SlideShare a Scribd company logo
drying
Industrial
distillation
Evaporation
Absorption
In the absence of other
gradients such as
-Temperature
-Electrical
-Gravitational potentials
Molecules of a given species
( e.g. A) within a single phase
will always diffuse from region
oh high to low concentrations.
This will result in a Molar Flux of
species A (NA) in the direction of
decreasing concentration.
Flux is the flow rate FA per unit
area normal to the direction
of flow
(NA) is a Vector quantity ( )
moles
2 .s
m
moles
2 .s
m
A
NA
FA
=
NH3
1 2
NH3
Steady state fluxes
Determine NA for ammonia and mass flux for
ammonia nA through stationary frame at steady
state? There are 12.4x10 molecules of NH3 that
pass through an area A (2m ) over time interval 10 s
23
2
High
Concentration
Low
Concentration
Number of NH3 molecules
Avogadro's No.
No. of Moles =
12.04 x 10
23
6.02 x 1023
No. of Moles = =2 Mol
Two moles pass through an area of 2m in 10 s. therefore
the No. of moles passing through 1 m per second ( Molar
flux NA)
2
2
2 mol
(2 m ) ( 10
s)
NA= = 0.1 mol/m .s
2
2
The mass Flux = nA = NA x MWA
nA = 0.1 mol/m .s x 17g/mol
nA = 1.7 g/m .s
2
2
The Molar Flux NA is the result of two
contributions:
1)The molecular diffusion flux
produced by a concentration
gradient JA
2) Flux resulting from the bulk motion of
the fluid BA
NA JA BA
+
=
What is the difference between
the two contributions?
Gas mixture A &B
Well mixed
(no concentration
gradient)
A
B
A
B
B
B
A
B
A
A
A
B
A
B
B
B
A
B
A
A
A
B
A
B
B
B
A
B
A
A
UA
Velocity UA
The flux of A
resulting from Bulk
motion
BA = XA (NA+ NB)
BA = XA (NT)
The flux of A is
only
JA = 0
BA
Well mixed
(no concentration
gradient)
The Bulk flow term can be expressed in
terms of concnteration CA and average
molar velocity U
M
U
M
CA
=
BA
U
M
=xi Ui
Xi = Ci
C
Particles velocity
Mole fraction
B
A
A
A
B
A
B
B
B
A
A
A A
A
A
UA
A
A
A
A
A
B B
B
B
B
JA
Let see if the mixture is not spatially uniform
( Concentration gradient exist) and moving with
molar average velocity U
M
In this case there will
be both diffusion flux
of A,(JA) relative to the
motion of the mixture
+ Bulk flow of A (BA)
Thus total molar Flux of
A is given by
NA JA BA
+
=
can be expressed either in
terms of concentration of A
BA
NA JA CA U
+
=
M
XA (NA+ NB)
NA JA+
=
M
Or in terms of mole fraction
Remember :
The Flux of A Relative to Fixed Frame ( e.g. Your
Desk) Is the product of concentration of A (CA) and
the particle velocity ( UA)
NA = CA X UA 1
The Flux JA is the flux of A Relative to the molar average
velocity U
The molar average velocity for a binary system is
M
U
M
=xi Ui U
M
= xAUA + xB
UB
(UA –U)
M
What this difference tells us?
It tells us the velocity at which
species A is moving relative to
average velocity of all the species
Flux MJA Relative to U
M
MJA = CA ( UA –U )
M
MJA = CAUA – CA U
M

NA
CA ( )
xAUA + xB UB

Factoring the reciprocal of the total concentration (1/C )
from the terms in parentheses m we have
C
(CA UA + CA UB )
CA
CA U
M
= xA
= NA + NB
( )
MJA = CAUA – CA U
M
NA
CA ( )
xAUA + xB UB


