Next Article in Journal
Adding Value to Waste Minerals in a Circular Economy Framework: Ochre-Derived Layered Double Hydroxide Catalysts in Fatty Acid Ketonisation
Next Article in Special Issue
Spontaneous Serpentine Carbonation Controlled by Underground Dynamic Microclimate at the Montecastelli Copper Mine, Italy
Previous Article in Journal
Texture Development and Stress–Strain Partitioning in Periclase + Halite Aggregates
Previous Article in Special Issue
Using Reservoir Geology and Petrographic Observations to Improve CO2 Mineralization Estimates: Examples from the Johansen Formation, North Sea, Norway
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Mineralogical Transformations of Heated Serpentine and Their Impact on Dissolution during Aqueous-Phase Mineral Carbonation Reaction in Flue Gas Conditions

by
Clémence Du Breuil
1,
Louis César-Pasquier
1,*,
Gregory Dipple
2,
Jean-François Blais
1,
Maria Cornelia Iliuta
3 and
Guy Mercier
1
1
Institut National de la Recherche Scientifique (Centre Eau, Terre et Environnement), University of Quebec, 490 rue de la Couronne, Quebec, QC G1K 9A9, Canada
2
Department of Earth, Ocean and Atmospheric Sciences, University of British Columbia, 2020–2207 Main Mall, Vancouver, BC V6T 1Z4, Canada
3
Chemical Engineering Department, Laval University, Quebec, QC G1V 0A6, Canada
*
Author to whom correspondence should be addressed.
Minerals 2019, 9(11), 680; https://doi.org/10.3390/min9110680
Submission received: 16 August 2019 / Revised: 16 October 2019 / Accepted: 23 October 2019 / Published: 3 November 2019
(This article belongs to the Special Issue Geological and Mineralogical Sequestration of CO2)

Abstract

:
Mineral carbonation is known to be among the most efficient ways to reduce the anthropogenic emissions of carbon dioxide. Serpentine minerals (Mg3Si2O5(OH)4), have shown great potential for carbonation. A way to improve yield is to thermally activate serpentine minerals prior to the carbonation reaction. This step is of great importance as it controls Mg2+ leaching, one of the carbonation reaction limiting factors. Previous studies have focused on the optimization of the thermal activation by determining the ideal activation temperature. However, to date, none of these studies have considered the impacts of the thermal activation on the efficiency of the aqueous-phase mineral carbonation at ambient temperature and moderate pressure in flue gas conditions. Several residence times and temperatures of activation have been tested to evaluate their impact on serpentine dissolution in conditions similar to mineral carbonation. The mineralogical composition of the treated solids has been studied using X-ray diffraction coupled with a quantification using the Rietveld refinement method. A novel approach in order to quantify the meta-serpentine formed during dehydroxylation is introduced. The most suitable mineral assemblage for carbonation is found to be a mixture of the different amorphous phases identified. This study highlights the importance of the mineralogical assemblage obtained during the dehydroxylation process and its impact on the magnesium availability during dissolution in the carbonation reaction.

1. Introduction

The increasing greenhouse gas emissions and particularly anthropogenic carbon dioxide (CO2) in the atmosphere are known to play a major role in climate change [1]. Mitigation solutions are needed more than ever. Among the methodologies proposed for mitigation, mineral carbonation appears to be one of the most sustainable [2,3]. This natural and spontaneous phenomenon involves the reaction between CO2 (aqueous or gas) and divalent cations bearing minerals in order to form the associate carbonates [3]:
Equation (1)     Carbonation reaction [4]
(Mg, Ca)xSiyOx + 2y + xCO2 = > x(Mg,Ca)CO3 + yCO2
The reaction products are stable and inert solids where CO2 is sequestered. The composition of the resulting carbonates depends on the major cations present in the reactant mineral [5]. Carbonation reaction can be divided in three main steps: (i) the CO2 dissolution in water (ii) the material dissolution and (iii) the precipitation of carbonates as final products. The process is essentially controlled by the first two steps [6]. Serpentine minerals, due to their high amount of Mg2+ [7] are considered for carbonation [8]. Thermal treatment acts on serpentine dissolution by enhancing Mg2+ availability, making it a key step for the process [9]. Serpentine dissolution first results in a rapid exchange of surfacing Mg2+ with protons (H+) before being extracted from the structure into the solution, during a much slower phase [10,11]. The dissociation of CO2 added to the solution will generate protons and HCO3- ions, therefore enhancing Mg2+ availability (Pasquier et al., 2014b).
Lizardite, antigorite, and chrysotile are the main minerals of the serpentine group (Mg3Si2O5(OH)4), belonging to the phyllosilicate class [7,12,13,14]. Serpentine structure is made of stacked layers composed of two sheets: the tetrahedral layer composed of silicon tetrahedral (SiO4), linked to the lateral Mg of the octahedral layer by its apical oxygen atoms, forming a covalent bond [14,15]. Outer hydroxyl groups contribute to Van der Waals interactions between the two layers, whereas inner hydroxyl groups contribute to intrafoliar Van der Waals interactions [15,16,17].
Under high temperatures, hydroxyl groups, linked to Mg atoms, escape the structure. During this dehydroxylation process, serpentine transformed into amorphous phases (between 550 and 750 °C—Equation (2)), and then recrystallized into forsterite (Mg2SiO4 > 750 °C), associated with enstatite (MgSiO3 > 800 °C) as the temperature increased (Equation (3)) [18,19,20]. Two types of amorphous phases have been described [21]: pseudo-amorphous phases, named α-meta-serpentine, appearing at 50% of the total dehydroxylation reaction, and amorphous meta-serpentine, appearing at 90% of the total dehydroxylation. The formation of αmeta-serpentine component can be observed at a temperature close to 580 °C visualized on a diffractogram by a feature in the lower angle domain (2Ɵ = ± 6°) [21].
Equations (2) and (3): Serpentine dihydroxylation
Mg3Si2O5(OH)4 (s) → Mg3Si2O7 (s) + 2H2O (g)
2Mg3Si2O7 (s) + SiO2 (s) → 3Mg2SiO4 (s) + MgSiO3 (s) + SiO2 (s).
It has been observed that amorphous meta serpentine tends to promote Mg2+ leaching and thus carbonation [21,22,23]. Therefore, optimized conditions for carbonations have been prescribed to be between 630 °C and 650 °C for 30 to 120 min [22,24,25]. However, in the previous studies, carbonation reactions have essentially been performed using pure CO2 gas at high temperature and high pressure [21,25,26,27], strong acids or salts to promote dissolution [22,28]. To date no studies have been conducted on optimizing thermal activation from the mineralogical point of view, especially for direct aqueous mineral carbonation using diluted gas. In these conditions, serpentine dissolution is only promoted by carbonic acid at room temperature and low/mild CO2 partial pressure and a good activation is more than ever critical for reaction.
This study is part of the follow-up work on direct flue gas carbonation process initiated by Mercier et al. at INRS, Québec [29]. Using mining residues available in the Province of Québec, the process uses a simulated cement plant flue gas to perform direct flue gas aqueous carbonation [30]. Carbonation reaction parameters have been optimized by Pasquier [31], optimized conditions for the precipitation of carbonates have been determined by Moreno [32] whereas a technical and economical evaluation of the process have shown its feasibility and sustainability in the Province of Québec [33]. However, a pilot scale test revealed that thermal treatment conditions needed to be optimized for the INRS process as well [34,35].
In the present paper, only the proportion of magnesium prior to precipitation will be studied and considered as an intermediate product of the carbonation, as thermal activation can only acts on enhancing serpentine dissolution. Therefore, post-carbonation solids were not considered in the present study for the given reasons. Furthermore, it serves to give a novel approach of evaluating the influence of amorphous phases on serpentine dissolution and thus Mg2+ leaching during direct flue gas aqueous mineral carbonation by introducing a new quantifying method of those phases. Those new mineralogical data will provide a further understanding of the relation between thermal activation and serpentine dissolution and therefore, improve this step in the INRS carbonation process.

