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CHEMICAL REACTION ENGINEERING LABORATORY
CARPT Calibration IssuesCARPT Calibration IssuesPoster 1
Bad Reconstruction
Calibration CurveCountsDis
tan
ce (
cms)
dE/d vs
0
0.2
0.4
0.6
0.8
1
1.2
1.4
0 100 200 300 400 500 600 700 800 900 1000
in mV
dE/d
det_9
Det_A
Det_K
Det_L
Det_M
Det_N
Det_O
Det_P
Det_Q
Det_R
Photo PeakCompton 0.89
Mev1.12 Mev
Full Spectrum
-8 -6 -4 -2 0 2 4 6 8-8
-6
-4
-2
0
2
4
6
8
r in cms
r in
cm
s
comparison of reconstructed vs actual calibration points in the entire column
2 Approach
Good Reconstruction
Proposed Solution to HPBCR
Acquire Photopeak
GoodCalibration Curve
CHEMICAL REACTION ENGINEERING LABORATORY
Gas Liquid Studies in Stirred Tank ReactorGas Liquid Studies in Stirred Tank Reactor
• New techniques in CT implementation result in better reconstruction!!! How ???
• Cross sectional gas holdup distributions (at different axial planes) in a Stirred Tank Reactor (for the first time!!)
• Detailed local fluid dynamic information in gas-liquid flows in stirred tank (for first time!!)
N=100 rpm, QG=7.5 lit/min, Z=10.0 cms
2.3mm
1.0mm
0.8mm
250 m
150 m
Poster 2
Poster II:Effect of Nozzle Orientation of the Cross Sparger Poster II:Effect of Nozzle Orientation of the Cross Sparger and Pressure on Bubble Columnand Pressure on Bubble Column HydrodynamicsHydrodynamics
CHEMICAL REACTION ENGINEERING LABORATORY
Peter SpickaPeter Spicka• research associate research associate
at CREL since 2001at CREL since 2001• bubble columns, bubble columns,
trickle bedstrickle beds• CT & CARPT CT & CARPT
experimental experimental studies and CFD studies and CFD simulationssimulationsPoster I: Review of CARPT/CT Experimental Database Poster I: Review of CARPT/CT Experimental Database
for Bubble Columns Operating in the Churn-for Bubble Columns Operating in the Churn-Turbulent RegimeTurbulent Regime
Contributors: Jinwen Chen, Abdenour Kemoun, Sailesh Kumar, Shadi Saberi, Sujatha Degaleesan, Puneet
Gupta, Booncheng Ong, Shantanu Roy, Qingi H. Wang
Review of CARPT/CT Experimental Database for Bubble Columns Operating in the Churn-Turbulent Regime
-60.0
-40.0
-20.0
0.0
20.0
40.0
60.0
0.0 0.2 0.4 0.6 0.8 1.0r/R
Axi
ally
Ave
rag
ed A
xia
l Ve
loci
ty,
cm/s
Air-Water
Air-Drakeoil
Ug=10 cm/s
DOE project (1995-2002)DOE project (1995-2002)
Participants: Air Products, Ohio State University, Sandia National Laboratories and Washington University
Objectives:1. effect of specific variables on observed flow
patterns in bubble columns2. engineering type models for flow and mixing
in bubble columns3. data for gas hold-up, velocity and turbulence
profiles for validation of CFD codes
Different effects studied:• gas superficial velocity, liquid
properties, pressure• column diameter, internals, gas
distributor and solids concentration
Scale up of bubble columns:• correlations for liquid centerline
velocity, gas holdup, holdup and liquid velocity radial profiles and eddy diffusivities
Effect of Nozzle Orientation of the Cross Sparger and Pressure on Bubble Column Hydrodynamics
Experiment• 6” I.D. stainless steel column• cross-sparger, two nozzle
orientations: facing upward and downward
• Air-water system• Pressure: 1 bar and 4 bars• UG= 5 cm/s (only CT) and 20
