Decarbonisation Technology - May 2024 Issue

Feedstock

Products

CO 2 emissions

5,312,500 crude oil 165,671 green H 2

Total products Gasoline product Diesel product

4,887,500 1,075,250 1,857,250 1,466,250 488,750

993,333

Complete refinery

5,352

Naphtha and gasoline complex Diesel, kero and conversion units

393,000 594,982

Kerosene product Other products - units

Other units

Optional case: 100,000 BBL processing refinery, high conversion. Carbon capture for blue hydrogen and synthetic fuels

Table 2 Hybrid refinery or fuels production centre feedstock and products

Capacity (A, TPA)

Cost (CE, Euros)

Capacity (A, TPA)

Cost (CE, Euros)

CCUS

A1 A2 A3

900,000 39,000 165,671

102,000,000 1,557,500,000 625,000,000 Total cost: 2,284,500,000

CCUS Synth

A1 A2 A3

884,230 20,075 100,000

102,806,197 1,031,658,184 461,670,496 Total cost: 1,596,134,877

Synth fuels

Green H 2

Green H 2

Table 4 Capital cost optimised using optimisation LP evolutionary algorithms

The analysis is based on the methanol to SAF process, comprising methanol synthesis, dimethyl ether (DME) production, and olefins oligomerisation. The synthetic fuels unit will produce 10% of the middle distillate products, enabling a 10% reduction in the load on the conventional middle distillates hydrotreatment units, as well as a reduction in the crude oil feed to the refinery, improving the reduction in the carbon footprint (see Table 2 ): • Synthetic fuels unit (e-SAF & e-diesel): 332,350 TPA • CO 2 : 1,258,902 TPA • H 2 : 176,246 TPA Table 3 Preliminary Class 5 estimate for the cost of new configuration

The CO 2 emissions in the two analysis cases present the conditions shown in Figure 5 . Optimisation of hybrid solution alternatives by means of linear programming concept The configuration analysed in the previous sections complies with the following criteria: • Maximum reduction of CO 2 emissions. • Use 100% of the CO 2 captured inside the refinery as feedstock (no vent, no transportation out of refinery). Table 3 give a preliminary Class 5 estimate for the cost of the new configuration. The size of each unit was optimised using linear programming (LP) with the following variables: • Total cost must be set to a calculated minimum. • A positive impact of carbon credit is included for an equivalent period of five years as a cost reduction factor. • Restrictions according to:

2 , 500 , 000

2 , 125 , 000

2 , 000 , 000

 CCUS A1 <900,000  CCUS A1 >600,000

1 , 500 , 000

993 , 333

1 , 000 , 000

 Synthetic fuels unit A2 <39,000  Synthetic fuels unit A2 >20,000

500 , 000

 Hydrogen electrolysis unit A3 <166,000  Hydrogen electrolysis unit A3 >100,000. These variables were used to conduct an LP optimisation using the evolutionary optimisation methodology. Evolutionary optimisation

0

CO base case renery

CO optional case renery

Figure 5 CO 2 emission comparison base and optional cases (values in TPA)

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