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Low molecular-weight ethoxy-based surfactants are able to accelerate oxygen
delignification of softwood kraft pulps [26]. The extent of lignin removal was
increased from 45% to 55% when 1wt.% of surfactant (15-S-5) was added to medium
consistency oxygen delignification (110 °C, 690 kPa, 60 min) using a commercial
softwood kraft pulp, kappa number 22. The study revealed that the
improved delignification efficiency can be explained rather by an accelerated
chemical reaction rate than by an increased diffusion rate. It can be assumed that
the presence of surfactants increases both the solubility of lignin and oxygen in
the liquid phase, thus increasing the intrinsic delignification rate.
7.3 Oxygen Delignification 687
7.3.4
A Model to Predict Industrial Oxygen Delignification [27]
Industrial oxygen delignification is reported to be less efficient as compared to laboratory
oxygen delignification. A study provided by Rewatkar and Bennington
revealed that industrial oxygen delignification systems operate, on average, at
about 20% below their potential [28]. The impaired efficiency of oxygen delignification
can be attributed to mass transfer limitations which occur under industrial
conditions. Oxygen delignification of pulp is a three-phase reaction system comprising
pulp fibers (solid phase), an aqueous phase, and the oxygen gas phase.
The mass transfer of oxygen to pulp fibers in medium consistency oxygen delignification
is shown schematically in Fig. 7.34.
Oxygen
gas bubble
kL
Liquid film
OHdissolved
oxygen
degraded
wood
compontens
Immobile
Liquid film
k FIBER S
Fig. 7.34 Scheme of mass transfer of oxygen to pulp fibers in
medium consistency oxygen delignification process (according
to Hsu and Hsieh [10]).
The process of oxygen delignification is described as follows:
_ Solubilization of oxygen in the alkaline pulp suspension during
high-shear mixing: first, oxygen transfer from the gas phase
through a gas film into the gas–liquid interfacial boundary takes
place. This is followed by oxygen transfer from the boundary
through a liquid film into the bulk liquid phase.
_ Diffusion of dissolved oxygen from the water surrounding the
fibers through the fiber wall, where the reaction occurs: dissolved
oxygen is transported from the bulk phase into the immobile liquid
layer surrounding the fiber by diffusion and convection, followed
by diffusion of hydroxide ions and oxygen molecules
through the immobile water layer to the fiber. Finally, the process
chemicals reach the reaction sites in the fiber through inter- and
intrafiber mass transfer.
Quite recently, van Heiningen et al. have presented a model where the effect of
mass transfer of oxygen on the efficiency of delignification in an industrial reten-
688 7Pulp Bleaching
tion tower is simulated [27]. The reaction conditions that occur at the entrance of
the oxygen reactor are determined by simulating the mass transfer and reaction
processes in a high-shear mixer. Figure 7.35 shows a simplified oxygen delignification
stage flowsheet.
MIX
NaOH
Oxygen
Steam
RETENTION
TOWER
WASH
VENT
Fig. 7.35 Schematic flowsheet of oxygen delignification.
Screened and washed pulp is pumped through one or more high-shear mixers,
where alkali, oxygen and steam are dispersed under pressure into a medium-consistency
suspension. Pulp passes through an upflow tower and is discharged from
the top of a blow tank from which gases are separated out, and the pulp finally
enters subsequent washers. The model presented by van Heiningen et al. is based
on this simplified process scheme. The main objective of this model is to calculate
the effect of the mass transfer of oxygen on the efficiency of delignification as a
function of caustic and oxygen charges, oxygen pressure, consistency and temperature.
Some minor changes and supplements have been introduced into the following
model proposed by van Heiningen et al. The model considers the following elements:
_ Oxygen solubilization during high shear mixing: the volumetric
mass transfer rate of oxygen, kLa (M), is obtained from an empiric
equation derived by Rewatkar and Bennington [29].
_ Oxygen balance through the retention tower assuming steadystate
conditions at a given pulp production rate and dimensions
of the retention tower.