xA (NA + NB)
NA= MJA + xA ( NA + NB )
From all these equations we
get
NA=-C DAB  xA + xA ( NA + NB )
Evaluating the Molar Flux
1- Equimolar Counter Current
Diffusion
EMCD A
B
A B
A B
Fluxes of A & B are Equal
in magnitute and flow
counter to each other
Mathematically
NA = - NB A diffuse from
the Bulk to
Catalyst Surface
where it
isomerizes to
form B
A diffuse from
the Bulk to
Catalyst Surface
where it
isomerizes to
form B
NA=-C DAB  xA + xA ( NA + NB )
Mathematically
NA = - NB
substitute into general equation
NA=-C DAB  xA + xA ( NA + {-NA} )
0
NA=-C DAB  xA =MJA
EMCD Equation
For constant total concentration
NA=-DAB  CA =MJA
Evaluating the Molar Flux
1-Dilute Concentrations
Such case occur when : The mole
fraction of the diffusing Solute & the
Bulk motion in the direction of diffusion
are small.
The Flux is similar to constant total
concentration
NA=-DAB  CA =MJA
NA=-C DAB  xA + xA ( NA + {-NA} )
0
The Equation above can also be reduced to that
similar to Constant total concentration and
dilute concentration
For porous catalyst systems when the pore
radii are very small. Diffusion under these
condition is known as Knudsen diffusion (Dk)
and occur when the mean free path
 >> diamter of the catalyst . Here the reacting
molecules collide more often with pore wall
than with other. In this case we neglect the
Bulk terms and the flux of species A for
Knudsen diffusion is expressed as follows:
NA=-Dk CA =MJA
This type is found in systems where
two phases are present.
Evaporation and gas absorption are
typical process
Evaluating the Molar Flux
Diffusion through a Stagnant Gas
If there is a stagnant gas, there will be
no net flux of B w.r.t. a fixed coordinate
i.e.
NB = 0
NA=-C DAB  xA + xA ( NA + NB )
NB = 0
Substituting
We get
NA=-C DAB  xA + xA NA
Rearranging
yields
NA= C DAB  xA
1 - xA
-1
NA= C DAB  xA
1 - xA
-1
NA=-C DAB  xA + xA NA
Take this term to LHS
NA- xA NA = -C DAB  xA
NA (1- xA) = -C DAB  xA
This will lead us to this equation
NA= C DAB ln ( ) = C DAB ln
1 - xA xB
JAz
JAx
Z
x
Evaluating the Molar Flux
Axial Diffusion effect is nglected
and flux result from forced
convection
When the flux of A results from forced convection. We
assume that the diffusion in the direction of flow (
which in this case z direction), Jaz , which is very
small in comparison with the Bulk flow.
Evaluating the Molar Flux
Axial Diffusion effect is nglected
and flux result from forced
convection
When the flux of A results from forced convection. We
assume that the diffusion in the direction of flow (
which in this case z direction), Jaz , which is very
small in comparison with the Bulk flow.
One contribution in the z direction ,
BAz (Uz  /Ac {m /m .s}) where  volumetric flow
rate in the direction of flow and Ac is the cross
sectional area. JAz is neglected, while JAx normal
to the direction of the flow, may not be nglected.
NA = Baz = CA Uz  CA /Ac
We can express the molar flow rate FA =  CA when not
accounting for diffusional effects, However when accounting
for diffusional effects The molar flow rate FAz is = NA Ac
3 2
FA = NAz Ac = - CDAB + xA (Nz) Ac
dxA
dz


Where Nz is the total molar average flux in z
direction of all n species , i.e
Nz =  Niz
i=1
m
Mass Flux
Molar Flux
Reference system
nA = A UA
NA = CA UA
Fixed Coordinates
jA = A(UA- U )
JA = CA (UA- U )
Molar average Velocity
jA = A (UA- U )
JA = CA (UA- U )
Mass average Velocity
jA = A (UA- U )
vJA = CA (UA- U )
Volume average Velocity
Fluxes for Binary Systems
M
M
M
M
m
m m
m
v v
v
Relationships between Fluxes
Relationship between
mass and molar fluxes
nA = NA MA MjA = mjA
M
MA
MjA = MJA
MA
mJA = MJA
MB
M
Relationships between Fluxes
Molar flux Relative to U
M
NA +NB = C U
M
MJA + MJB = 0
NA = MJA + xA ( NA +NB
NA = MJA + CA U
M
Relationships between Fluxes
Mass flux Relative to U
m
nA +nB =  U
m
mjA + mjB = 0
nA = mjA + A ( nA +nB)
nA = mjA +  A U
m
Changing from one reference to
another Hooyman et al (1953) derived
a general diffusion coefficient
expressed as
JA =-DAB xA
1-A
1-xA
1
V
Molar
volume of
the mixture
Weighing
factor relating
to the
appropriate
velocity
A
Reference velocity
Fick`s Law