cm/s
Nozzle orientation of the sparger
• important design issue since it may affect the length of the flow development region (Schollenberger et al., 2000)
• sparse information in the available literature
Goals• to quantitatively determine the variation of gas hold-up, liquid recirculation and
mixing due to variations in nozzle orientation and pressure • to compare the exp. data with 1-D recirculation model due to Kumar (1992)
-10
1r/R
2
4
6
8
x/D
0.400.360.320.280.240.200.160.120.080.040.00
Gas Holdup
U
z[c
m/s
]
0 0.2 0.4 0.6 0.8 1-60
-40
-20
0
20
40
60
exp., 1 barexp., 4 barsmodel, 1 barmodel, 4 bars
Gas holdup Liquid velocity profile
CHEMICAL REACTION ENGINEERING LABORATORY
Development of Improved Engineering Models for Flow, Development of Improved Engineering Models for Flow, Mixing and Transport in Bubble ColumnsMixing and Transport in Bubble Columns
(Review of Phenomenological Model accomplished in CREL during 1995-2001)(Review of Phenomenological Model accomplished in CREL during 1995-2001)
Tracer experiments during Methanol, Fischer-Tropsch and Dimethyl Ether Synthesis
Gas tracer: Ar41
Liquid tracer: Powdered oxide of Mn56 (Mn2O3)
suspended in the heat transfer oil
Solid tracer: Catalyst particles doped with an oxide of Mn56
CHEMICAL REACTION ENGINEERING LABORATORY
ContentsContents
• Suitability of the Axial Dispersion Model• One Dimensional Recirculation Model• One Dimensional Recycle with Cross Flow and Dispersion Model• Two-Dimensional Convection-Diffusion Model• Gas Phase Recirculation and Dispersion Model• Scale-up Strategy• Comparison of experimental and simulated tracer responses
Level 3 (3.9 m)
0.0
0.2
0.4
0.6
0.8
1.0
0 20 40 60 80 100Time (sec.)
Nor
mal
ized
Res
pons
e
Sim.
Inj. 2
Inj. 3
Inj. 4
Inj. 5
Inj. 6
Inj. 7
0.0
0.2
0.4
0.6
0.8
1.0
0 20 40 60 80 100Time (Sec.)
No
rma
lize
d R
es
po
ns
e
Exp.
No Attenuation
With Attenuation
Level 13.5
•What is the next step?
CHEMICAL REACTION ENGINEERING LABORATORY
Radioactive Tracer Studies in the AFDU Reactor during Radioactive Tracer Studies in the AFDU Reactor during Dimethyl Ether (DME) SynthesisDimethyl Ether (DME) Synthesis
W
N
S
E
Fresh Feed
0.46 m
Gas Tracer InjectionRecycle
Syngas In
Syngas/Products Out
DET
1.83m
2.74m
0.61m
1.74m
1.52m
1.52m
2.74m
2
1
3
4
5
6
7 DET
DET
DET
DET
DET
DET
DET
DET
13.25m
r/R = 0.6r/R = 0.35
24 tubes of 1” O. D.
DME Synthesis
Reactor Insulation
Reactor Wall
Down-flow of Gasand LiquidUp-flow of Gas and Down-
Flow of Liquid
Up-flow of Gasand Liquid
Detector
Lead Shielding
cross-section along with scintillation detectors and their lead shielding
CHEMICAL REACTION ENGINEERING LABORATORY
Schematic of the reactor compartmentalization for the gas-Schematic of the reactor compartmentalization for the gas-liquid mixing model with interphase mass transfer (Gupta, 2001)liquid mixing model with interphase mass transfer (Gupta, 2001)
GG22 LL22GG11 LL11
Qg
Qg1Qg2
Cl1Cl2Cg1Cg2
Clb
ClaQl1Ql2
Cg, in
x = 0
x = L
Cgb
Cga
Ql Cl, in
Qg Ql
Level 3 (3.9 m)
0.0
0.2
0.4
0.6
0.8
1.0
0 20 40 60 80 100Time (sec.)
No
rma
lize
d R
es
po
ns
e
Sim.
Inj. 2
Inj. 3
Inj. 4
Inj. 5
Inj. 6
Inj. 7
Level 5 (9.4 m)
0.0
0.2
0.4
0.6
0.8
1.0
0 100 200 300 400 500 600
Time (sec.)