_ The gas void fraction, X g, is calculated assuming a preset and constant
gas-to-suspension linear velocity ratio.
_ The oxygen consumption rate is related to the rates of pulp
delignification and dissolved lignin (carryover) oxidation.
_ The kinetics of kappa number degradation is described by the
one-stage model proposed by Iribarne and Schroeder [12]. Due to
the lack of an appropriate kinetic model, the course of dissolved
organic carbon (DOC) oxidation is modeled by using the model
from Iribarne and Schroeder, as well considering a DOC-to-lignin
conversion factor.
7.3 Oxygen Delignification 689
_ Temperature increase in the retention tower is calculated using
published values of the heat of reactions of both kappa number
degradation and DOC oxidation, whereas heat loss through the
reactor walls is neglected.
_ The saturated oxygen concentration in the aqueous phase is
obtained from the empiric model provided by Broden and Simonson
[30].
_ Values for the mass transfer rate of oxygen, kLa (R) in the tower
are assumed in a certain range, as measured in a laboratory
equipment [28].
7.3.4.1 Theoretical Base of the van Heiningen Model [27]
The pulp suspension is assumed to pass through the oxygen bleaching tower by
plug flow. As the steady state of the process is considered, the course of all variables
through the reactor can be expressed as a function of the residence time t of
the pulp suspension. The oxygen balance is governed by Eqs. (44) and (45):
d _ O 2
dt _ kLa _ O 2_sat __ __ O 2__
_ l
_ s __1 _ con __1 _ Xg _ _ ___ rO 2 _44_
d VO 2 _ g _ dt _ _
d _ O 2
dt _ rO 2 __ _ Vl _45_
where:
t = time after entering the reactor, [s]
[O2] = oxygen concentration in the liquor, [mol L–1]
kLa = mass transfer rate of oxygen to the liquid phase, [Lliquid
–1 Lcontactor s–1]
[O2,sat ] = oxygen concentration in the liquid in equilibrium with the oxygen
pressure, [mol L–1]
ql = density of the liquor, [kg L–1]
qs = density of the suspension, [kg L–1]
con= pulp consistency, mass fraction [-]
X g = gas volume (void) fraction, [-]
r O2 = oxygen consumption rate caused by pulp delignification, [mol
O2 Lliquor
–1 s–1]
V O 2 _ g = oxygen flow in gas phase, [mol s–1]
V˙
l = liquor flow, calculated as V l = R. (1– con)/(con. ql), [L s–1]
R = rate of pulp production, [kg s–1]
It is believed that the gas void fraction, X g, is not constant throughout the reaction,
as was assumed by van Heiningen et al. due to progressive oxygen consumption
[27]. Instead, it is supposed that the gas to suspension linear velocity ratio can
be kept constant, which should be valid as long as the production rate remains
stable. The linear gas velocity in the tower is assumed to be higher than the veloci-
690 7Pulp Bleaching
ty of the suspension due to the density difference between the gas and suspension.
X g can then be calculated according to Eq. (46):
Xg _
_ V
g
_ V
s _ vgvs _ _ V _ g _ _46_
where:
V˙
g = gas flow, calculated as V˙ g= V O 2 _ g. 0.008315. Tp –1, [L s–1]
T = temperature, [K]
p = pressure, [MPa]
V˙
s = suspension flow, calculated as V˙ s = R /(con. qs) [L s–1]
v g/ v s = ratio gas to suspension velocity [-]
The oxygen consumption rate, r O2, depends on both the degradation of residual
lignin and dissolved oxidizable matter (carryover), measured as DOC according to
the following expression:
rO 2 _ _
1_5 _ d _
dt _ b 1 _ dDOC
_ dt _ b 2__ R
32 _ _ Vl _47_
where:
b1 = stoichiometric coefficient for the reaction of oxygen with the residual
lignin [g DO2/g Dlignin]. The value of b1 is taken as 1.0 [31].
