European Patent Application ”Method for reducing nitrogen oxide

emissions and corrosion in a bubbling fluidized bed boiler and a bubbling fluidized bed boiler”, (Application No. EP12397524, Applicant Fortum OYJ)

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VTT creates business from technology


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