A
mJA
xA
MJA
CA VA
vJA
U
m
U
M
U
v
Weighing factors Values
Formulation of Mass Transfer Models
Macroscopic models
Describe industrial Process
but do not provide a detailed
description of the process.
Because the properties of the
system are averaged over
position.
The only independent
variable is time , so its easy
to solve the derived
differential equation of
macroscopic models
Macroscopic material balance
Inlet (i)
Applying the law of conservation of matter to a
stream flowing into a volume element fixed in
space
Outlet (i)
Volume
element
General Material Balance in the
RATE FORM
Rate of
Accumulation
Rate of
Transport
into
Rate of
Transport
Out
Rate of
generation
Rate of
Transport
Out
General Material Balance for total flow of mass
V V U S U S
( )
Mass of
material
within the
system
Average
velocity of
the fluid
Dividing both sides by and shrinking the
time to zero we get
dt
d
(  V ) ( U S) ( U S) ( U S)
Note:
1- Since total mass can not be neither created
nor destroyed both the generation and
consumption terms are not present. (no
chemical reaction).
2- the mixing within the volume element is
perfectly mixed concentration leaving or
entering the volume is the same.
3- The subscript on the exit term (Outlet) will
be dropped from the equation because the
exiting stream is a variable.
4- The S in and out are the same.
THE MASS BALANCE BECOMS
dt
d
S
1
(  V ) ( U) ( U) Absence of
Coordinates
General Microscopic Material
Balance
Derivation of continuity equation
Eulerian approach
In this approach the mass of component
A moves at a velocity, UA through a
fixed volume element
And Can be extended to cases where the
volume element moves with some
reference velocity ( UM, Um, U )
M m v
Start:
considering a differential element of fixed shape
 Flow entering and leaving the element at all direction.
 Substitute mass flux terms for species A into the
general balance equation
Rate of
Accumulation
Rate of
Transport
into
Rate of
Transport
Out
Rate of
generation
Rate of
Transport
Out
(nAx - nAx ) Y Z
x X +x
(nA - nAx ) X Z
Y Y +Y
(nA - nAx ) X Y
Y Y +Y
rA X Y Z
*
X Y Z A


t


More Related Content

Similar to ملخص من عبدالله الترهونى.pptx

slidesWaveRegular.pdf
slidesWaveRegular.pdfslidesWaveRegular.pdf
slidesWaveRegular.pdf
cfisicaster
 
Presentation1.ppt
Presentation1.pptPresentation1.ppt
Presentation1.ppt
DoulatNangare1
 
WavesAppendix.pdf
WavesAppendix.pdfWavesAppendix.pdf
WavesAppendix.pdf
cfisicaster
 
Ec8451 - Electro Magnetic Fields
Ec8451 - Electro Magnetic FieldsEc8451 - Electro Magnetic Fields
Ec8451 - Electro Magnetic Fields
Benesh Selvanesan
 
10.1.1.31.6238ghhj.pdf
10.1.1.31.6238ghhj.pdf10.1.1.31.6238ghhj.pdf
10.1.1.31.6238ghhj.pdf
JahanTejarat
 
International Journal of Computational Engineering Research(IJCER)
International Journal of Computational Engineering Research(IJCER)International Journal of Computational Engineering Research(IJCER)
International Journal of Computational Engineering Research(IJCER)
ijceronline
 
Fluid Dynamics
Fluid DynamicsFluid Dynamics
Fluid Dynamics
Om Kumar
 
Chapter 4.pptx
Chapter 4.pptxChapter 4.pptx
Chapter 4.pptx
jazzcashlimit
 
Convective mass transfer
Convective mass transferConvective mass transfer
Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...
Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...
Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...
JISHAPACHAT
 
Fluid mechanics - Motion of Fluid Particles and Stream
Fluid mechanics - Motion of Fluid Particles and StreamFluid mechanics - Motion of Fluid Particles and Stream
Fluid mechanics - Motion of Fluid Particles and Stream
Viraj Patel
 
mass transfer for metallurgy, chemical, mechanical department
mass transfer for metallurgy, chemical, mechanical departmentmass transfer for metallurgy, chemical, mechanical department
mass transfer for metallurgy, chemical, mechanical department
vasundharasingh70
 
Mass transfer & diffusion hari
Mass transfer & diffusion hariMass transfer & diffusion hari
Mass transfer & diffusion hari
harirammishra
 
Application of vector integration
Application of vector integration Application of vector integration
Application of vector integration
Varuna Kapuge
 
Molecular diffusion
Molecular diffusionMolecular diffusion
5. lec5 curl of a vector
5. lec5 curl of a vector5. lec5 curl of a vector
5. lec5 curl of a vector
shabdrang
 