Nor
mal
ized
Res
pons
e
Simulation
Exp. (Inj. 3)
Exp. (Inj. 4)
Exp. (Inj. 5)
Level 6 (11.2 m)
0.0
0.2
0.4
0.6
0.8
1.0
0 100 200 300 400 500 600 700 800
Time (sec.)
No
rma
lize
d R
es
po
ns
e
Simulation
Catalyst (N2 Center)
CHEMICAL REACTION ENGINEERING LABORATORY
Implementation of Breakup and Coalescence Models into CFD of Implementation of Breakup and Coalescence Models into CFD of Bubble Column FlowsBubble Column Flows
G
G
L
The engineering models needs input
Only Eulerian model seems feasible for churn turbulent flow regime
In churn turbulent regime, bubble size is widely distributed; the mean bubble diameter seems to be the simplest assumption
However, it is difficult to choose the “right” bubble diameter without going through tedious trial-and-error procedure
If one try to change to another column or operation condition, the “right” bubble diameter normally may not work any more
We need to predict rather than input bubble diameter, we had better predict it locally!
???
Chemical Reaction Engineering Laboratory (CREL)
CFD Modeling of Bubble Column Flows(Review of CFD activities in CREL 1995-2001)
Gas Outlet
Gas Inlet
Gas Outlet
Gas Inlet
Bubbly flow regime Churn turbulent regime
Outline:•Hydrodynamics of bubble columns
•Eulerian-Eulerian Two-Fluid Model•Algebraic Slip Mixture Model (ASMM)
•Hydrodynamics of (passive) tracers (gas/liquid) in bubble column flows•Implementation of the Bubble Population Balance in CFD
Compiled by: M. Rafique•Research Associate•Ph.D. (Fluid Mechanics), INPL, France
Contributors:•Dr. M. P. Dudukovic•Dr. M. H. Al-Dahhan•Dr. S. Kumar•Dr. Y. Pan•Dr. M. Rafique•Mr. P. Chen
Acknowledgement: DOE Contract: DE FC 22 95 PC 95051
Chemical Reaction Engineering Laboratory (CREL)
D=15.2 cm
0.2 cm
L=
10D
=15
2 cm
Ug =1cm/s
width
10 cm
D=15.2 cm
0.2 cm
L=
10D
=15
2 cm
Ug =1cm/s
width
10 cm
2D 3D
Mesh system &
Gas holdup contours
2D & 3D dynamic simulations
Chemical Reaction Engineering Laboratory (CREL)
0 sec 2 sec 4 sec 6 sec 9 sec 19 sec
Numerical (liquid) Tracer Study Numerical particle tracking (calculation of turbulent diffusivities)
Chemical Reaction Engineering Laboratory (CREL)
Meso-scale modeling of bubble column flows
M. Rafique, M. H. Al-Dahhan, M. P. Dudukovic
Objective: •To simulate the bubble column hydrodynamics by resolving meso-scale flow structures through grid refinement.•To study the effect of attraction and repulsion forces on the hydrodynamics
D=15.2 cm
0.2 cm
Ug=1cm/s
width
10 cm
D=15.2 cm
L =
110
cm
Ug=1cm/s
10 cm
Fin
e g
rid
(0
.2x
0.2
5 c
m)
Co
ars
e g
rid
(0
.5x
0.5
cm
)
Chemical Reaction Engineering Laboratory (CREL)
Coarse gridCd+Cv
Fine gridCd+Cv
Fine gridCd+Cv+Catt
Instantaneous contours of gas volume fraction
Optical Fiber Probes for Bubble DynamicsMeasurement in Bubble Columns
J. L. Xue, M. H. Al-Dahhan & M. P. Dudukovic
In cooperation withRobert F. Mudde
Delft University of Technology, The Netherlands
Chemical Reaction Engineering Laboratory (CREL)
November, 2001
CHEMICAL REACTION ENGINEERING LABORATORY
Measurement of Bubble Dynamics in BubbleColumns Using Four-point Optical Probe
J. L. Xue, M. H. Al-Dahhan & M. P. Dudukovic
In cooperation withRobert F. Mudde
Delft University of Technology, The Netherlands
Chemical Reaction Engineering Laboratory (CREL)
Oct. 24, 2002
CHEMICAL REACTION ENGINEERING LABORATORY
bubble dynamics, i.e. bubble size distribution, bubble velocity distribution, specific interfacial area and gas holdup are among the key parameters that affect the hydrodynamics in bubble columns.