2. Materials and Methods

2.1. Sample Preparation, Characterization and Analytical Methods

Serpentinite residues were sampled on stockpiles from Jeffrey Mine, near the town of Asbestos, southern of the Province of Québec. Lizardite is identified to be the major serpentine polymorph [36]. Fibres, representing 20 wt % of the residue, were removed by gravimetric separation based on their buoyancy. Iron oxides were also removed by wet gravimetric separation using the Wifley table, due to their potential commercial value for the process.
The sample was ground using a ring mill (Retsch RS200, Dusseldorf, Germany). The grain size distribution is given in Table 1 Values were obtained and measured using a particle size distribution analyzer (LA-950V2 Horiba, Kyoto, Japan).
The chemical composition of the starting material is given in Table 2. The chemical composition of liquid and solid samples was obtained using inductively coupled plasma-atomic emission spectrometry (ICP-AES) analysis (Varian, Palo Alto, CA, USA). Solid samples were first fused using the Claisse Method [37]. Loss on ignition (LOI) was obtained from mass difference after placing the sample into a ceramic crucible inside a muffle furnace for 6 h at 1025 °C.
Phases were identified using XRPD analysis (Bruker AXS, 2004, Karlsruhe, Germany), performed at the University of British Columbia. To prepare the sample, 1.6 g were mixed with 0.4 g of pure corundum (Al2O3) [38], used as an internal standard, representing a 20.0 wt % spike. Samples were ground in ethanol using agate grinding pellets for seven minutes, in a McCrone micronizing mill to ensure homogenization. Scans were acquired for 30 min with 2Ɵ ranging from 3° to 80° with scanning step size of 2Ɵ = 0.3° with a counting time of 7 s per step, on a Siemens D5000 Bragg-Brentano Ɵ-2Ɵ diffractometer (Bruker AXS, 2004, Karlsruhe, Germany) with radiation CuKα (40kV, 40mA). Matches were obtained using Bruker identification software DIFFRACplus EVA and the ICDD PDF-2 database.
Quantification of phases was performed using the Rietveld method ([39,40,41,42]) based on a calibration factor obtained from the mass and volume of each phase’s unit cell. However, this method requires that all of the phases show high degrees of crystallinity with well-defined crystal structures [42]. Serpentine minerals are known to show discrepancies from their ideal crystal structures [38,43]. Therefore, when the crystalline structure of a phase is unknown or partially known, it can be quantified through the use of the Partial Or No Known Crystalline Structure method (PONKCS), combined with the Rietveld method [44]. A standard sample of pure chrysotile (90.0 wt %) and fluorite (10.0 wt %), provided by The University of British Columbia (Vancouver, British Columbia, Canada)., whose composition is well known [38] was used in order to calibrate the PONKCS model. A calibrated mass value for the unit cell of both phases was acquired by Rietveld refinements and the chrysotile peaks were fitted using the Le Bail method [45]. The unit cell parameters and the space group were extracted from Falini [46]. The generated PONKCS model was then used in the Rietveld refinements as a crystallographic information files in the software TOPAS (Bruker AXS) [44,47].

2.2. Experimental Apparatus and Conditions

2.2.1. Thermal Activation

Heat treatments were performed in a muffle furnace, Furnatrol I33 (Thermolyne Subron Corporation). Twenty grams of samples were placed in a cast-iron skillet in a thin surface, then introduced into the furnace. Cast iron was chosen for its resistance to drastic temperature changes. No major iron contaminations were observed after thermal treatments according to chemical analysis. Tests were performed under isothermal conditions, meaning that the furnace was set to the targeted temperature beforehand to the test. At the end of the treatment, the furnace was open to help the skillet cool down, for five minutes. The skillet and the sample were weighted and the difference between initial and final masses corresponded to the mass lost induced by heat treatment. A series of seven tests were conducted at different residence times and temperatures, as shown in Table 3.