Reflection and Transmission of Mechanical Waves
Reflection and Transmission of Mechanical WavesReflection and Transmission of Mechanical Waves
Reflection and Transmission of Mechanical Waves
Millathina Puji Utami
 
DC AC.pptx
DC AC.pptxDC AC.pptx
DC AC.pptx
KubaOrszulak
 
Aerodynamics part ii
Aerodynamics   part iiAerodynamics   part ii
Aerodynamics part ii
Solo Hermelin
 
The Effect of Bottom Sediment Transport on Wave Set-Up
The Effect of Bottom Sediment Transport on Wave Set-UpThe Effect of Bottom Sediment Transport on Wave Set-Up
The Effect of Bottom Sediment Transport on Wave Set-Up
ijceronline
 

Similar to ملخص من عبدالله الترهونى.pptx (20)

slidesWaveRegular.pdf
slidesWaveRegular.pdfslidesWaveRegular.pdf
slidesWaveRegular.pdf
 
Presentation1.ppt
Presentation1.pptPresentation1.ppt
Presentation1.ppt
 
WavesAppendix.pdf
WavesAppendix.pdfWavesAppendix.pdf
WavesAppendix.pdf
 
Ec8451 - Electro Magnetic Fields
Ec8451 - Electro Magnetic FieldsEc8451 - Electro Magnetic Fields
Ec8451 - Electro Magnetic Fields
 
10.1.1.31.6238ghhj.pdf
10.1.1.31.6238ghhj.pdf10.1.1.31.6238ghhj.pdf
10.1.1.31.6238ghhj.pdf
 
International Journal of Computational Engineering Research(IJCER)
International Journal of Computational Engineering Research(IJCER)International Journal of Computational Engineering Research(IJCER)
International Journal of Computational Engineering Research(IJCER)
 
Fluid Dynamics
Fluid DynamicsFluid Dynamics
Fluid Dynamics
 
Chapter 4.pptx
Chapter 4.pptxChapter 4.pptx
Chapter 4.pptx
 
Convective mass transfer
Convective mass transferConvective mass transfer
Convective mass transfer
 
Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...
Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...
Bonding-Notes spectroscopy A detailed discriptions on vibrational spectra of ...
 
Fluid mechanics - Motion of Fluid Particles and Stream
Fluid mechanics - Motion of Fluid Particles and StreamFluid mechanics - Motion of Fluid Particles and Stream
Fluid mechanics - Motion of Fluid Particles and Stream
 
mass transfer for metallurgy, chemical, mechanical department
mass transfer for metallurgy, chemical, mechanical departmentmass transfer for metallurgy, chemical, mechanical department
mass transfer for metallurgy, chemical, mechanical department
 
Mass transfer & diffusion hari
Mass transfer & diffusion hariMass transfer & diffusion hari
Mass transfer & diffusion hari
 
Application of vector integration
Application of vector integration Application of vector integration
Application of vector integration
 
Molecular diffusion
Molecular diffusionMolecular diffusion
Molecular diffusion
 
5. lec5 curl of a vector
5. lec5 curl of a vector5. lec5 curl of a vector
5. lec5 curl of a vector
 
Reflection and Transmission of Mechanical Waves
Reflection and Transmission of Mechanical WavesReflection and Transmission of Mechanical Waves
Reflection and Transmission of Mechanical Waves
 
DC AC.pptx
DC AC.pptxDC AC.pptx
DC AC.pptx
 
Aerodynamics part ii
Aerodynamics   part iiAerodynamics   part ii
Aerodynamics part ii
 
The Effect of Bottom Sediment Transport on Wave Set-Up
The Effect of Bottom Sediment Transport on Wave Set-UpThe Effect of Bottom Sediment Transport on Wave Set-Up
The Effect of Bottom Sediment Transport on Wave Set-Up
 

Recently uploaded

Global Climate Change and global warming
Global Climate Change and global warmingGlobal Climate Change and global warming
Global Climate Change and global warming
ballkicker20
 
在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样
在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样
在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样
pjq9n1lk
 
Global Peatlands Map and Hotspot Explanation Atlas
Global Peatlands Map and Hotspot Explanation AtlasGlobal Peatlands Map and Hotspot Explanation Atlas
Global Peatlands Map and Hotspot Explanation Atlas
Global Landscapes Forum (GLF)
 