Measurement of bubble dynamics is difficult, especially in churn-turbulent flows.
Non-invasive techniques, e.g. video imaging techniques, are limited to 2-D transparent columns. and can not be used in real 3-D systems which are opaque due to high volume fraction of the dispersed phase.
Optical probes can be applied in practical 3-D systems. The measurements of bubble dynamics by two-point probes are not reliable. Four-point optical probe was adopted in this research to measure the bubble dynamics in bubble columns.
Motivation
CHEMICAL REACTION ENGINEERING LABORATORY
L
r
Probe
Tip0
Tip3
Tip1
Tip2
L
r
Probe
Tip0
Tip3
Tip1
Tip2
Tip1
Tip3 Tip2
Tip0
rr
r
Tip1
Tip3 Tip2
Tip0
rr
r
Bottom view
Side view
With a new data processing algorithm, it can measure:
Bubble velocity vector
Bubble size
Specific interfacial area
Gas holdup
The Configuration of the Four-point Optical Probe
Computed Tomography
in
Slurry Bubble Column Reactors
Ashfaq Shaikh, M.H. Al-Dahhan
CHEMICAL REACTION ENGINEERING LABORATORY
CREL Annual MeetingOctober 24, 2002
Acknowledgements: DE-FG-26-99FT40594
• Evaluate the CT/Overall gas holdup algorithm
Mimic fluid System: Therminol LT-air-glass beads (150 m)
Single source CT Two-phase systems
Three-phase systemsOne equation, two unknowns
Need one more equation
CHEMICAL REACTION ENGINEERING LABORATORY
CT/Overall gas holdup (Rados, 2002)
Sensitivity analysis
Assumptions in CT/Overall gas holdup procedure has been critically examined
Assessing and Reinforcing the Phenomenological Assessing and Reinforcing the Phenomenological Consistency of Multiphase Flow Artificial Neural Consistency of Multiphase Flow Artificial Neural
Network CorrelationsNetwork Correlations L.A. Tarca, B.P.A. Grandjean, F. Larachi
Classically built ANN models may be phenomenological consistent in vicinity of some data points but not in the whole input space Large prediction errors
800
1000
1200
1400
1600
1800
2000
3.0E-03 8.0E-03 1.3E-02
L(kg/m.s)
D P
/Z (P
a/m
)0
200
400
600
800
1000
1200
1400
1600
1800
2000
0 0.5 1 1.5
Gas superficial velocity, UG (m/s)
Irri
ga
ted
pre
ss
ure
dro
p, D
P/Z
(P
a/m
)
Liquid Viscosity
(r L = 1150 kg/m3)
f - L = 1 cP
D - L = 10 cP
O - L = 20 cP
(d)
Piché et al. (2001) [3]Counter-current packed bed
0)/(
1
D
pL
ZP
0
)/(
2
D
pL
ZP
,,,,Re,,Re/ BLLLGG SStGaGaANNZP D
L
Using phenomenological error (PCE) of the trained models we guide a Genetic Algorithm search for pertinent dimensionless numbers to predict a reactor characteristic
otherwise
a
yyy
U
y
U
yif
fkkkkk
k
pTpLpGpLpG
PCp
0
0)(
&0)(
&0)(
&0)(
&0)(
1
r
T
k
PCp
N
fPCE
k
1100[%] Phenomenological Consistency Error
Phenomenological and prediction error decrease by combining multiple “good” ANNs
g
ZPy
Lr/D
Pressure drop in counter-current packed
beds
……
bm1
…
…
bm2
……
bm3
1
2
3
gZP
Lr/D
UG
UL
rG
L
aT
Z
DC
rL
L,G
log
log
log ^10
N10N13N14N18N23N26N27
N9N10N13N14N21N24N27
N10N14N17N18N24N27
……
bm1
…
…
bm2
……
bm3
1
2
3
UG
UL
rG
L
aT
Z
DC
rL
LG
log
log
log ^10
N10N13N14N18N23N26N27
N9N10N13N14N21N24N27
N10N14N17N18N24N27
THEORY OF TRICKLE BED MAGNETOHYDRODYNAMICS IN INHOMOGENEOUS MAGNETIC FIELDS – Potential route to process intensification by I. Iliuta and F. Larachi
0
6000
12000
18000
24000
-1000 -500 0 500 1000
BdB/dz (T2/m)
P/H
, Pa/
m
Liquid velocity=0.007 m/sLiquid velocity=0.002 m/s
(b)
FMg+
FMl-
FMg-