DOC = dissolved organic carbon, kg t–1 pulp
b2 = stoichiometric coefficient for the reaction of oxygen with the dissolved
black liquor [kg DO2/kg DDOC]; as no experimental values are available,
it is assumed that only the dissolved lignin fraction reacts with
oxygen: 50% of the DOC can be assigned to lignin compounds, and
1kg lignin relates to 0.63 kg DOC, then 0.5/0.63 = 0.79 kg lignin kg–1
DOC; therefore, b2 can be taken as 0.79 kg DO2/kg DDOC.
The kinetics of kappa number degradation is described by the model obtained
by Iribarne and Schroeder [12] (Tab. 7.17), as proposed by van Heiningen et al.
[27]. Any other kinetic model, as introduced in Chapter 4.2.3 (Mass transfer and
kinetics) may also be used for illustration. The validity of the model from Iribarne
and Schroeder is limited to softwoods (preferably Pinus taeda) in the kappa number
range 20–58 (see Tabs. 7.14 and 7.17):
_
d _
dt _
3_0 _ 106
60 _ Exp _
8_315 _ T __ OH _ _ 0_7
__ O 20_7__2_0 _48_
where T is the temperature, °K after residence time t, and [OH– ] (mol L–1) is the
hydroxide ion concentration in the liquor. The change in hydroxide ion concentration
can be calculated as follows:
d OH _ _ dt _ _
1_5 _ d _
_ dt _ b 3__ R
17 _ _ Vl _49_
7.3 Oxygen Delignification 691
where b3 = stoichiometric coefficient of hydroxide ion consumption by the residual
lignin of the pulp, given as kg hydroxide ions, OH–, consumed per kg lignin
removed; b3 is taken as 0.9. 17/40, based on recent measurements by Violette
[32].
To the present authors’ knowledge, a kinetic expression for DOC degradation
during oxygen delignification is not yet available. In order to estimate the effect of
dissolved lignin, measured as DOC, on the course of oxygen delignification, a
similar kinetic expression as depicted in Eq. (48) is considered.
The heat of reaction is estimated by a value of 14 MJ per ton of pulp and
removed kappa number [33]. Thus, the temperature increase caused by the oxidation
reactions during oxygen delignification may be obtained from Eq. (50):
dT
dt _
D HL _ d _
dt _ 1_5 _ D HDOC _ dDOC
_ dt _
cpulp _ cH 2 O _ 1
_ _ con _ 1__ mO 2_ g _ cO 2_ _50_
where:
DHL= heat of reaction of residual lignin oxidation [9.3 MJ kg–1 lignin], assuming
that one kappa number unit, j represents 1.5 kg of lignin in 1 t of
pulp.
DHDOC = heat of reaction dissolved lignin oxidation [7.4 MJ kg–1 DOC], assuming
that 1kg DOC contains 0.79 kg of dissolved lignin.
mO2_g = oxygen in gas phase, [kg t–1 pulp]
cpulp = specific heat capacity of pulp, 1550 kJ t–1 K–1
cH2O = specific heat capacity of water, 4187 kJ t–1 K–1
cO2 = specific heat capacity of oxygen, 0.93 kJ kg–1 K–1.
The pressure drop across the reactor can be calculated by Eq. (51):
dp
dt _ _0_00981 _ _ s _ vs _ _0_00981 _ _ s _
_ V
s _ H
1 _ Xg _ __ V _51_
where H and V are height (m) and volume (m3) of the reactor.
The model of Broden and Simonson was used to estimate the solubility of oxygen
in equilibrium conditions, [O2,sat], as a function of oxygen pressure, temperature
and hydroxide ion concentration [34]. A minimum in solubility is obtained at
a temperature of about 100 °C. The presence of dissolved sodium hydroxide
induces a salting-out effect which leads to a decrease in the oxygen solubility. The
dissolved oxygen concentration as a function of temperature and pressure for two
different sodium hydroxide concentrations is expressed by Eq. (52):
_ O 2_ sat_a1 _ a2 _ T _ a3 _ p _ a4 _ p _ T 2 _ _ a5 _ p _ T __ 0_001 _52_
where [O2,sat] = oxygen concentration in the liquid in equilibrium with the oxygen
pressure, [mol L–1].