Overview of the Global Peatlands Assessment
Overview of the Global Peatlands AssessmentOverview of the Global Peatlands Assessment
Overview of the Global Peatlands Assessment
Global Landscapes Forum (GLF)
 
world-environment-day-2024-240601103559-14f4c0b4.pptx
world-environment-day-2024-240601103559-14f4c0b4.pptxworld-environment-day-2024-240601103559-14f4c0b4.pptx
world-environment-day-2024-240601103559-14f4c0b4.pptx
mfasna35
 
Wildlife-AnIntroduction.pdf so that you know more about our environment
Wildlife-AnIntroduction.pdf so that you know more about our environmentWildlife-AnIntroduction.pdf so that you know more about our environment
Wildlife-AnIntroduction.pdf so that you know more about our environment
amishajha2407
 
原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样
原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样
原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样
p2npnqp
 
Enhanced action and stakeholder engagement for sustainable peatland management
Enhanced action and stakeholder engagement for sustainable peatland managementEnhanced action and stakeholder engagement for sustainable peatland management
Enhanced action and stakeholder engagement for sustainable peatland management
Global Landscapes Forum (GLF)
 
Promoting Multilateral Cooperation for Sustainable Peatland management
Promoting Multilateral Cooperation for Sustainable Peatland managementPromoting Multilateral Cooperation for Sustainable Peatland management
Promoting Multilateral Cooperation for Sustainable Peatland management
Global Landscapes Forum (GLF)
 
How about Huawei mobile phone-www.cfye-commerce.shop
How about Huawei mobile phone-www.cfye-commerce.shopHow about Huawei mobile phone-www.cfye-commerce.shop
How about Huawei mobile phone-www.cfye-commerce.shop
laozhuseo02
 
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...Kinetic studies on malachite green dye adsorption from aqueous solutions by A...
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...
Open Access Research Paper
 
ENVIRONMENT~ Renewable Energy Sources and their future prospects.
ENVIRONMENT~ Renewable Energy Sources and their future prospects.ENVIRONMENT~ Renewable Energy Sources and their future prospects.
ENVIRONMENT~ Renewable Energy Sources and their future prospects.
tiwarimanvi3129
 
Peatlands of Latin America and the Caribbean
Peatlands of Latin America and the CaribbeanPeatlands of Latin America and the Caribbean
Peatlands of Latin America and the Caribbean
Global Landscapes Forum (GLF)
 
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...
Joshua Orris
 
Improving the viability of probiotics by encapsulation methods for developmen...
Improving the viability of probiotics by encapsulation methods for developmen...Improving the viability of probiotics by encapsulation methods for developmen...
Improving the viability of probiotics by encapsulation methods for developmen...
Open Access Research Paper
 
Peatland Management in Indonesia, Science to Policy and Knowledge Education
Peatland Management in Indonesia, Science to Policy and Knowledge EducationPeatland Management in Indonesia, Science to Policy and Knowledge Education
Peatland Management in Indonesia, Science to Policy and Knowledge Education
Global Landscapes Forum (GLF)
 
Improving the Management of Peatlands and the Capacities of Stakeholders in I...
Improving the Management of Peatlands and the Capacities of Stakeholders in I...Improving the Management of Peatlands and the Capacities of Stakeholders in I...
Improving the Management of Peatlands and the Capacities of Stakeholders in I...
Global Landscapes Forum (GLF)
 
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...
Joshua Orris
 
一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理
一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理
一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理
zm9ajxup
 
Climate Change All over the World .pptx
Climate Change All over the World  .pptxClimate Change All over the World  .pptx
Climate Change All over the World .pptx
sairaanwer024
 

Recently uploaded (20)

Global Climate Change and global warming
Global Climate Change and global warmingGlobal Climate Change and global warming
Global Climate Change and global warming
 
在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样
在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样
在线办理(lboro毕业证书)拉夫堡大学毕业证学历证书一模一样
 
Global Peatlands Map and Hotspot Explanation Atlas
Global Peatlands Map and Hotspot Explanation AtlasGlobal Peatlands Map and Hotspot Explanation Atlas
Global Peatlands Map and Hotspot Explanation Atlas
 
Overview of the Global Peatlands Assessment
Overview of the Global Peatlands AssessmentOverview of the Global Peatlands Assessment
Overview of the Global Peatlands Assessment
 
world-environment-day-2024-240601103559-14f4c0b4.pptx
world-environment-day-2024-240601103559-14f4c0b4.pptxworld-environment-day-2024-240601103559-14f4c0b4.pptx
world-environment-day-2024-240601103559-14f4c0b4.pptx
 