FMl+
0
0.05
0.1
0.15
0.2
0.25
0.3
-1000 -500 0 500 1000BdB/dz, T2/m
L
Liquid velocity=0.007 m/s
Liquid velocity=0.002 m/s
(a)
FMg+
FMl-
FMg-
FMl+
When magnetic gradients are negative,liquid holdup decreases with increasing|BdB/dz| because the driving force (two-phase pressure drop) increases
- for negative magnetic gradients, the upward gas magnetization force reduces the effect of gravity (sub or micro-gravity) and two-phase pressure drop increases
When magnetic gradients are positive, liquid holdup increases with increasing |BdB/dz| because the driving force decreases
-for positive magnetic gradients, gas magnetization force amplifies the effect of gravity (macro-gravity) and two-phase pressure drop is reduced
rG=47
kg/m3
rG=1.2
kg/m3
0.4
0.48
0.56
0.64
0.72
-100 0 100 200 300 400 500 600 700
BdB/dz, T2/m
Phe
nol c
onve
rsio
n
0.2
0.4
0.6
0.8
1
Wet
ting
effic
ienc
y
vSL=0.001 m/svSG=0.0283 m/sCP,0=0.01 mol/l
(a)
0.4
0.5
0.6
0.7
0.8
0.9
-100 0 100 200 300 400 500 600 700
BdB/dz, T2/mP
heno
l con
vers
ion
0.2
0.4
0.6
0.8
1
Wet
ting
effic
ienc
y
vSL=0.0005 m/svSG=0.0283 m/sCP,0=0.01 mol/l
(b)
Elevated levels of magnetic field gradient improve the liquid holdup and thus the wetting efficiency of the catalyst particle
Because phenol oxidation is liquid-reactant limited, as catalyst wetting improves the phenol conversion increases significantly
Prediction of HETP for randomly packed tower operation: Prediction of HETP for randomly packed tower operation: Integration of aqueous and non-aqueous mass transfer Integration of aqueous and non-aqueous mass transfer characteristics into one consistent correlationcharacteristics into one consistent correlation
Simon PICHÉ, Stéphane LÉVESQUE, Bernard GRANDJEAN, Faïçal LARACHIDepartment of chemical engineering & CERPICQuébec, CANADA G1K 7P4
L
G
L
G
S
POLLUTION CONTROL: Particulate removal, SO2, NOX, VOC & TRS scrubbing
WATER PURIFICATION: Ammonia stripping and recovery, VOC stripping
DISTILLATION: Styrene purification (Ethylbenzene - Styrene separation)
(Vacuum or Pressure) Demethanizers (ex: CH4 removal / heavy feedstock)
OBJECTIVE: Build a new, efficient & consistent correlation using
an artificial neural network, dimensionless analysis & data (HETP,
KGaW, KLaW) reconciliation procedure that could predict either HETP
for distillation or kGaW, kLaW, KGaW & KLaW for absorption and stripping
DATABASE: 3770 absorption/stripping measurements
2357 distillation measurements
(1) Testing of ANN correlations developed for aqueous solutions [1] on HETP (non-aqueous solutions)
(2) Extraction of pseudo interfacial areas from HETP and mass transfer coefficients
(with previously developed ANN-k) & development of new interfacial area correlation (ANN-aW)
(3) Weights reconciliation on the 6 mass transfer parameters (HETP, aw, kLaw, kGaw, KLaw, KGaw)
General procedure and Results
ANN-kI
k (cal)
aw (pseudo)
(5,802 data)
aw (exp)
(325 data)
ANN-aw(3)
ANN-aw(3) & ANN-k
I weights reconciliation
HETP, KLaw, KGaw, kLaw, kGaw, aw (6,127 data)
ANN-awII ANN-k
II
HETP, Kaw & kaw (exp)
(5,802 data)
ANN-awI & ANN-k
I testing on HETP
= 76%, = 100%
[1] Piché, S., Larachi, F. & Grandjean, B., Reconciliation procedure for gas-liquid interfacial area and mass transfer coefficient in randomly packed towers, Ind. Eng. Chem. Res., 41 (19) (2002) 4911-4920 .