The coefficients ai are presented in Tab. 7.19.
692 7Pulp Bleaching
Tab. 7.19 Numerical values of the coefficients ai in Eq. (52) for
the calculation of oxygen solubility as a function of temperature,
oxygen partial pressure and hydroxide ion concentration (as
determined by Broden and Simonson [34]).
Parameter 0.01 M [OH– ] 0.1 M [OH– ]
a1 3.236 9.582
a2 –0.00747 –0.02436
a3 –56.02 –94.77
a4 0.00016 0.00025
a5 15421 24610
Solubilization of oxygen in the alkaline pulp suspension is accomplished by
high shear mixing. The volumetric mass transfer rate of oxygen to the liquid
phase, kLa, for the mixer can be calculated by an empirical equation determined
by Rewatkar and Bennington [29], considering the specific power dissipation,
e[Wm–3], the gas void fraction, X g, and the pulp consistency, con:
kLa _ 1_7 _ 10_4 _ e1_0_ Xg _2_6
_ Exp __0_386 _ con _ _53_
where e = power dissipation per unit volume of the mixer, [W m–3].
The power dissipation of the mixer largely determines the achieved level of dissolved
oxygen concentration at the entrance of the retention tower. So far, only
limited data are available concerning the mass transfer rate, kLa, in the tower.
Based on laboratory measurements, Rewatkar and Bennington reported kLa values
in the tower as being in the range between 0.002 and 0.01s –1 [28]. In their chemical
reactor analysis, van Heiningen et al. have not considered any relationship between
the efficiency of a high-shear mixer in terms of the extent of dissolution of
oxygen in the aqueous phase and the mass transfer rate, kLa, in the tower [27].
Based on our own industrial experience, we believe that the efficiency of a highshear
mixer also determines the kLa in the tower to a certain extent [35]. It was
shown that the increase of both power dissipation and residence time in a highshear
mixer significantly improved the degree of delignification of a beech acid
sulfite dissolving pulp. Therefore, we are quite convinced that there should be a
relationship between the efficiency of a high-shear mixer and the mass transfer
rate in an oxygen delignification tower. As bubbles of oxygen gas tend to coalesce
during their transport through the tower, the kLa would rather follow a gradient to
lower values. Due to lack of information, the effect of different kLa values in the
tower on the extent of delignification is evaluated in a case study.
The second step of the mass transfer of oxygen to pulp fibers is the diffusion of
dissolved oxygen from the water surrounding the fibers through the fiber wall
where reaction occurs. It has been estimated by considering the ratio between the
rate of oxygen consumption by reaction to oxygen diffusion into the fiber that the
7.3 Oxygen Delignification 693
liquid–fiber transfer resistance is negligible in comparison with the apparent
intrinsic reaction rate [10,27]. Therefore, the intra-fiber diffusion resistance is considered
insignificant for oxygen delignification. Quite recently, measurements
revealed that oxygen is able to diffuse at least a distance of some 4–6 mm within
the pulp suspension in a 60-min retention time of a typical pressurized retention
tower at 786 kPa [36].
The effect of mass transfer of oxygen on the course of delignification through
the mixer and the bleaching tower can be calculated by solving the equations
numerically.
Although the model equations can be solved by any method suited for solving
ordinary differential equations (ODE), we use a simple scheme which exploits the
structure of the equations to yield accurate and reliable results. The tower is
divided into a large number of layers, each of volume DV. A total of 500 layers was
used for the examples discussed below, and this resulted in an error lower than
0.0001kappa units at the outlet of the reactor. The retention time Dt in the volume
element DV is calculated by the following expression:
D t _
1 _ Xg _ __ D V
_ V
s _54_
The calculation in a layer consists of two steps. In the first step, an approximation
for the variables at layer outlet is obtained, while the second step applies the
midpoint rule to improve the approximation.
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