Wildlife-AnIntroduction.pdf so that you know more about our environment
Wildlife-AnIntroduction.pdf so that you know more about our environmentWildlife-AnIntroduction.pdf so that you know more about our environment
Wildlife-AnIntroduction.pdf so that you know more about our environment
 
原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样
原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样
原版制作(Newcastle毕业证书)纽卡斯尔大学毕业证在读证明一模一样
 
Enhanced action and stakeholder engagement for sustainable peatland management
Enhanced action and stakeholder engagement for sustainable peatland managementEnhanced action and stakeholder engagement for sustainable peatland management
Enhanced action and stakeholder engagement for sustainable peatland management
 
Promoting Multilateral Cooperation for Sustainable Peatland management
Promoting Multilateral Cooperation for Sustainable Peatland managementPromoting Multilateral Cooperation for Sustainable Peatland management
Promoting Multilateral Cooperation for Sustainable Peatland management
 
How about Huawei mobile phone-www.cfye-commerce.shop
How about Huawei mobile phone-www.cfye-commerce.shopHow about Huawei mobile phone-www.cfye-commerce.shop
How about Huawei mobile phone-www.cfye-commerce.shop
 
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...Kinetic studies on malachite green dye adsorption from aqueous solutions by A...
Kinetic studies on malachite green dye adsorption from aqueous solutions by A...
 
ENVIRONMENT~ Renewable Energy Sources and their future prospects.
ENVIRONMENT~ Renewable Energy Sources and their future prospects.ENVIRONMENT~ Renewable Energy Sources and their future prospects.
ENVIRONMENT~ Renewable Energy Sources and their future prospects.
 
Peatlands of Latin America and the Caribbean
Peatlands of Latin America and the CaribbeanPeatlands of Latin America and the Caribbean
Peatlands of Latin America and the Caribbean
 
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...
Optimizing Post Remediation Groundwater Performance with Enhanced Microbiolog...
 
Improving the viability of probiotics by encapsulation methods for developmen...
Improving the viability of probiotics by encapsulation methods for developmen...Improving the viability of probiotics by encapsulation methods for developmen...
Improving the viability of probiotics by encapsulation methods for developmen...
 
Peatland Management in Indonesia, Science to Policy and Knowledge Education
Peatland Management in Indonesia, Science to Policy and Knowledge EducationPeatland Management in Indonesia, Science to Policy and Knowledge Education
Peatland Management in Indonesia, Science to Policy and Knowledge Education
 
Improving the Management of Peatlands and the Capacities of Stakeholders in I...
Improving the Management of Peatlands and the Capacities of Stakeholders in I...Improving the Management of Peatlands and the Capacities of Stakeholders in I...
Improving the Management of Peatlands and the Capacities of Stakeholders in I...
 
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...
Evolving Lifecycles with High Resolution Site Characterization (HRSC) and 3-D...
 
一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理
一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理
一比一原版(UMTC毕业证书)明尼苏达大学双城分校毕业证如何办理
 
Climate Change All over the World .pptx
Climate Change All over the World  .pptxClimate Change All over the World  .pptx
Climate Change All over the World .pptx
 