ANN STRUCTURES: = G (gas) and L (liquid)
[1] aw/aT = f (ReL, FrL, EoL, wall factor, ) – ANN-awI
k/(aTD) = f (Re, Fr, Sc, ) – ANN-kI
This work
aw/aT = f (ReL, FrL, EoL, wall factor, RSI) - ANN-awII
k/(aTD) = f (Re, Fr, Sc, ) – ANN-kII
RSI (Relative stability index) = (dL/dxvol) / L(mixture)
RSI=0 (aqueous solutions); RSI<>0 (non-aqueous
mixtures)
STATISTICAL PERFORMANCE:
HETP (N=2357, =21%); aW/aT (N=325, =24%);
kLaW/kGaW (N=1461, =23%); KLaW/KGaW (N=1984,
=29%)
CHEMICAL REACTION ENGINEERING LABORATORY
Modelling of Radioactive Tracer Distribution in Bubble Columns
bbyy
Chengyu MaoChengyu Mao
Advisor: Prof. M.P. DudukovicAdvisor: Prof. M.P. Dudukovic
Prof. P.A. RamachandranProf. P.A. Ramachandran
CHEMICAL REACTION ENGINEERING LABORATORY
Liquid Recirculation Model
Recycle with Cross Flow and Dispersion Model (RCFDM)
Single Bubble Class Model (SBCM)
Distributed Bubble Size Model (DBSM)
Two Dimensional Convection with Eddy Diffusion Model
Many engineering models are available for description of flow, mixing, and transport in bubble columns. However, their accuracy to simulate and predict experimental data needs to be verified.
CHEMICAL REACTION ENGINEERING LABORATORY
Single Bubble Class Model (SBCM)
Two Dimensional Convection with Eddy Diffusion Model
Liquid tracer concentration distribution
Method 1
Calculate Cross-Sectional concentration, normalize and compare with data
Method 2
Calculate 2D Response accounting approximately for the attenuation of radiation, normalize and compare with data
Method 3
Calculate 3D Response accounting fully for the attenuation of radiation, normalize and compare with data
Liquid MaldistributionLiquid Maldistributioninin Trickle Bed Reactors Trickle Bed ReactorsExperimental and CFD Modeling StudyExperimental and CFD Modeling Study
M.P. Dudukovic, M.H. Al-Dahhan, P. SpickaChemical Reaction Engineering Laboratory, Washington University
St Louis, USA
D. Védrine, J. BousquetCentre Européen de Recherche et Technique, TOTALFINAELF
Harfleur, FRANCE
Nicolas DromardMaster in Process Engineering, INPL, Nancy, FRANCE
Chemical and Process Engineer, ENSIC, Nancy, FRANCE
Liquid Maldistribution in TBRsLiquid Maldistribution in TBRs
• An Experimental Study• How to quantify maldistribution?• Determination of the parameters
responsible for maldistribution
• A step to CFD modeling• Generate a pseudo random
porosity profile
x (mm)
y(m
m)
-60 -40 -20 0 20 40 60
-60
-40
-20
0
20
40
60 31.0
28.0
25.1
22.1
19.2
16.2
13.3
10.3
7.4
4.4
1.5
Exit liquid distribution
UL = 8 mm.s-1 & UG = 0.1 m.s-11 Flux in kg.m-2.s-1
r
0.950.910.880.840.800.760.720.680.650.610.570.530.490.460.420.380.340.300.260.230.190.150.110.070.04
Pseudo RandomPorosity Profile
R(column center)
0(wall)
Z
0(bottom)
L(top)
?
