Abstract:Mineral sequestration has a great potential for abating CO 2 emissions, especially at locations where no opportunities for CO 2 geological storage exist. This article focuses on the mineral carbonation of magnesium silicates, that is, serpentinites, which offers an attractive option for CO 2 emission mitigation in Lithuania. Mineral CO 2 carbonation in a staged gas/solid process route is one of the most prospective approaches. The process was conducted in several steps. Firstly, extraction of the magnesium hyd… Show more
“…An Mg(OH) 2 produced from a Lithuanian serpentinite was carbonated up to 65 % in 15 min in 51 bar pure CO 2 at 535 °C whereas 70 % conversion in 30 min was obtained with Mg(OH) 2 produced from Portuguese rock at 510 °C, 20 bar pure CO 2 , size fraction <74 μm . More detail on Mg(OH) 2 production and carbonation is given in the Experimental Section.…”
Section: Resultsmentioning
confidence: 99%
“…Typical reaction temperatures for the serpentinite/AS salt reaction are somewhat lower than the carbonation temperature, at 400–440 °C so as to avoid decomposition and sublimation “losses” of the AS salt as recently reported . On the other hand, with increased fractions of iron oxides and silicates in the serpentinite a temperature of up to 520 °C (for 20 min) gave the highest extraction yields for Mg and Fe …”
Vast resources of serpenitinite rock available worldwide are capable of binding CO2 amounts that diminish the capacity of methods based on geological storage of CO2. R&D has been ongoing in Finland for many years on developing large‐scale application of process routes for serpentinite carbonation. Several routes have been assessed in the laboratory, in all cases using ammonium salts to extract magnesium from rock followed by carbonation either in a gas/solid reactor at elevated temperatures and pressures or in an aqueous solution at ambient conditions. The choice for either route is motivated by the CO2‐producing source, (waste) heat availability, the magnesium (hydro‐)carbonate product aimed at, and a preference for energy efficiency or simplicity. Rocks from several locations have been analysed. A special issue is the recovery of the ammonium flux salt, typically from an aqueous solution. As for application, several industry sectors are considered, such as a (natural gas fired) power plant, a lime kiln, or iron‐ and steelmaking, applying mineral carbonation (MC) to blast furnace top gas. The analysis includes life cycle assessment (LCA). Finally, the use of magnesium (hydro‐)carbonates for heat storage is addressed.
“…An Mg(OH) 2 produced from a Lithuanian serpentinite was carbonated up to 65 % in 15 min in 51 bar pure CO 2 at 535 °C whereas 70 % conversion in 30 min was obtained with Mg(OH) 2 produced from Portuguese rock at 510 °C, 20 bar pure CO 2 , size fraction <74 μm . More detail on Mg(OH) 2 production and carbonation is given in the Experimental Section.…”
Section: Resultsmentioning
confidence: 99%
“…Typical reaction temperatures for the serpentinite/AS salt reaction are somewhat lower than the carbonation temperature, at 400–440 °C so as to avoid decomposition and sublimation “losses” of the AS salt as recently reported . On the other hand, with increased fractions of iron oxides and silicates in the serpentinite a temperature of up to 520 °C (for 20 min) gave the highest extraction yields for Mg and Fe …”
Vast resources of serpenitinite rock available worldwide are capable of binding CO2 amounts that diminish the capacity of methods based on geological storage of CO2. R&D has been ongoing in Finland for many years on developing large‐scale application of process routes for serpentinite carbonation. Several routes have been assessed in the laboratory, in all cases using ammonium salts to extract magnesium from rock followed by carbonation either in a gas/solid reactor at elevated temperatures and pressures or in an aqueous solution at ambient conditions. The choice for either route is motivated by the CO2‐producing source, (waste) heat availability, the magnesium (hydro‐)carbonate product aimed at, and a preference for energy efficiency or simplicity. Rocks from several locations have been analysed. A special issue is the recovery of the ammonium flux salt, typically from an aqueous solution. As for application, several industry sectors are considered, such as a (natural gas fired) power plant, a lime kiln, or iron‐ and steelmaking, applying mineral carbonation (MC) to blast furnace top gas. The analysis includes life cycle assessment (LCA). Finally, the use of magnesium (hydro‐)carbonates for heat storage is addressed.
“…In general, carbon mineralization can be achieved by two different routes: 1) an indirect process in which the dissolution of the reactive phases and the precipitation of the respective carbonates are performed separately in order to optimize each step; examples of this route are reported for Mg(OH) 2 or for CaO produced by limestone calcination ; 2) direct carbonation, where Ca/Mg oxide or silicate rich residues are carbonated in a single process step in which both dissolution and precipitation take place. Direct carbonation is generally applied via an aqueous phase process performed either through the slurry‐phase route, characterized by a liquid to solid ratio (L/S) above 1 w/w, or by the wet (or thin film) one, with a L/S ratio below 1 w/w .…”
“…In 2013, global CO 2 emissions hit a new record, reaching about 36.1 billion tons. [9][10][11][12][13][14][15][16][17] The carbonation of natural minerals oen requires harsh reaction conditions because the natural minerals are thermodynamically stable. 7 The global carbon cycle is sufficiently extensive to conclude that natural processes cannot absorb all the anthropogenically produced carbon dioxide (CO 2 ) in the coming centuries, so adaptation technologies are urgently required.…”
The feasibility of mineral carbonation of a desulfurization residue for sequestering CO 2 was evaluated both through theoretical and experimental approaches. The carbonation reaction, including carbonation of Ca(OH) 2 and CaSO 4 , occurred through a kinetically controlled stage with an activation energy of 20.21 kJ mol À1 . The concentration of ammonia, CO 2 flow rate, liquid to solid ratio and temperature impacted on the carbonation ratio of the desulfurization residue through their direct and definite influence on the rate constant. Concentration of ammonia and liquid to solid ratio were the most important factors influencing the desulfurization residue carbonation in terms of both the carbonation ratio and reaction rate. Under optimized conditions the carbonation ratio could reach approximately 98% when using industry-grade CO 2 . The crystalline phases of the carbonated desulfurization residue were calcite and vaterite with spherical and granular morphology. CO 2 /O 2 /N 2 mixed gas was also used as the simulated desulfurization fuel gas in the carbonation reaction and it had a relatively minor effect on the carbonation ratio. However, it slowed the carbonation reaction and produced a carbonation product with a smaller average particle size, which included high purity ($99%) white calcite. The carbonated desulfurization residue reported herein showed a rapid CO 2 sequestration ratio, high CO 2 sequestration amount, low cost, and a large potential for in situ CO 2 sequestration in the electricity and steel industry.
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