2.2.2. Dissolution in Aqueous Carbonation Conditions

Dissolution reactions were performed using carbonation conditions in order to evaluate thermal treatment effects on the developing process. Carbonation reactions were conducted in a 300 mL stirred reactor, model 4561 of Parr Instrument Company (Moline, IL, USA) [29,31]). The tests were performed using a certified composition gas of 4.0 vol% O2 and 18.2 vol% CO2, balanced with N2, simulating cement plant flue gas. The pulp density was set to 15% (150 g·L−1), with a volume of 75 mL of water, 11.25 g of solid and a gas phase volume of 225 mL, as optimized by Mercier et al. [29]. A batch of 10.2 bar of gas was introduced into the stirred reactor and was allowed to react with the pulp for 15 min at room temperature 22 °C ± 3 °C with the agitation sets to 600 RPM (Figure 1). As the reaction happens, the pressure decreased between 0.1 and 3.5 bar, depending on the amount of gas initially introduced. At the end of each batch, the pulp was filtered to obtain the liquid for chemical composition analyses. The reactivity of the eight thermally treated samples were tested along with an untreated sample (U). They were only observed throughout the proportion of magnesium leached from the solid during the reaction, using Equation (4) [Mg]liq corresponds to the measured concentration of Mg2+ at the end of the reaction, V and m are the volume of the solution and the mass of solid, respectively, and CMg is the measured concentration of Mg in the post-thermal treatment solid. Carbonates were not precipitated from the solution as thermal activation impacts on the Mg leaching. Mg analysis was performed on liquid sample after reaction. The liquid fraction was obtained after filtration of the resulting pulp. Consistency in the procedure was validated by performing mass balance to highlight any precipitation occurring during manipulation or during the pressure release of the vessel.
Equation (4):     Proportion of Mg2+ leached
% M g =   ( [ M g ] l i q × V ) × 100 ( C M g × m ) .
In a successive batches test, the solid was used for 12 batches of gas. Every two batches, the solid was filtered and reused with fresh liquid in the subsequent batches. After six batches, the solid was filtered, dried at 60 °C, and ground for 1 min at 700 RPM in a ring mill, to partially remove the silica layer formed around the grains and then re used for another series of 6 batches as described by Figure 2. The liquid phase was sampled and renewed every two batches to prevent saturation. Long term reactivity of samples D and F treated at 650 °C for 30 min and 750 °C for 15 min, respectively, were tested in a successive batches experiment.

3. Results and Discussion

3.1. Mass Loss

The proportion of mass lost by each sample during thermal treatments has been registered and is presented in Table 4. As expected, the proportion of mass lost during treatment increased with the temperature. It reached a peak at 14.5% for sample F and was treated at 750 °C for 15 min. This value is in agreement with the expected one, between 12.0% and 14.0% [48,49].

3.2. Mineralogical Transformations Along with Activation Temperatures

The evolution in the mineral composition at different temperatures and residence times has been studied using XRPD. Serpentine shows high crystallinity in samples U, A, and B, respectively untreated, treated at 550 °C for 15 min, and treated for 60 min. It then decreases in samples C, D, E, and F, respectively treated at 650 °C for 15 min, 30 min, and 60 min, and at 750 °C for 15 min. Crystalline features disappear in samples F and G, respectively, at 750 °C for 15 and 30 min. Amorphous contents can be identified in all of the treated samples as the crystallinity decreases. Forsterite is observed in samples E, G, and H, shown by highly crystalline peaks.
The remaining magnetite (the small proportion not removed during gravimetric separation) shows peaks in all samples, whereas the hematite (Fe2O3) which appears during the duration and temperature of the test increases. Due to the tests being performed in atmospheric conditions, the iron in the ferrous form (Fe2+) contained in the serpentine structure is oxidized into ferric iron (Fe3+) [50]. As iron rich olivine (fayalite—Fe2SiO4) can essentially incorporate Fe2+ in its structure [51], hematite (Fe2O3) is preferentially formed.
Table 5 presents phases quantification as measured using the Rietveld refinement. Three issues are faced: (i) these values do not consider the mass loss occurring during thermal treatment (ii) amorphous components are identified in the untreated sample, due to the stacking disorder of serpentine, making the identification of thermally induced amorphous components difficult, and finally (iii) a small peak is observed in the low angle that can be attributed to illite thus undermining the observation of the formation of meta-serpentine as described by [21]. Wilson et al. [38] determine that absolute quantification errors (wt %) for serpentine (chrysotile) and non-serpentine phases, regardless of their abundance in a sample, to be under 5.0 wt %. Consequently, illite is not considered in the Rietveld refinement as their peaks are too low and would fall under the estimation limit.
In an attempt to overcome these issues, a mass factor (MF in Equation (5)) is computed based on the mass loss of each sample (Table 4). Using this factor, the abundance of each phase can be expressed as grams per 100 g of starting material as given in Equation (5).
Equation (5):     Proportion of phases expressed in mass
m phase   =   % phase   ×   ( 100 100   +   % mass   loss )   =   % phase   ×   MF .
As dehydroxylation is considered to be the loss of H2O from the structure, the mass of H2O lost per gram of serpentine is computed in order to obtain the proportion of dehydroxylated serpentine (Equation (6)). The value used as maximum mass loss “%mass loss max” was obtained experimentally and found to be 14.2% for this material.
Equation (6):     Proportion of dehydroxylated serpentine
%   dehydroxylated   serpentine   =   % mass   loss ( m amorphous   +   m serpentine ) %   mass   loss max   =   m H 2 O   lost % mass   loss max .
The initial remaining material is decomposed into a non-reacted serpentine (serpentine(i)) associated with a non-reacted amorphous phase (amorphous(i)) induced by the layered structure of the serpentine. Their masses are calculated according to Equation (7), assuming that amorphous phase and crystalline initial serpentine both dehydroxylated in the same proportion.
Equation (7):     Mass of initial phases
m phase ( i )   =   ( m phase )     ( m phase   ×   %   dehydroxylated   serpentine ) .
The amount of dehydroxylated serpentine and amorphous phase corresponding to the first amorphous observed, (respectively named serpentine(d) and amorphous(d)) are given by Equation (8).
Equation (8):     Mass of intermediate amorphous phases
mphase(d) = mphasemphase(i).
Further dehydroxylation leads to the formation of meta-serpentine, whose mass is obtained by Equation (9) This formation is marked by the total loss of the hydroxyls groups at close to 10 wt % of the starting material mass.
Equation (9):     Mass of meta-serpentine
m meta serpentine   =   ( m amorphous   ×   m H 2 O   lost )     m amorphous ( i )   .
As a result, three phases emerge from this calculation: first an initial serpentine, resulting from the sum of amorphous(i) and serpentine(i), then an intermediate amorphous components which is the sum of amorphous(d) and serpentine(d) corresponding to the first stage of amorphization, and finally meta-serpentine. Forsterite and iron oxides (magnetite and hematite) remain unaltered by the calculation.
As shown in Table 6, Serpentine is gradually replaced by intermediate amorphous phases in samples treated at temperatures lower than 650 °C and peaks for 60 min treatment at 70.3 g/100 g of starting material. Meta-serpentine is first found in samples treated at 650 °C for 15 min. Its proportion increases with the temperature and peaks at 27.2 g/100 g of starting material in the sample treated at 750 °C for 15 min. The increase of meta-serpentine is combined with a decrease of intermediate amorphous components contents. As seen previously (Table 5), forsterite is observed in samples E, G and H, respectively treated at 650 °C for 60 min and at 750 °C for 30 and 60 min. A treatment at 750 °C for 15 min produced a sample with no initial serpentine and no forsterite but only amorphous phases, associated with iron oxides. These observations are in agreement with previous studies which observed the formation of an intermediate amorphous component, α meta-serpentine, progressively replacing serpentine below 580 °C. It is then followed by the appearance of an amorphous meta-serpentine material by 650 °C prevailing by 750 °C [21].