Multiphase Packed-bed Reactor Modeling
Jing GuoCREL Annual Meeting, 2002 Dr. M. H. Al-Dahhan
MotivationScale up of packed bed:
Simulation vs huge amount of experimental work
? How to choose multiple level model for reaction system of interest
Understand and compare the hierarchy of model for catalytic multiphase packed-bed reactorsCapture the time-dependent reaction features of catalytic wet oxidation in packed beds
Objective
outputinput
C0, usL
Xa, C, usL,
Reactor scale
Completely actively wetted
Completely inactively wetted
Half wetted
Pellet scale
CHEMICAL REACTION ENGINEERING LABORATORY
Combination of Reactor and Pellet Scale Model
C i, N
C i, N-1
C i, j
C i, 2
C i, 1
C i, 0
Rea
c tor
Sca
le
El-Hisnawi Model
Ci,jDry side Wet sidePellet scale
Beaudry Model
El-Hisnawi Model
Beaudry Model
Predict axial concentration
distribution
Refine local effectiveness factor
Predict catalyst local performance
CHEMICAL REACTION ENGINEERING LABORATORY
I:reactant componentJ:Cell sequence
Rea
ctor
Axi
s
Pellet scale
Ul, Ug
Reactionwet oxidation of phenol
over deactivating catalyst
Active site distribution after 110 hours
New CT Setup and studies on Gas-Liquid Hold-up in Structured Packing
using CT
Shaibal RoyMuthanna Al-Dahhan
Main difference between the old and new CT
Resolution Characteristics of new CT setup
Gas Liquid Flow Characteristics (hold-up and pressure drop) in a 12 inch
Structured packing
Poster 1
4”
4"
Guide for the source
Plate 1
Plate 2
A Study of Structured Packing for Solid Catalyzed Gas-Liquid Reaction
Shaibal RoyMuthanna Al-Dahhan
Structured Packing for solid catalyzed gas-liquid reaction provides
Large Volumetric productivity Lower pressure drop Excellent mass transfer properties Higher selectivity (low axial dispersion, short
diffusion length scale) Ease of scale-up
Motivation
Poster 2
Research Objective
The overall objective of the proposed study is to develop better
understanding
and fundamentally based model for comparison of structured packing (e.g.
Monolith and other selected configuration) with conventional reactors for
multiphase reactionsResearch Goal
Apparent Kinetic model with extrudates
And washcoated monolith
Hydrodynamic aspects in structured packing
Combined effects in overall performance of structured packing for multiphase reactions
Compare with conventional packed bed
reactor
Develop model for performance prediction
CHEMICAL REACTION ENGINEERING LABORATORY
A Non-Invasive Method for Overall Solids Flux Measurements A Non-Invasive Method for Overall Solids Flux Measurements in a Circulating Fluidized Bed (CFB)in a Circulating Fluidized Bed (CFB)
Satish Bhusarapu, Pascal Fongarland,
M. H. Al-Dahhan and M. P. Dudukovic’
CREL Annual MeetingCREL Annual MeetingOctober 24, 2002October 24, 2002
Chemical Reaction Engineering Laboratory
Department of Chemical Engineering
St.Louis, MO 63130
CHEMICAL REACTION ENGINEERING LABORATORY
6” Column
Disengagementaxisymmetric
section
Deflector plate
Filterunit
Downcomer
18’ Length
2” Diameter26’ Riser
Challenge : How to measure overall solids mass flux Challenge : How to measure overall solids mass flux accurately in a CFB ?accurately in a CFB ?
Obtain solids velocity and concentration in a standpipe where solids hold up is high
• Solids velocity – “time of flight” measurements – track a single radioactive tracer using a two detector set-up
• Solids concentration – -ray line densitometry
Overall solids flux at varying operating conditions
Photobioreactors for Culturing High Value Microalgae and Cyanobacteria: Experimentation and Modeling
CHEMICAL REACTION ENGINEERING LABORATORY
Hu-Ping Luo, Muthanna Al-DahhanChemical Reaction Engineering Laboratory (CREL)
Washington University
CREL ANNUAL MEETING October 24, 2002
CHEMICAL REACTION ENGINEERING LABORATORY
Cells’ growth depends on their movement
radius, r, (cm)x, cm
y, c
m
Wall or internals
Split Column
Spiral movements, time scale: 1 s
In Nonlinear and Dynamic Systems, results are determined by the process
A cell’s movement in the reactor determines its accessibility to the light, nutrients, the shear stress
need to endure, etc.
