Environmental Engineering Reference
In-Depth Information
At the upper boundary:
T n
T n
n n
n
·
N O 2 =
0
,
u
·
n
=
0
,
u
+ (
u
)
u
+ (
u
)
·
=
0 )
At the lower boundary:
n
·
N O 2 =
0
,
u
=
0
(7)
At the outlet boundary
I n
·
C O 2 =
2
3 ( ∇·
T
,
=
p atm ,
+ (
=
n
0
p
u
u
)
u
)
0
(8)
At the particle surface:
n
·
N O 2 =−
K r C O 2 C coke ,
u
=
0
(9)
In Eqs. ( 4 )-( 9 ) p atm is the atmospheric pressure, I is the identity tensor, C inj
O 2 is
the oxygen concentration in the injected gas, F inj is the mass flux of the injected
gas, n is the unit normal vector pointing outside the boundary, K r is the reaction rate
constant, C coke is the coke surface molar concentration at the particle surface, and
N O 2
represents the oxygen total molar flux expressed in the next form
N O 2 =−
D O 2
C O 2 +
u C O 2
(10)
The units of C O 2 and C coke are mole/m 3 and mole/m 2 , respectively. As initially
the oxygen concentration is 0, then the gas is only composed by nitrogen with a
molar concentration depending on temperature and pressure.
In turn, the coke concentration at the particle surface is computed through the
solution of the following differential equation
C coke
=− ʷ
K r C O 2 C coke
(11)
t
ʷ
where
is the stoichiometric coefficient between oxygen and coke. This equation
has the next initial condition
C coke
At
t
=
0
,
C coke =
(12)
where C coke is the initial coke concentration.
On the other hand, the density (
ˁ)
was calculated using the real gas equation, the
reaction rate constant ( K r )
was obtained using an Arrhenius-type expression, and
the gas viscosity was calculated with the Wilke approach (Wilke 1950 ) for binary
mixtures at low pressures. The oxygen diffusivity was obtained from the work of
Bird et al. ( 2010 ).
 
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