3.3. Impact of Mineralogy on Dissolution

3.3.1. Two Batches Dissolution

It is known that the amount of Mg2+ available for leaching will directly control, along with the amount of CO2 treated, the quantity of carbonates being precipitated from the liquid phase after carbonation [30,31]. This study focuses on the proportion of Mg2+ leached from thermally treated serpentine samples. Figure 3 shows the mass of intermediate amorphous components and of meta-serpentine added up and plotted against the proportion of Mg2+ leached into the liquid phase during the carbonation reaction. As the amount of amorphous components increases from none (U- untreated sample) to 77 g/ 100 g of starting material (F—750 °C 15 min), the proportion of Mg2+ leached during two batches of gas increases too, respectively from 3.3 wt % to 13.5 wt % of initial Mg2+ concentration in solid. Samples D, G and H show similar proportions of Mg2+ leached and a close amount of amorphous components. However, initial serpentine constitutes a third of the former composition, whereas forsterite is formed in the two latter. As observed in previous studies at 650 °C, the solubility of Mg2+ ions is first increased by thermal treatment until it is reduced with the decreasing content of amorphous phases and the formation of forsterite. The amount of Mg2+ leached from the heat activated serpentine appears to be linearly dependent on the proportion of amorphous phases.

3.3.2. Successive Batches Dissolution

Thermal treatment conditions of samples D and F (650 °C for 30 min and 750 °C for 15 min) are chosen to be tested on successive batches as they respectively are the recommended conditions in literature [22] and the conditions giving the highest proportion of Mg2+ leached after two batches of gas in our conditions. Figure 4 shows the cumulative proportion of Mg2+ leached after twelve batches of gas. After two batches of gas, the proportion of Mg2+ leached demonstrates a significant discrepancy from the previous results and the present one. Indeed, the sample treated at 650 °C for 30 min shows a similar proportion of Mg2+ leached to the one treated at 750 °C for 15 min. After 4 batches, the sample treated at 750 °C for 15 min is catching up with a proportion of Mg2+ leached higher by 5 wt % compared to the other sample. At the end of the 12 batches, 44.6 wt % of Mg2+ has been leached from the sample treated at 750 °C for 15 min against 32.4 wt % for the one treated at 650 °C for 30 min. For the sample treated at 650 °C for 30 min, the proportions of Mg2+ leached reached a plateau close to 0.5 wt % during the tenth batch, suggesting that almost all of the Mg2+ available in the present dissolution conditions might have been leached. This occurred with at 750 °C after 15 min, which indicates that the plateau has not been reached yet, suggesting that more batches of CO2 could allow a higher proportion of Mg2+ leached. As the solution is refreshed for every two batches of gas, the limiting factor is the availability of the Mg2+ and not the saturation of the solution.
The increase in the slope of the curves between the batches 6 and 8 demonstrate the slight effect of the grinding on the material after the batch 6. Pasquier et al. [30] demonstrated that the effect of the passivation silica layer, formed during dissolution, can be reduced by grinding and so revive the leaching of Mg2+. Nevertheless, studies from the Carmex project [52,53]) show that a continuous mechanical exfoliation of the passivation layer as it forms on the grains would be a promising way to avoid the need for regrinding after six batches of gas.

