TEXTE Environmental Impacts of Exhaust Gas Cleaning Systems for Reduction of SOx on Ships — Analysis of status quo
Report compiled within the framework of the project ImpEx
2 Technical description of the EGCS technology
There are several information sources from classification societies, governmental authorities,
research institutes and manufacturers describing the fundamentals and operation of the EGCS
technology on board ships. Especially EGCSA (2012), ABS (2019), Lloyd’s Register (2012),
Kjglholt et al. (2012) and US EPA (2011) offer an extensive technical description of EGCS. This
report does not aim to describe into detail the EGCS technology. Thus, only a general description
is presented in this chapter. Aspects related to the water management are discussed more
extensively.
EGCS, also called scrubber, is an established technology in the land-based industry sector for air
pollution abatement (e.g. flue gas from combustion plants) and for recovery of valuable products
from a gas stream. Depending on the medium used for removal of the target compounds, EGCS
can be classified as dry and wet; the first type uses packed bed granulated chemicals and the
latter a liquid stream (typically water) as absorption medium.
In the maritime industry, wet EGCS dominate the market, while for dry EGCS just one
manufacturer (EGCSA, 2012) and four installations (DNV GL, 2020) are reported. The reasons
for the low acceptability are among others, the requirement for extensive space for dry EGCS
installations which cannot be met by many ships and the huge amount of solid waste produced
(gypsum). Wet EGCS are divided in open (OL) and closed loop (CL) EGCS, depending on the
mode of operation; if the installation can be operated in both modes it is called hybrid EGCS.
Figure 1 depicts the differences in the water management between open loop and closed loop
EGCS. Independently of the type of system, water is pumped into an absorption tower and
sprayed into the exhaust gas stream. In the absorption tower, SO, is transferred from the gas to
the liquid phase and subsequently oxidized to sulphate species. The SO2 removal efficiency for
every system depends on several factors (e.g. amount and quality of water, system design,
temperature, initial SO» concentration, and chemical addition) that affect diffusivity and
equilibrium solubility (US EPA, 2002). Removal efficiency can be above 98% (Fridell and Salo,
2014; Lloyd’s Register, 2012). This process is called flue gas desulphurisation or SOx scrubbing.
Figure 1: Process flow for the two modes of operation of wet EGCS: open loop (left) and
closed loop (right)
Open loo* >
xhaust
3 aut
Scrubber
YJilntion
Water
reatmen
{unusua"
im Ib“
+
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icrubber
Process.
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a:
Fresh-
water
Water
Dr
Jilution Water
(optional)
Holding tank
{optional for zerc
discharge)
—
il Discharge
"water
Source: BSH (2020).
17