ملخص من عبدالله الترهونى.pptx

  • 1.
  • 2.
  • 4.
  • 5. In the absence of other gradients such as -Temperature -Electrical -Gravitational potentials Molecules of a given species ( e.g. A) within a single phase will always diffuse from region oh high to low concentrations.
  • 6. This will result in a Molar Flux of species A (NA) in the direction of decreasing concentration. Flux is the flow rate FA per unit area normal to the direction of flow (NA) is a Vector quantity ( ) moles 2 .s m moles 2 .s m A NA FA =
  • 7. NH3 1 2 NH3 Steady state fluxes Determine NA for ammonia and mass flux for ammonia nA through stationary frame at steady state? There are 12.4x10 molecules of NH3 that pass through an area A (2m ) over time interval 10 s 23 2 High Concentration Low Concentration
  • 8. Number of NH3 molecules Avogadro's No. No. of Moles = 12.04 x 10 23 6.02 x 1023 No. of Moles = =2 Mol Two moles pass through an area of 2m in 10 s. therefore the No. of moles passing through 1 m per second ( Molar flux NA) 2 2 2 mol (2 m ) ( 10 s) NA= = 0.1 mol/m .s 2 2 The mass Flux = nA = NA x MWA nA = 0.1 mol/m .s x 17g/mol nA = 1.7 g/m .s 2 2
  • 9. The Molar Flux NA is the result of two contributions: 1)The molecular diffusion flux produced by a concentration gradient JA 2) Flux resulting from the bulk motion of the fluid BA NA JA BA + =
  • 10. What is the difference between the two contributions? Gas mixture A &B Well mixed (no concentration gradient) A B A B B B A B A A A B A B B B A B A A A B A B B B A B A A UA Velocity UA The flux of A resulting from Bulk motion BA = XA (NA+ NB) BA = XA (NT) The flux of A is only JA = 0 BA Well mixed (no concentration gradient)
  • 11. The Bulk flow term can be expressed in terms of concnteration CA and average molar velocity U M U M CA = BA U M =xi Ui Xi = Ci C Particles velocity Mole fraction
  • 12. B A A A B A B B B A A A A A A UA A A A A A B B B B B JA Let see if the mixture is not spatially uniform ( Concentration gradient exist) and moving with molar average velocity U M In this case there will be both diffusion flux of A,(JA) relative to the motion of the mixture + Bulk flow of A (BA) Thus total molar Flux of A is given by NA JA BA + = can be expressed either in terms of concentration of A BA NA JA CA U + = M XA (NA+ NB) NA JA+ = M Or in terms of mole fraction
  • 13. Remember : The Flux of A Relative to Fixed Frame ( e.g. Your Desk) Is the product of concentration of A (CA) and the particle velocity ( UA) NA = CA X UA 1 The Flux JA is the flux of A Relative to the molar average velocity U The molar average velocity for a binary system is M U M =xi Ui U M = xAUA + xB UB
  • 14. (UA –U) M What this difference tells us? It tells us the velocity at which species A is moving relative to average velocity of all the species
  • 15. Flux MJA Relative to U M MJA = CA ( UA –U ) M MJA = CAUA – CA U M  NA CA ( ) xAUA + xB UB  Factoring the reciprocal of the total concentration (1/C ) from the terms in parentheses m we have C (CA UA + CA UB ) CA CA U M = xA = NA + NB ( )
  • 16. MJA = CAUA – CA U M NA CA ( ) xAUA + xB UB   xA (NA + NB) NA= MJA + xA ( NA + NB ) From all these equations we get NA=-C DAB  xA + xA ( NA + NB )
  • 17. Evaluating the Molar Flux 1- Equimolar Counter Current Diffusion EMCD A B A B A B Fluxes of A & B are Equal in magnitute and flow counter to each other Mathematically NA = - NB A diffuse from the Bulk to Catalyst Surface where it isomerizes to form B A diffuse from the Bulk to Catalyst Surface where it isomerizes to form B
  • 18. NA=-C DAB  xA + xA ( NA + NB ) Mathematically NA = - NB substitute into general equation NA=-C DAB  xA + xA ( NA + {-NA} ) 0 NA=-C DAB  xA =MJA EMCD Equation For constant total concentration NA=-DAB  CA =MJA
  • 19. Evaluating the Molar Flux 1-Dilute Concentrations Such case occur when : The mole fraction of the diffusing Solute & the Bulk motion in the direction of diffusion are small. The Flux is similar to constant total concentration NA=-DAB  CA =MJA
  • 20. NA=-C DAB  xA + xA ( NA + {-NA} ) 0 The Equation above can also be reduced to that similar to Constant total concentration and dilute concentration For porous catalyst systems when the pore radii are very small. Diffusion under these condition is known as Knudsen diffusion (Dk) and occur when the mean free path  >> diamter of the catalyst . Here the reacting molecules collide more often with pore wall than with other. In this case we neglect the Bulk terms and the flux of species A for Knudsen diffusion is expressed as follows: NA=-Dk CA =MJA
  • 21. This type is found in systems where two phases are present. Evaporation and gas absorption are typical process Evaluating the Molar Flux Diffusion through a Stagnant Gas If there is a stagnant gas, there will be no net flux of B w.r.t. a fixed coordinate i.e. NB = 0