3.4. Mineralogical Assemblage and Carbonation

As the hydroxyl groups escape the serpentine octahedral sheets, the remaining atoms of Mg and Si are reorganized through the amorphous components. As the temperature increases, serpentine is transformed into amorphous phases, then recrystallizes into forsterite.
The best mineralogical assemblage is shown to be a mixture of amorphous phases, as observed in sample F with the highest proportion of Mg2+ leached after both two batches and successive batches carbonation tests. McKelvy et al. [21] observed significantly higher carbonation reaction rates in the presence of amorphous meta-serpentine, formed above 610 °C, than in the presence of α-meta-serpentine formed below 580 °C and identified as intermediate amorphous components here. When structurally stable Mg-bearing phases are present in the assemblage, such as serpentine or forsterite, material reactivity decreases. In serpentine, Mg atoms are bonded to the hydroxyls groups whereas in forsterite, they are ionically bonded to silica tetrahedron [54]. The differentiation of the two amorphous phases based on the proposed calculation in this paper were revealed to be accurate because the sample showing the highest value of metaserpentine appeared to be the one demonstrating the highest proportion of Mg2+ leached, in accordance with observations proposed in the literature.
Moreover, reactivity appears to be affected more by mineralogy than by surface area. Larachi et al. [15] provide surface area measurements on calcined samples, from 300 °C to 1200 °C, showing that it tends to decrease with increasing temperature as dehydroxylation occurs.
Furthermore, observations made here are in accordance to those made by other authors regarding the mineralogical transformations occurring during thermal activation and dehydroxylation [21,22]. Nevertheless, a shift of ideal temperature is observed, as observations made by others suggest that reactions at 650 °C were more likely to occur, rather than at 750 °C as occurred in the present study. Such a change can be attributed to numerous factors such as the initial material mineralogy, the experimental set up, and the methodology used to evaluate activation efficiency. For instance, Li et al., [22] used hydrochloric acid to perform lixiviation tests, which is far from neutral pH and weak acid conditions used in the present study. On the other hand, McKelvy et al.’s [21] work set the basis of serpentine dehydroxilation understanding using TGA/DTA and XRD. Conversely, their carbonation conditions used high temperature and supercritical CO2, which is again far from the conditions tested here. Based on their results, past ideal activation conditions were shown to be effective, but not necessarily optimal. Therefore, the present results highlight the importance of considering the mineralogical assemblage alongside the thermal treatment parameters (temperature and residence time). Such an approach will allow us to take into account the effect of the initial material composition and potential specificity of the activation conditions/technique. Indeed, conditions in a rotary kiln will be very different from a furnace or a fluidized bed. As results, a study of the mineralogical assemblage can lead to an accurate optimization of heat activation operating conditions in accordance with the material activated and the equipment used.

4. Conclusions

In this study, a novel approach of amorphous phase quantification, resulting from serpentine thermal activation, is introduced. It enables a better understanding of their implications in serpentine dissolution using carbonic acid as a lixiviant, in similar conditions to those used in the direct flue gas mineral carbonation process developed at INRS. The following conclusions can be made from this study:
(i)
It is possible to differentiate and quantify intermediate amorphous phases and metaserpentine formed during dehydroxylation of serpentine and correlate these values to the efficiency of carbonation reaction. In a static furnace, treatment at 750 °C for 15 min leads to the formation of 27.2 g/100 g of starting material of meta-serpentine.
(ii)
Thermally produced amorphous phases enhance Mg2+ solubility during carbonation reaction. Furthermore, the formation of meta-serpentine, resulting in a complete dehydroxylation, significantly upgrades Mg2+ leaching yield.
(iii)
The crystallization of forsterite decreases the sample dissolution potential by limiting the amount of Mg2+ accessible for leaching in the present dissolution conditions.
(iv)
Adjusting thermal activations parameters (temperature and residence time) led to an increase of 39% of Mg2+ leached during the carbonation reaction.

Author Contributions

Methodology, C.D.B., L.C.-P., G.D., J.-F.B., M.C.I., G.M.; formal analysis, C.D.B.; writing—original draft preparation, C.D.B., L.C.-P., G.D., J.-F.B., M.C.I. and G.M.; writing—review and editing, C.D.B., L.C.-P.; supervision, L.C.-P., G.D., J.-F.B., M.C.I. and G.M.; project administration, G.M.; funding acquisition, L.C.-P., G.D., J.-F.B., M.C.I. and G.M.

Funding

This research was funded by Fond de Recherche Quebecois en Nature et Technology, projet de recherche en équipe 2015–2016.

