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Mineral Carbonation Feasibility, an Economic Approach.

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MINERAL CARBONATION FEASIBILITY, AN ECONOMIC APPROACH

Louis-César Pasquier1, Nassima Kemache1, Emmanuelle Cecchi1, Guy Mercier1, Jean-François Blais1, Sandra Kentish2

1 INRS ETE, 490 rue de la Couronne, Québec, QC, G1K 9A9

2 Dep. Biomolecular & Chemical Eng. The Univ. Of Melbourne, Melbourne, VIC, Australia

A natural solution for an environmental problematic

Mineral carbonation is one approach proposed for tackling anthropic CO2 emissions. It mimics the natural reaction of silicates weathering, were the gaseous CO2 reacts with a divalent cation to form the associated carbonates following the reaction:

MeO + CO2 = MeCO3 +Heat

Mineral carbonation advantages/challenges are:

Advantages:

Various feedstock can be used:

Natural minerals; Olivine, Serpentine, Wollastonite etc. Alkaline Wastes: Mining residues, Concrete, Slags, Kiln dusts etc.

Reaction can bedirectly performed with flue gases: No need for capture step.

Value added by-product:

Rentability for the processes, waste valorization.

Challenges:

Reactivity limited feedstocks:

The mineral stability can greatly limit the reaction. Some alkaline waste have a small sequestration

capacity.

Slow kinetics:

Might increase the energy needs.

Needs important feedstock resources.

Tailings

Crusher Mill

Magnetic separation

Transportation

1- Mining site: Milling and Magnetic separation

Fuel Gas R1 R2 R3 Water Flue gas Compressor Mill R4 R5 R6 Precipitation Treated Flue gas Dryer Carbonates Dryer Amorphous solids

2- Industrial Emitter: Carbonation Plant

Magnetic fraction Solid stream Gas stream Liquid stream Pulp stream Legend:

The process:

Use serpentinite mining tailings for direct industrial flue gas CO2 capture and storage.

Pre-treatments:

Grinding (granulometry < 25µm)

Magnetic separation: Magnetite (30$/t) Heat activation: 650°C for 30 minutes

CO2 capture and storage (3 steps):

Reaction between the flue gas and the residues in the presence of water (25°C and 10 bars for 15 minutes)

Filtration: CO2 & Mg-saturated solution and inert solids High purity carbonates precipitation (40°C)

Solids recirculation:

During the gas treatment step, solids are recirculated.

A reconditioning step by grinding is required to increase the Mg leaching efficiency.

Many emitters within an acceptable transportation range

MTL Est:150km (train) Suncor

1 158 412tCO2

Process diagram (Pasquier et al., 2016) Railroad network and emmiters in the southern Quebec province

Cost model parameters:

Plant treatment capacity: 200t rocks / h Transportation distance: 200 Km

Sequestration efficiency: 234 kgCO2 / t rocks Energy unit costs (Electricity):

Hydroelectricity: 3.5 ¢ / kWh Coal: 7.8 ¢ / kWh

Energy unit cost (Heat Activation & Precipitation): Nat. Gas: 3.00 $ / MBtu

Biomass:1.54 $ / MBtu

Transportation unit cost: Truck: 0.12 $ / km Train: 0.07 $/ km

Profitability analysis parameters:

Carbon credit price: 10.75 $ / tCO2

Magnesium carbonate sale price: 275 $ / t MgCO3 Magnetic fraction sale price: 30 $ / t

Results

GC23C-1251

Energy and GHG balance

Process Step Power (MJ/t.rock) Heat (MJ/t.rock)

Crushing / Grinding and Magnetic sep. Heat Activation

Gas compression

Carbonation reactors (R1- R6) Reconditionning

Precipitation

Others (pumps, conveyors etc.)

Total 83 1 143 68 0.4 36 467 76 263 1610

Process power and heat consumptions :

Effect of the energy source on the process storage capacity and global process cost

The process energetical demand is mostly heat.

The energy source is greatly impacting the process net storage capacity and cost.

Model principal parameters

Train & NG Train & Biomass

Total process costs ($/tCO2) Net profit ($/tCO2)

Annual sequestration capacity (tCO2/year)

Capital costs (M$)

Payback Period (years)

152

Truck & NG Truck & Biomass

490 246 152 203 1.39 143 502 385 512 203 1.36 191 450 189 754 203 1.51 182 462 329 114 203 1.47

Process economics for base case scenario :

Economics analysis

The process is economically profitable Profitability relies on the carbonates sale

The sensitivity analysis highlights the importance of the sequestration efficiency.

The process costs remain below 200$ for a capa-city up to 50t/h.

Conclusions

Mineral Carbonation can be a feasible and profitable approach for industrial direct CO2

emissions abatement.

One step capture and storage strategy is a key Energy consumption reduced.

The energy efficiency of the process can be increased.

For more details: Pasquier, L. C., Mercier, G., Blais, J. F., Cecchi, E., & Kentish, S. (2016). Technical and economic evaluation of a mineral carbonation process using southern Québec mining wastes for CO2 sequestration of raw flue gas with by-product recovery. International Journal of Greenhouse Gas Control, 50, 147-157. doi:10.1016/j.ijggc.2016.04.030

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