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Current status of CO 2 capture from coal facilities                51

           H 2 and CO produced by steam methane reforming. The carbon capture facility uses an
           amine-based solvent (BASF’s OASE® white technology) to capture 90% of the CO 2
           produced (0.8 Mt/y). The CO 2 product is compressed, dehydrated, and pumped
           through a 50 km pipeline for injection into an Abu Dhabi national oil company
           onshore oil field for EOR.
              Although the steel industry in Japan is the world’s top level efficiency, its CO 2
           emissions still account for 15% of the total. The Japan Iron and Steel Federation under
           the project COURSE 50 aims to develop advanced technologies to reduce CO 2 emis-
           sions by 30%, to establish them by 2030, and to industrialize and transfer them by
           2050. A double approach is pursued: (1) 10% mitigation is expected to be achieved
           through the reduction of iron ore with reformed coke oven gas and (2) 20% by CO 2
           capture from blast furnace gas (BFG) using chemical absorption and physical adsorp-
           tion methods and unused waste heat (Tonomura et al., 2016). The project is developing
           advanced technologies to exploit unused waste heat to capture CO 2 . Advanced sol-
           vents, tested with real BFG at pilot plants CAT1, of 1 t/d, and CAT30, of 30 t/d,
           have shown reduced regeneration energies of 2.5 GJ/t for over 2,000 h operation in
           2011 at 90% capture rate (Tonomura, 2013). The advanced separation system by car-
           bon oxide adsorption (ASCOA) has been evaluated in a small pilot-scale plant,
           ASCOA-3, with a CO 2 recovery capacity of 3 t/d at JFE Steel’s West Japan Works
           in Fukuyama, Japan. The BFG is pressurized, cooled, and dehumidified using silica

           and alumina gel to a dew point of  60 C. The dry gas is then compressed to

           0.15e0.3 MPa, cooled down to 10 C, and fed to a PSA unit that uses a zeolite
           (zeolum F9) as adsorbent. The technology has been validated with CO 2 recoveries
           up to 6.3 t/d with a cost of 63% of the original recovery cost (Saima et al., 2013a)
           and an associated energy consumption of 0.44 GJ/t (GCCSI, 2014). The total cost esti-
           mated for a commercial plant with a capacity of 1 Mt/y is only $20/t CO 2 (Saima et al.,
           2013b).
              The European STEPWISE Project will demonstrate SEWGS technology using the
           BFG from a steel plant at the 15 t CO 2 /d scale in Luleå, Sweden. The pilot consists of a
           compression section, an advanced WGS section, and a SEWGS section. Although
           SEWGS is a multicolumn reactive hot PSA process, in the pilot, a single column
           will be used to demonstrate the H 2 /CO 2 separation in countercurrent PSA, using
           2.5 t of K-promoted MgOeAl 2 O 3 hydrotalcite-based sorbent material. Operation
           will focus on the steam requirement to obtain the targeted separation efficiency, cycle
           design, heat management, and the interplay between the WGS and the SEWGS sec-
           tions. The data will serve as reference to fine-tune the SEWGS simulation model
           and to demonstrate material durability using real BFG (van Dijk et al., 2017).


           2.5.4  CO 2 capture in the cement production sector
           90% of the energy consumed by cement plants worldwide comes from coal. The
           cement industry accounts for nearly 5% of anthropogenic CO 2 emissions. Moreover,
           over 60% of the CO 2 emissions of modern cement plants arise from mineral decom-
           position, and thus cannot be avoided by using renewable energy or improving energy
           efficiency. CCUS will be necessary to fully abate the CO 2 emissions from the cement
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