Warshaw, 2017). Therefore, several stationary and
dynamic modelling and simulation studies have been
performed to optimize the sulphuric acid
manufacturing plant. In particular, numerous studies
have been conducted on the steady and dynamic
modelling of SO
2
oxidation reactors, which focused
on the design and operating conditions. For example,
Günther et al. (Günther et al., 2012) developed a
mathematical model to describe the dynamics
oxidation of SO
2
to SO
3
. The results proposed a new
design for zero-emission to the environment. Also,
Mann et al. (Gosiewski, 1993) proposed a new
dynamic simulation based on ordinary differential
equations, which describes the behaviour of a single-
bed reactor in the contact sulphuric acid plant, thus,
several variables have been studied, such as flow
start-up and initial fixed-bed reactor temperatures.
Interestingly, the results showed that the model can
be used for the qualitative analysis of SO
2
oxidation.
Recently, Sørensen et al. (Sørensen et al., 2015)
validated a dynamic model of SO
2
oxidation using
experimental data from a sulphuric acid pilot plant.
The results demonstrated that the dynamic simulation
can efficiently be used to evaluate operating
conditions, equipment sizing with respect to the
environmental impact.
In contrast to the previous studies, few studies
were conducted for the complete sulphuric acid plant.
Notably, Kiss et al. (Kiss et al., 2010) presented a
complete model of an industrial sulphuric acid plant
using gPROMS tool. The results demonstrated that
40% of SO
x
emissions can be reduced by the
optimization of the split fraction or feed flow rates. In
addition, they developed an excel interface, which
simulates the real behaviour of the plant. Also, the
results of Oni et al. (Oni et al., 2018) showed that the
process can be operated at different optimal
conditions, and the ideal conditions was 9.5 ppm of
SO
x
and 70.9 ppm of acid mist and 143.0 M$/y of net
revenue. Likewise, Rahman et al. (Rahman et al.,
2019) developed a new model that offers a cost-
effective solution to reduce energy demand and limit
emissions of aromatic compounds. In addition to the
above-mentioned study, Chowdhury et al.
(Chowdhury et al., 2012) simulated and optimized a
simplified process for the production of sulphuric
acid using Aspen HYSYS simulator. The results
exhibited that the process plant simulation is an
effective approach to optimizing annual profit. On the
other hand, various limitations are noted in the
models mentioned, for example, the non-
consideration of the thermal kinetics of the
conversion reactions, which is a key step in the
sulphuric acid manufacturing plant.
Based on the previous investigations, a
considerable effort has been made to improve the
performance of the double-absorption contact
process. Indeed, these studies were based on multi-
objective optimization, which considers
environmental impact as a main objective such as
sulphuric acid production. In this context, it is
important to dispose of more powerful and flexible
modelling and simulation solutions, which reflect the
experimental plant reality, and resolve the limitations
of the existed models. In this study, the closed loop
of sulphuric acid process is modelled and simulated
using UniSim Design R451 simulator and validated
with plant data.
2 PROCESS DESCRIPTION
The simplified bloc-flow diagram of the sulphuric
acid manufacturing process with double absorption is
presented in Figure 1.
Firstly, moist air is filtered in an air filter to
eliminate particles contained in the air. To reduce its
moisture content, the air is dried by absorption in a
drying tower using the circulating sulphuric acid
H
2
SO
4
. The liquid sulphur that has been prepared in
the melting unit is burned with the dry air in the
sulphur burner, which forms the sulphur dioxide SO
2
.
The reaction of sulphur combustion is exothermic;
thus, a waste heat boiler is paced at the outlet of the
sulphur burner to recover the heat of the sulphur
combustion and generate the saturated steam. As the
optimal required temperature for the sulphur dioxide
SO
2
conversion is 420°C, a by-pass of the sulphur
burner is mixed with the waste heat boiler outlet to
regulate the desired temperature. The conversion of
SO
2
into SO
3
is carried out in a converter formed by
four catalytic bed. The vanadium oxide V
2
O
5
is used
as a catalyst to accelerate the SO
2
/SO
3
conversion. In
order to reach the high desired conversion on SO
2
, the
gaseous outlet flow of the 1st converter bed passes
through an inter-pass heat exchanger to regulate its
temperature before feeding the 2nd converter bed.
Between each bed of the four converter beds, heat
exchangers and economizers are used for the same
raison. After passing the three first beds of the
converter, the outlet flow of the 3rd bed feeds the first
absorption tower, in which the SO
3
formed reacts
with the H
2
O presented in the diluted circulating
H
2
SO
4
98% to form the concentrated H
2
SO
4
99%.
The outlet gas flow of the first absorption tower
feeds the 4th bed of the converter where the remained
SO
2
is converted to SO
3
, before feeding the second
absorption tower in order to absorb the formed SO
3
.