The unceasing production of anthropogenic CO
2 has been rising serious concerns among scientific community. Since the signing of Kyoto protocol, back in the 1997, tight policies have been implementing in order to decrease the amount of CO
2 generated from industrial processes and domestic activities, as well as to reduce the overall CO
2 concentration in the atmosphere, whose value above 420 ppm is targeted to play a role in global warming and climate change [
1]. In this scenario, “carbon capture, utilisation and storage” (CCUS) encompasses the set of activities in the fields of basic science, technology development, regulatory affairs, etc., aimed at subtracting CO
2 from the atmosphere by permanent confinement, through the implementation of physical, chemical, biological CO
2 fixation/conversion, as well as developing processes with a zero net impact of CO
2, by directly capturing the CO
2 when it is produced [
2,
3]. Indeed, the release of CO
2 into the atmosphere primarily occurs from specific sources, including thermoelectric plants, foundries, cement factories, and so on. This category of CO
2, known as "capturable CO
2," is emitted near its production source, making it more manageable to trap using targeted technologies [
4]. Among these, the post-combustion approach expected that the CO
2 is captured from the exhaust gases of the combustion process, and it is the most promising sequestration route as it comes just after the process that produces carbon dioxide [
5,
6]. The concentration of CO
2 in the exhaust gases is typically between 4-14 v/v%, with unfavourable conditions for gas separation at atmospheric pressure [
7]. In these operating modes, the denitrified and desulphurised CO
2 reacts with liquid, such as MEA (methyl ethyl amine), the only widely used and established commercial solution, or filtered by specially designed membranes, rising concerns on the whole environmental sustainability of the process [
8]. A more viable alternative to remove CO
2 being now on the spot is the so-called mineralization of carbon dioxide,
i.e. its transformation into carbonates of alkaline and alkaline-earth metals starting from mafic and ultra-mafic minerals, as well as metal oxides or hydroxides. Among the minerals, olivine, serpentine, talc, basalt are some of the investigated minerals which gained wide attention due to low cost and large availability. In particular, olivine is an abundant mineral in the Earth's crust (>50% by upper mantle volume) commonly found in mafic igneous rocks [
9]. The mineralisation process using Ca-Mg-Fe natural silicates was proposed in the pioneering reports of Seifritz [
10] and Lackner [
11] mimicking the phenomenon that naturally happens in the deep oceans. The whole set of reaction schemes accompanying CO
2 mineralization is quite complex and it is well known in the literature [
8,
12]. It is worth remembering that metal carbonate may be formed at expense of corresponding silicates or of other metal precursors, and these reactions can occur in parallel with metal oxidation, H
2 evolution and CO
2 reduction processes. However, the process occurs with too sluggish kinetics that limit its feasibility for large-scale purposes. Despite this main hurdle, several methods have been studied to increase the reaction rate of silicates in carbonation, such as chemical and electrochemical activation [
13], thermal activation [
12], the use of additives in the reaction fluid with high temperatures and pressures [
14] or mechanochemical activation [
14,
15]. Thermal activation leads to dehydrating hydrosilicates, such as serpentine minerals but is ineffective on olivine [
12]. Chemical activation allows for the removal of metal cations from silicates but involves a high additional cost for the disposal of hazardous acid sludge [
16]. On the other hand, mechanical activation reduces the average size of the crystallites with a corresponding increase in the surface area and eventually in the active-reactive sites of the silicate. Even though this technique is energy-demanding, it could become effective if integrated with pre-existing processes [
17]. In this regard, mechanical milling, with repeated fracturing on the reagent powders, would induce structural defects into materials, reduce the average size of mineral grains and expose new active surfaces in the reaction environment [
18]. Mechanochemical treatment was found to be an effective way to enhance the reactivity of natural silicates [
19,
20] and several reports [9, 15,21,22] highlighted how the microstructural parameter and texture properties were influenced by type of grinding, duration, presence or liquid as water or ethanol. A further step forward was taken by highlighting that by grinding natural silicates (such as forsterite, serpentine and wollastonite) in the presence of CO
2 (reactive milling, RM) [
23], promoted mechanochemical absorption of carbon dioxide in the form of metal carbonate. More recently, studies based on the mechanical treatment of olivine minerals conducted by our research group [
24,
25] have highlighted the effective CO
2 mechanosorption on silicates, although in batch conditions (under static CO
2 atmosphere). Nonetheless, there are no applications to processes mechanochemically activated and carried out in continuous-gas-feeding mode. This work aims at studying the behaviour of olivine as solid-state CO
2 store in flow conditions, driven by mechanochemical activation, thus simulating a mechanochemically induced process of post-combustion CO
2 capture and transformation, ideally applicable to an industrial process that continuously emits CO
2. Moreover, the conversion process will be investigated by a structural characterization to get more insight into the serpentinization process in dynamic conditions.