Feeding to the cells is irregular in bioreactors, especially for light
Light distribution
CHEMICAL REACTION ENGINEERING LABORATORY
Dynamic approach for photobioreactor analysis
Challenge: How to combine the knowledge of: Physiology of photosynthesis processReactor hydrodynamic
Current approaches: use Static kinetic model for bio-reactions, take into account only average light intensity (effects of hydrodynamic are ignored)
Our new approach: combines dynamic kinetic model for bio-reactions with hydrodynamic information via CARPT experimental technique.
Please stop at my poster, I’ll show you all the details 0
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0 50 100 150 200 250 300
Time, hr
Cel
l co
nce
ntr
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*10
6 c
ell/m
l)
EXP
Simulation of Wu
Ug=5 cm/s (this work)
Ug=1 cm/s (this work)
FLOW PATTERN IMAGINGINSIDE A SIMULATED ANAEROBIC DIGESTER
USING CARPT AND CT
Washington University Group: Rebecca Hofmann, Mehul Vesvikar, Rajneesh Varma, Khursheed Karim, Muthanna Al-Dahhan
Oak Ridge National Lab. Group: Thomas Klasson, Alan Wintenberg, Chuck Alexander, David Depaoli
CHEMICAL REACTION ENGINEERING LABORATORY
ANIMAL WASTE :Environmental Perspective ANIMAL WASTE :Environmental Perspective and motivation for Treatmentand motivation for Treatment
More than one billion tons of animal waste generated every year in the USA.
Unsafe and improperly disposed
– Surface & groundwater contamination – Ammonia leaching– Methane emission– Odors
Methane = Energy source, hence animal waste = renewable energy source
Biomass has applications of fertilizer and land fill
High failure rate observed in digesters that is attributed to mixing related problems
Effects of hydrodynamics and mixing in anaerobic bioreactors needs investigation.
Objective of The Present Work
To demonstrate the ability of single particle CARPT technique to visualize 3D flow patterns inside a simulated digester.
To determine the gas phase hold-up of the three phase anaerobic system using single source CT.
CHEMICAL REACTION ENGINEERING LABORATORY
Modeling of Catalytic Partial Oxidation Reactors
R.C. Ramaswamy, P.A. Ramachandran& M.P. Dudukovic
CREL Annual MeetingOctober 24, 2002
CHEMICAL REACTION ENGINEERING LABORATORY
Catalytic Partial Oxidation of Methane to Syn-gas
CH4 & O2
(2:1)
Tin ~773 K
H2/CO < 2;
CO2 & H2O
Texit ~ 1300 K
Exo. rxn. &Endo. rxn.
A schematic of syn-gas packed bed reactor
Synthesis Gas (mixture of CO and H2)• Feed stock to chemical process industries• Feed stock to Syn-fuels, H2 for fuel cells
CHEMICAL REACTION ENGINEERING LABORATORY
Reactions :1) Exothermic Combustion Reaction2) Endothermic Steam Reforming Reaction3) Slightly Exothermic Water Gas Shift Reaction
Mathematical models are required for design, control and optimization purposes
Transport and Capture of Particles in Magnetic FieldsPrakash Kumar
Advisors: Prof. Pratim Biswas, Prof. M. P. Dudukovic
2. Setup to study the particle transport Magnetic fields.
1. Model to predict the particle trajectories in magnetic fields.
10-7
10-6
10-5
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10-8
10-6
10-4
10-2
100
diameterj (m)co
llisi
on fr
eque
ncy(
cm3 /s
ec)
capture efficiency based on total no concentration vs gap(based on 4 runs)
Gap between magnet and the tube, Zgap(mm)0 5 10 15 20 25
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rall
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efiic
ienc
y
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ExperimentalModel
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22395.0
ji
jimangetic dd
ddM
Brownian (Friedlander 1964)
(Magnetic)
3. Comparison of theoretical and experimetal results.
4. Effect of magnetic fields on particle aggregation.