Acknowledgments

This research was funded by ‘projet de recherche en équipe’ grant from FRQNT. The authors would like to thank Matti Raudsepp. Kate Carroll. Ian Power from the University of British Columbia (Vancouver. Canada) and Connor Turvey from Monash University (Melbourne. Australia) for their advice and help on the XRD and Rietveld refinement application to the serpentine minerals.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. IPCC. Climate Change 2014: Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change; Core Writing Team, Pachauri, R.K., Meyer, L.A., Eds.; IPCC: Geneva, Switzerland, 2014; p. 151. [Google Scholar]
  2. Lackner, K.S.; Wendt, C.H.; Butt, D.P.; Joyce, B.L.; Sharp, D.H. Carbon dioxide disposal in carbonate minerals. Energy 1995, 20, 1153–1170. [Google Scholar] [CrossRef]
  3. Seifritz, W. CO2 disposal by means of silicates. Nature 1990, 345, 486. [Google Scholar] [CrossRef]
  4. Maroto-Valer, M.M.; Fauth, D.J.; Kuchta, M.E.; Zhang, Y.; Andrésen, J.M. Activation of magnesium rich minerals as carbonation feedstock materials for CO2 sequestration. Fuel Process. Technol. 2005, 86, 1627–1645. [Google Scholar] [CrossRef]
  5. Hänchen, M.; Prigiobbe, V.; Baciocchi, R.; Mazzotti, M. Precipitation in the Mg-carbonate system: Effects of temperature and CO2 pressure. Chem. Eng. Sci. 2008, 63, 1012–1028. [Google Scholar] [CrossRef]
  6. Harrison, A.L.; Power, I.M.; Dipple, G.M. Accelerated carbonation of brucite in mine tailings for carbon sequestration. Environ. Sci. Technol. 2012, 47, 126–134. [Google Scholar] [CrossRef]
  7. Page, N.J. Chemical differences among the serpentine polymorphs. Am. Mineral. 1968, 53, 201–215. [Google Scholar]
  8. Goff, F.; Guthrie, G.D.; Lipin, B.; Fite, M.; Chipera, S.; Counce, D.A.; Kluk, E.; Ziock, H. Evaluation of Ultramafic Deposits in the Eastern United States and Puerto Rico as Sources of Magnesium for Carbon Sequestration; Los Alamos National Laboratory: Los Alamos, NM, USA, 2000; p. 30. [Google Scholar]
  9. Nagamori, M.; Plumpton, A.J.; Le Houillier, R. Activation of magnesia in serpentine by calcination and the chemical utilization of asbestos tailings, A review. C. Bull. 1980, 73, 144–156. [Google Scholar]
  10. Luce, R.W.; Bartlett, R.W.; Parks, G.A. Dissolution kinetics of magnesium silicates. Geochim. Cosmochim. Acta 1972, 36, 35–50. [Google Scholar] [CrossRef]
  11. Stumm, W.; Morgan, J.J. Aquatic Chemistry: An Introduction Emphasizing Chemical Equilibria in Natural Waters; John Wiley and Sons: Hoboken, NJ, USA, 1981. [Google Scholar]
  12. Aruja, E. An X-ray study of crystal-structure of antigorite. Mineral. Mag. 1994, 27, 11. [Google Scholar]
  13. Nagy, B.; Faust, G. Serpentines: Natural mixtures of Chrysotile and antigorite. Am. Mineral. 1956, 41, 817–838. [Google Scholar]
  14. Wicks, F.J.; Whittaker, E.J.W. Serpentine textures and serpentinization. Can. Mineral. 1977, 15, 459–488. [Google Scholar]
  15. Larachi, F.; Daldoul, I.; Beaudoin, G. Fixation of CO2 by chrysotile in low-pressure dry and moist carbonation: Ex-situ and in-situ characterizations. Geochim. Cosmochim. Acta 2010, 74, 3051–3075. [Google Scholar] [CrossRef]
  16. Mellini, M.; Zanazzi, P.F. Crystal structures of lizardite-1T and lizardite-2H1 from Coli, Italy. Am. Mineral. 1987, 72, 943–948. [Google Scholar]
  17. Turci, F.; Tomatis, M.; Mantegna, S.; Cravotto, G.; Fubini, B. A new approach to the decontamination of asbestos-polluted waters by treatment with oxalic acid under power ultrasound. Ultrason. Sonochem. 2008, 15, 420–427. [Google Scholar] [CrossRef] [PubMed]
  18. Ball, M.C.; Taylor, H.F.W. The dehydration of chrysotile in air and under hydrothermal conditions. Mineral. Mag. 1963, 33, 467–482. [Google Scholar] [CrossRef]
  19. Brindley, G.W.; Hayami, R. Mechanism of formation of forsterite and enstatite from serpentine. Mineral. Mag. 1965, 35, 189–195. [Google Scholar] [CrossRef]
  20. Brindley, G.W.; Hayami, R. Kinetics and mecanisms of dehydration and recrystallization of serpentine. Clays Clay Miner. 1965, 12, 35–37. [Google Scholar] [CrossRef]
  21. McKelvy, M.J.; Chizmeshya, A.V.; Diefenbacher, J.; Béarat, H.; Wolf, G. Exploration of the role of heat activation in enhancing serpentine carbon sequestration reactions. Environ. Sci. Technol. 2004, 38, 6897–6903. [Google Scholar] [CrossRef]
  22. Li, W.; Li, W.; Li, B.; Bai, Z. Electrolysis and heat pretreatment methods to promote CO2 sequestration by mineral carbonation. Chem. Eng. Res. Des. 2009, 87, 210–215. [Google Scholar] [CrossRef]
  23. Farhang, F.; Rayson, M.; Brent, G.; Hodgins, T.; Stockenhuber, M.; Kennedy, E. Insights into the dissolution kinetics of thermally activated serpentine for CO2 sequestration. Chem. Eng. J. 2017, 330, 1174–1186. [Google Scholar] [CrossRef]
  24. Gerdemann, S.J.; O’Connor, W.K.; Dahlin, D.C.; Penner, L.R.; Rush, H. Ex situ aqueous mineral carbonation. Environ. Sci. Technol. 2007, 41, 2587–2593. [Google Scholar] [CrossRef] [PubMed]
  25. O’Connor, W.K.; Dahlin, D.C.; Rush, G.E.; Gedermann, S.J.; Penner, L.R.; Nilsen, D.N. Aqueous Mineral Carbonation; Final Report DOE/ARC-TR-04-002. 2005, p. 462. Available online: https://www.researchgate.net/profile/William_Oconnor8/publication/315844800_Aqueous_Mineral_Carbonation_Mineral_Availability_Pretreatment_Reaction_Parametrics_and_Process_Studies/links/58ebb247a6fdcc965767765f/Aqueous-Mineral-Carbonation-Mineral-Availability-Pretreatment-Reaction-Parametrics-and-Process-Studies.pdf (accessed on 3 November 2019).
  26. Gerdemann, S.J.; Dahlin, D.C.; O’Connor, W.K.; Penner, L.R. Carbon dioxide sequestration by aqueous mineral carbonation of magnesium silicate minerals. In Greenhouse gas Technologies; Albany Research Center (ARC): Albany, OR, USA, 2003; p. 8. [Google Scholar]
  27. Mann, J. Serpentine Activation for CO2 Sequestration. Ph.D. Thesis, University of Sydney, Sydney, Australia, 2014; p. 274. [Google Scholar]
  28. Sanna, A.; Wang, X.; Lacinska, A.; Styles, M.; Paulson, T.; Maroto-Valer, M.M. Enhancing Mg extraction from lizardite-rich serpentine for CO2 mineral sequestration. Miner. Eng. 2013, 49, 135–144. [Google Scholar] [CrossRef]
  29. Mercier, G.; Blais, J.-F.; Cecchi, E.; Veetil, S.P.; Pasquier, L.-C.; Kentish, S. Carbon Dioxide Chemical Sequestration from Industrial Emissions by Carbonation. U.S. Patent 9.440,189 B2, 13 September 2016. [Google Scholar]
  30. Pasquier, L.-C.; Mercier, G.; Blais, J.F.; Cecchi, E.; Kentish, S. Reaction mechanism for the aqueous-phase mineral carbonation of heat-activated serpentine at low temperatures and pressures in flue gas conditions. Environ. Sci. Technol. 2014, 48, 5163–5170. [Google Scholar] [CrossRef] [PubMed]
  31. Pasquier, L.-C.; Mercier, G.; Blais, J.F.; Cecchi, E.; Kentish, S. Parameters optimization for direct flue gas CO2 capture and sequestration by aqueous mineral carbonation using activated serpentinite based mining residues. Appl. Geochem. 2014, 50, 66–73. [Google Scholar] [CrossRef]
  32. Moreno Correia, M.J. Optimisation de la Précipitation des Carbonates de Magnésium pour L’application dans un Procédé de Séquestration de CO2 par Carbonatation Minérale de la Serpentine. Master’s Thesis, Université du Québec, Québec, QC, Canada, 2018; p. 125. [Google Scholar]
  33. Pasquier, L.-C.; Mercier, G.; Blais, J.-F.; Cecchi, E.; Kentish, S. 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. Int. J. Greenh. Gas Control 2016, 50, 147–157. [Google Scholar] [CrossRef]
  34. Kemache, N.; Pasquier, L.-C.; Cecchi, E.; Mouedhen, I.; Blais, J.-F.; Mercier, G. Aqueous mineral carbonation for CO2 sequestration: From laboratory to pilot scale. Fuel Process. Technol. 2017, 166, 209–216. [Google Scholar] [CrossRef]