  • 22. NA=-C DAB  xA + xA ( NA + NB ) NB = 0 Substituting We get NA=-C DAB  xA + xA NA Rearranging yields NA= C DAB  xA 1 - xA -1
  • 23. NA= C DAB  xA 1 - xA -1 NA=-C DAB  xA + xA NA Take this term to LHS NA- xA NA = -C DAB  xA NA (1- xA) = -C DAB  xA This will lead us to this equation NA= C DAB ln ( ) = C DAB ln 1 - xA xB
  • 24. JAz JAx Z x Evaluating the Molar Flux Axial Diffusion effect is nglected and flux result from forced convection When the flux of A results from forced convection. We assume that the diffusion in the direction of flow ( which in this case z direction), Jaz , which is very small in comparison with the Bulk flow.
  • 25. Evaluating the Molar Flux Axial Diffusion effect is nglected and flux result from forced convection When the flux of A results from forced convection. We assume that the diffusion in the direction of flow ( which in this case z direction), Jaz , which is very small in comparison with the Bulk flow. One contribution in the z direction , BAz (Uz  /Ac {m /m .s}) where  volumetric flow rate in the direction of flow and Ac is the cross sectional area. JAz is neglected, while JAx normal to the direction of the flow, may not be nglected. NA = Baz = CA Uz  CA /Ac We can express the molar flow rate FA =  CA when not accounting for diffusional effects, However when accounting for diffusional effects The molar flow rate FAz is = NA Ac 3 2
  • 26. FA = NAz Ac = - CDAB + xA (Nz) Ac dxA dz   Where Nz is the total molar average flux in z direction of all n species , i.e Nz =  Niz i=1 m
  • 27. Mass Flux Molar Flux Reference system nA = A UA NA = CA UA Fixed Coordinates jA = A(UA- U ) JA = CA (UA- U ) Molar average Velocity jA = A (UA- U ) JA = CA (UA- U ) Mass average Velocity jA = A (UA- U ) vJA = CA (UA- U ) Volume average Velocity Fluxes for Binary Systems M M M M m m m m v v v
  • 28. Relationships between Fluxes Relationship between mass and molar fluxes nA = NA MA MjA = mjA M MA MjA = MJA MA mJA = MJA MB M
  • 29. Relationships between Fluxes Molar flux Relative to U M NA +NB = C U M MJA + MJB = 0 NA = MJA + xA ( NA +NB NA = MJA + CA U M
  • 30. Relationships between Fluxes Mass flux Relative to U m nA +nB =  U m mjA + mjB = 0 nA = mjA + A ( nA +nB) nA = mjA +  A U m
  • 31. Changing from one reference to another Hooyman et al (1953) derived a general diffusion coefficient expressed as JA =-DAB xA 1-A 1-xA 1 V Molar volume of the mixture Weighing factor relating to the appropriate velocity
  • 32. A Reference velocity Fick`s Law  A mJA xA MJA CA VA vJA U m U M U v Weighing factors Values
  • 33. Formulation of Mass Transfer Models Macroscopic models Describe industrial Process but do not provide a detailed description of the process. Because the properties of the system are averaged over position. The only independent variable is time , so its easy to solve the derived differential equation of macroscopic models
  • 34. Macroscopic material balance Inlet (i) Applying the law of conservation of matter to a stream flowing into a volume element fixed in space Outlet (i) Volume element General Material Balance in the RATE FORM Rate of Accumulation Rate of Transport into Rate of Transport Out Rate of generation Rate of Transport Out
  • 35. General Material Balance for total flow of mass V V U S U S ( ) Mass of material within the system Average velocity of the fluid Dividing both sides by and shrinking the time to zero we get dt d (  V ) ( U S) ( U S) ( U S)
  • 36. Note: 1- Since total mass can not be neither created nor destroyed both the generation and consumption terms are not present. (no chemical reaction). 2- the mixing within the volume element is perfectly mixed concentration leaving or entering the volume is the same. 3- The subscript on the exit term (Outlet) will be dropped from the equation because the exiting stream is a variable. 4- The S in and out are the same. THE MASS BALANCE BECOMS dt d S 1 (  V ) ( U) ( U) Absence of Coordinates
  • 38. Derivation of continuity equation Eulerian approach In this approach the mass of component A moves at a velocity, UA through a fixed volume element And Can be extended to cases where the volume element moves with some reference velocity ( UM, Um, U ) M m v
  • 39. Start: considering a differential element of fixed shape  Flow entering and leaving the element at all direction.  Substitute mass flux terms for species A into the general balance equation Rate of Accumulation Rate of Transport into Rate of Transport Out Rate of generation Rate of Transport Out
  • 40. (nAx - nAx ) Y Z x X +x (nA - nAx ) X Z Y Y +Y (nA - nAx ) X Y Y Y +Y rA X Y Z * X Y Z A   t 