  35. Kemache, N.; Pasquier, L.-C.; Mouedhen, I.; Cecchi, E.; Blais, J.-F.; Mercier, G. Aqueous mineral carbonation of serpentinite on a pilot scale: The effect of liquid recirculation on CO2 sequestration and carbonate precipitation. Appl. Geochem. 2016, 67, 21–29. [Google Scholar] [CrossRef]
  36. Aumento, F. Serpentine Mineralogy of Ultrabasic Intrusion in Canada and on the Mid-Atlantic Ridge; Department of Energy, Mines and Resources: Ottawa, ON, Canada, 1970. [Google Scholar]
  37. Tertian, R.; Claisse, F. Principles of Quantitative X-ray Fluorescence Analysis; Wiley-Heyden: London, UK, 1982. [Google Scholar]
  38. Wilson, S.A.; Raudsepp, M.; Dipple, G.M. Verifying and quantifying carbon fixation in minerals from serpentine-rich mine tailings using the Rietveld method with X-ray powder diffraction data. Am. Mineral. 2006, 91, 1331–1341. [Google Scholar] [CrossRef]
  39. Bish, D.L.; Howard, S. Quantitative phase analysis using the Rietveld method. J. Appl. Crystallogr. 1988, 21, 86–91. [Google Scholar] [CrossRef]
  40. Pawley, G.S. Unit-Cell Refinement from Powder Diffraction scans. J. Appl. Crystallogr. 1981, 14, 357–361. [Google Scholar] [CrossRef]
  41. Raudsepp, M.; Pani, E.; Dipple, G. Measuring mineral abundance in skarn; I, The Rietveld method using X-ray powder-diffraction data. Can. Mineral. 1999, 37, 1–15. [Google Scholar]
  42. Rietveld, H.M. A Profile Refinement Method for Nuclear and Magnetic Structures. J. Appl. Crystallogr. 1969, 2, 65–71. [Google Scholar] [CrossRef]
  43. Turvey, C.C.; Wilson, S.A.; Hamilton, J.L.; Southam, G. Field-based accounting of CO2 sequestration in ultramafic mine wastes using portable X-ray diffraction. Am. Mineral. 2017, 102, 1302–1310. [Google Scholar] [CrossRef]
  44. Scarlett, N.V.Y.; Madsen, I.C. Quantification of phases with partial or no known crystal structures. Powder Diffr. 2006, 21, 278–284. [Google Scholar] [CrossRef]
  45. Le Bail, A. Whole powder pattern decomposition methods and applications: A retrospection. Powder Diffr. 2005, 20, 316–326. [Google Scholar] [CrossRef] [Green Version]
  46. Falini, G.; Foresti, E.; Gazzano, M.; Gualtieri, A.F.; Leoni, M.; Lesci, I.G.; Roveri, N. Tubular-Shaped Stoichiometric Chrysotile Nanocrystals. Chem. A Eur. J. 2004, 10, 3043–3049. [Google Scholar] [CrossRef]
  47. Du Breuil, C.; Pasquier, L.C.; Dipple, G.; Blais, J.F.; Iliuta, M.C.; Mercier, G. Impact of particle size in serpentine thermal treatment: Implications for serpentine dissolution in aqueous-phase using CO2 in flue gas conditions. Appl. Clay Sci. 2019, 182, 105286. [Google Scholar] [CrossRef]
  48. Jolicoeur, C.; Duchenes, D. Infrared and thermogravimetric studies of the thermal degradation of chrysotile asbsestos fibers: Evidence for matrix effects. Can. J. Chem. 1981, 59, 1521–1526. [Google Scholar] [CrossRef]
  49. Viti, C. Serpentine minerals discrimination by thermal analysis. Am. Mineral. 2010, 95, 631–638. [Google Scholar] [CrossRef]
  50. Balucan, R.D.; Dlugogorski, B.Z. Thermal activation of antigorite for mineralization of CO2. Environ. Sci. Technol. 2013, 47, 182–190. [Google Scholar] [CrossRef]
  51. Hora, Z. Ultramafic hosted chrysotile asbestos. In Fieldwork; British Columbia Geological Survey: Victoria, BC, Canada, 1997; p. 4. [Google Scholar]
  52. Bodénan, F.; Bourgeois, F.; Petiot, C.; Augé, T.; Bonfils, B.; Julcour-Lebigue, C.; Guyot, F.; Boukary, A.; Tremosa, J.; Lassin, A.; et al. Ex situ mineral carbonation for CO2 mitigation: Evaluation of mining waste resources, aqueous carbonation processability and life cycle assessment (Carmex project). Miner. Eng. 2014, 59, 52–63. [Google Scholar] [CrossRef]
  53. Julcour, C.; Bourgeois, F.; Bonfils, B.; Benhamed, I.; Guyot, F.; Bodénan, F.; Petiot, C.; Gaucher, É.C. Development of an attrition-leaching hybrid process for direct aqueous mineral carbonation. Chem. Eng. J. 2015, 262, 716–726. [Google Scholar] [CrossRef] [Green Version]
  54. Birle, J.; Gibbs, G.; Moore, P.; Smith, J. Crystal structures of natural olivines. Am. Mineral. 1968, 53, 807. [Google Scholar]
Figure 1. Parr reactor experimental set up.
Figure 1. Parr reactor experimental set up.
Minerals 09 00680 g001
Figure 2. Batches dissolution experiments.
Figure 2. Batches dissolution experiments.
Minerals 09 00680 g002
Figure 3. Extracted plotted against the quantity of amorphous phases, being the sum of the intermediate amorphous components and meta-serpentine. (Squares, triangle, and circles stands for test temperature of 550 °C, 650 °C, and 750 °C, respectively).
Figure 3. Extracted plotted against the quantity of amorphous phases, being the sum of the intermediate amorphous components and meta-serpentine. (Squares, triangle, and circles stands for test temperature of 550 °C, 650 °C, and 750 °C, respectively).
Minerals 09 00680 g003
Figure 4. The Mg2+ leached (expressed in percent of initial Mg2+ concentration in the solid) for samples treated at 650 °C for 30 min (blue) and at 750 °C for 15 min (green).
Figure 4. The Mg2+ leached (expressed in percent of initial Mg2+ concentration in the solid) for samples treated at 650 °C for 30 min (blue) and at 750 °C for 15 min (green).
Minerals 09 00680 g004
Table 1. Size distribution of the sample.
Table 1. Size distribution of the sample.
Mean Size (µm)d90d50d10
16.001.998.1643.28
Table 2. Composition of the raw solid feedstock 1.
Table 2. Composition of the raw solid feedstock 1.
ElementsValues (wt %)
CaO0.7
Cr2O30.2
Fe2O36.8
K2O0.2
MgO41.0
MnO0.1
NiO0.3
SiO239.9
LOI10.8
1 Major compounds only.
Table 3. Treatment conditions.
Table 3. Treatment conditions.
Residence Time (min)Temperature (°C)
550650750
15ACF
30-DG
60BEH
Table 4. Mass lost during each thermal treatment, expressed as percent of initial mass of sample.
Table 4. Mass lost during each thermal treatment, expressed as percent of initial mass of sample.
Temperature (°C)550650750LOI
Residence Time (min)1560153060153060
Sample NameABCDEFGH
% Mass Lost5.55.55.09.912.514.213.111.710.8
Table 5. Mineral composition using Rietveld refinements on XRD patterns, given in wt %.
Table 5. Mineral composition using Rietveld refinements on XRD patterns, given in wt %.
AmorphousSerpentineForsteriteMagnetiteHematite
UntreatedU39.655.80.04.40.0
550 °CA (15 min)40.454.90.04.10.4
B (60 min)39.256.30.03.50.8
650 °CC (15 min)44.550.80.03.60.9
D (30 min)43.551.60.03.41.3
E (60 min)46.946.32.42.41.8
750 °CF (15 min)70.119.80.06.04.1
G (30 min)67.90.028.50.03.6
H (60 min)61.80.034.60.03.7
Table 6. Mineralogical compositions based on Rietveld refinements, expressed in grams per 100 g of starting material) at given temperature and residence times. In. Serp: Initial serpentine, Inter. Am.: Intermediate amorphous components, Meta-serp.: Meta-serpentine, For.: forsterite, Mag: magnetite, Hem: hematite and ML: Mass loss.
Table 6. Mineralogical compositions based on Rietveld refinements, expressed in grams per 100 g of starting material) at given temperature and residence times. In. Serp: Initial serpentine, Inter. Am.: Intermediate amorphous components, Meta-serp.: Meta-serpentine, For.: forsterite, Mag: magnetite, Hem: hematite and ML: Mass loss.
In. Serp.Inter. Am. Meta-Serp.For.Mag.Hem.ML
UntreatedU95.60.00.00.04.40.00.0
550 °CA (15 min)52.836.50.00.03.90.45.5
B (60 min)53.537.00.00.03.30.85.5
650 °CC (15 min)54.031.94.80.03.40.95.0
D (30 min)21.660.34.00.03.01.29.8
E (60 min)4.270.37.22.12.11.612.5
750 °CF (15 min)0.049.927.20.05.23.514.2
G (30 min)0.033.625.524.80.03.113.1
H (60 min)0.034.320.330.50.03.211.7

Share and Cite

MDPI and ACS Style

Du Breuil, C.; César-Pasquier, L.; Dipple, G.; Blais, J.-F.; Iliuta, M.C.; Mercier, G. Mineralogical Transformations of Heated Serpentine and Their Impact on Dissolution during Aqueous-Phase Mineral Carbonation Reaction in Flue Gas Conditions. Minerals 2019, 9, 680. https://doi.org/10.3390/min9110680

AMA Style

Du Breuil C, César-Pasquier L, Dipple G, Blais J-F, Iliuta MC, Mercier G. Mineralogical Transformations of Heated Serpentine and Their Impact on Dissolution during Aqueous-Phase Mineral Carbonation Reaction in Flue Gas Conditions. Minerals. 2019; 9(11):680. https://doi.org/10.3390/min9110680

Chicago/Turabian Style

Du Breuil, Clémence, Louis César-Pasquier, Gregory Dipple, Jean-François Blais, Maria Cornelia Iliuta, and Guy Mercier. 2019. "Mineralogical Transformations of Heated Serpentine and Their Impact on Dissolution during Aqueous-Phase Mineral Carbonation Reaction in Flue Gas Conditions" Minerals 9, no. 11: 680. https://doi.org/10.3390/min9110680

APA Style

Du Breuil, C., César-Pasquier, L., Dipple, G., Blais, J. -F., Iliuta, M. C., & Mercier, G. (2019). Mineralogical Transformations of Heated Serpentine and Their Impact on Dissolution during Aqueous-Phase Mineral Carbonation Reaction in Flue Gas Conditions. Minerals, 9(11), 680. https://doi.org/10.3390/min9110680

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop