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High-Capacity Li4SiO4-based CO2 Sorbents via a Facile Hydration-NaCl Doping Technique Ke Wang, Wei Li, Zeguang Yin, Zhongyun Zhou, and Pengfei Zhao Energy Fuels, Just Accepted Manuscript • Publication Date (Web): 20 May 2017 Downloaded from http://pubs.acs.org on May 20, 2017
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Energy & Fuels
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High-Capacity Li4SiO4-based CO2 Sorbents via a Facile Hydration-NaCl Doping
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Technique
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Ke Wang, Wei Li, Zeguang Yin, Zhongyun Zhou, Pengfei Zhao*
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School of Electrical and Power Engineering, China University of Mining and
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Technology, Xuzhou 221116, China
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Corresponding author:
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Dr. Pengfei Zhao
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School of Electrical and Power Engineering
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China University of Mining and Technology
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Xuzhou 221116, China
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Fax: 86-516-83592000
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E-mail:
[email protected] 13
Abstract: A sodium chloride (NaCl) doping-hydration technique was used to modify
14
the structure of Li4SiO4 to improve its sorption properties at low CO2 concentration.
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XRD, nitrogen adsorption, SEM, XPS, differential scanning calorimetry (DSC), and
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thermogravimetric analyses were conducted to characterize the compositions, textural
17
characteristics, morphologies, chemical valence states, molten phases and adsorption
18
properties of the synthesized samples. Hydration and NaCl doping produced
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synergistic effects. On one hand, a small particle size and large specific surface area
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were obtained, significantly facilitating chemisorption processes. On the other hand,
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co-doped sodium and chlorine induced molten phases when absorbing CO2,
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noticeably decreasing CO2 diffusion resistance. Thus, the CO2 absorption rate and 1
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uptake were remarkably improved. Different amounts of NaCl also greatly affected
2
the morphology and chemisorption properties of the sorbents. At the optimized NaCl
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concentration, the sorbent only required 3 wt.% doping to attain a maximum sorption
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capacity of up to 34.2 wt.%. Moreover, the high capacity was maintained after 10
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sorption/desorption cycles.
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1. Introduction
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The increased anthropogenic emission of greenhouse gases, such as CO2, mainly
8
from fossil fuel combustion, is one of the major contributors to global warming.1-3
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CO2 capture and sequestration (CCS) technologies provide effective and practical
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solutions for nations who wish to both continue to consume fossil fuels and obtain
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ambitious emission targets.4-7 However, current CCS technology using aqueous
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amines has a large energy penalty.8 To address this problem, the removal of CO2 at
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high temperatures utilizes calcium-based materials,9-15 and ceramic absorbents
14
can separate CO2 directly from hot flue gases and the sorption-enhanced steam
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methane reforming (SESMR) process, thereby eliminating the cooling process and
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significantly decreasing the operating costs. Among these candidate materials, lithium
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orthosilicate (Li4SiO4) has been recognized as one of the most attractive sorbents for
18
its relatively large absorption capacity and reasonable durability.20-24
16-19
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Common Li4SiO4 sorbents produced via solid-state reaction have very low
20
surface areas.25, 26 Due to the limited gas-solid contact, slow kinetics are presented.
21
Several superior synthetic methods, such as ball milling 27, impregnated precipitation
22
28-30
, sol–gel,
31-33
carbon coating
34, 35
and hydration,36 were proposed to increase the 2
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specific surface area of sorbents. Modified Li4SiO4 particles with larger surface areas
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and smaller particle sizes attainted higher carbonation conversions (>90%) at 100%
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CO2/700 °C compared to that of raw Li4SiO4. Unfortunately, under a realistic CO2
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concentration of 15 vol.%, only half of the sorbents participate in CO2 uptake even
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over long time periods (~120 min).34 Therefore, it is highly important to further
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enhance the performance of Li4SiO4 at low CO2 partial pressure.
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Based on the double-shell model,37 due to a dense and solid product layer (a
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mixture of Li2CO3 and Li2SiO3) surrounding the unreacted core of Li4SiO4, the
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absorption shifts from the rapid chemisorption controlled regime to the slow CO2
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diffusion-controlled regime.38 Inferior CO2 absorption properties were thus obtained
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within a given residence time in the reactor. Compared with a pure CO2 atmosphere,
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the CO2 diffusion resistance at low CO2 partial pressure (i.e., flue gases is only 15
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vol.%) was increased, considering the absorption temperature was decreased to
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500-600 °C under a CO2 concentration of 15 vol.%.39,
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doping alkali carbonates (Na2CO3 and K2CO3) into Li4SiO4 ceramics can significantly
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reduce the diffusion resistance, thereby facilitating the removal of CO2. Zhang et al. 41
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mixed K2CO3 with Li4SiO4 through a solid-state reaction route. The large and dense
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K2CO3-doped Li4SiO4 particles show only a slightly improved absorption conversion
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of 58% at 15 vol.% CO2. Seggiani et al.
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mixtures to promote Li4SiO4. The addition of 30 wt.% Na2CO3 showed a noticeably
21
improved absorption conversion of 80%. Later, several reports proved that extremely
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high sorption properties can be further achieved by controlling the morphology of the
42
40
It has been proven that
developed binary and ternary carbonate
3
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Li4SiO4 precursor using synthetic routes. Yang et al. 43 introduced the organic lithium
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impregnated suspension method to tailor Na2CO3-doped Li4SiO4 particles with
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relatively smaller and larger surface areas. Under 15 vol.% CO2, 10 wt.%
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Na2CO3-doped sorbents present a 90% absorption conversion. Subha et al.44 also
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reported the high capacity (90% absorption conversion) of alkali carbonate-doped
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Li4SiO4 nanorods made through a microwave sol–gel process. However, both
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synthetic methods clearly suffer from expensive reagents or time-consuming steps.
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We prepared a highly effective Li4SiO4 sorbent via a new NaCl doping and
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hydration procedure. On one hand, the steam was used in the most of hydration
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method.45, 46 Recently, we have developed the water-based hydration to significantly
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improve the sorption capacity of Li4SiO4.36 On the other hand, Na2CO3 and K2CO3
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are widely used in the synthesis of alkali-doped Li4SiO4 sorbents. This is the first time
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that NaCl has been used as doping source. Moreover, the structure of NaCl-doped
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sorbents was different from the cases of alkali carbonate-doped Li4SiO4. In
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comparison to organic lithium impregnated suspension and microwave sol–gel, four
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features are apparent. 1) Our approach is simple and cost effective. This method
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involved one wet impregnation doping step. Moreover, NaCl is abundant and
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inexpensive. 2) This synthetic procedure is an absolutely “green” procedure. Only
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non-toxic NaCl solutions were used. 3) Our sorbents require only 3 wt.% NaCl
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doping to reach a maximum absorption capacity of up to 34.2 wt.% (~96% absorption
21
conversion). 4) NaCl-water solutions are the main component of sea water, which
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would benefit scalable applications. 4
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2. Experimental
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2.1. Sorbents
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All synthetic raw materials were of analytical grade (from Aladdin Chemical
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Reagent Co., Ltd.). Pure Lithium silicate (Li4SiO4) sorbents were synthesized by a
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high-temperature solid-state reaction. For the preparation process, 4.7 g of lithium
6
nitrate (LiNO3) and 1.0 g of fumed silica (SiO2) were accurately weighed. After
7
sufficient mixing, the mixture was calcined at 800 °C for 4 h. The resulting powder
8
was called SS. Samples were prepared by a NaCl doping-hydration method as follows:
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1 g of SS and 0.01~0.05 g of sodium chloride (NaCl) were placed in 200 ml of
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deionized water. The mixture was stirred for 2 h at 80 °C and dried in a drier at
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105 °C. Finally, the obtained powder was calcined again at 800 °C for 2 h. For
12
comparison, HC (via a water hydration-calcination method) sorbents were synthesized
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by a similar method but without adding NaCl.
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NaCl-doped Li4SiO4 absorbents were also synthesized using the traditional
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solid-state reaction method. 4.7 g of LiNO3, 1.0 g of SiO2 and 0.03 g of NaCl were
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accurately weighed and mixed, and then calcined at 800 °C for 4 h, and the resulting
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sorbent was named SS-3Na.
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All samples were named according to the following rules: the first half referred
19
to the preparation method (HC: hydration-calcination method and SS: solid-state
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method) and the second half designated the mass ratio of NaCl/Li4SiO4. If the second
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half is absent, the sample had no NaCl doping. For example, HC-3Na indicates that
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the modified Li4SiO4 powders were synthesized by the hydration-calcination method 5
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with 3 wt.% NaCl addition.
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2.2 Characterization Methods
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X-ray diffraction (XRD) was utilized to detect the phase composition of the
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sorbents using a Bruker Model D8 Advance X-ray diffractometer. Scanning electron
5
microscopy (SEM) was performed to observe the morphology of these samples using
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a Hitachi S-4800 field-emission microscope. N2 adsorption/desorption isotherms were
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employed to analyze the specific BET surface area and BJH pore-size distribution
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using a TriStar 3020 volumetric adsorption analyzer. The chemical valence states on
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the surfaces of the samples were investigated using X-ray photoelectron spectroscopy
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(XPS, Perkin-Elmer, PHI 5600). The data were calibrated using the adventitious C 1s
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peak with a fixed value of 284.6 eV and analyzed using XPSPEAK41 processing
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software. DSC analysis was performed in a Labsys Evo simultaneous thermal
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thermogravimetric analyzer; the samples were dynamically heated from room
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temperature to 1000 °C at a rate of 10 °C/min under a CO2 atmosphere with a flow
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rate of 50 mL/min.
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CO2 absorption properties were measured by a ZRY-1P thermogravimetric
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analyzer (Techcomp Jingke Scientific Instrument Co., Ltd., Shanghai, China). A series
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of sorbents was heat-treated from room temperature to 800 °C at a rate of 10 °C/min,
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and the whole process was carried out under 15 vol.% CO2 in N2 (50 ml/min).
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Additionally, the isothermal absorption properties were determined. The samples were
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heated to a specified temperature under N2 atmosphere (50 ml/min), then the gas line
22
was immediately switched to 15 vol.% CO2 in N2 (50 ml/min), and the sample 6
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maintained at the specified temperature for 120 min. For evaluating the cyclic
2
absorption properties, 10 absorption/desorption cycles were performed as follows:
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CO2 absorption at 575 °C in a 50 ml/min CO2-N2 mixture containing 15 vol.% CO2
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for 40 min and CO2 desorption at 700 °C in 50 ml/min pure N2 for 10 min.
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3. Results and discussion
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3.1. Different modified methods
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After Li4SiO4 samples were synthesized using different methods, the samples
8
were characterized by XRD. As shown in Figure 1, the XRD peaks of SS and HC
9
were identified as Li4SiO4 crystalline phase, and no any second phase appeared. In
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addition to the crystalline phase of Li4SiO4, the characteristic peaks of NaCl were
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observed in both SS-3Na and HC-3Na. It seemed that the doping limit is less than 3
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wt.%, which was confirmed by XRD and XPS results in the following section.
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Furthermore, the diffraction peaks of HC and HC-3Na became much broader than
14
those observed in the samples synthesized by solid-state reaction.
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The microstructural properties of samples obtained by different methods were
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observed by SEM. As illustrated in Figure 2, the morphology of SS and SS-3Na
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samples were relatively dense and large particles (~30 µm), which are consistent with
18
those produced in the solid state reaction. Although there are still some sintered
19
particles in the HC and HC-3Na sample, the size of most particles decreased to
20
approximately 2 µm. Apparently, the water-based hydration technique can effectively
21
reduce the particle size in pure and doped Li4SiO4 samples. In addition, the addition of
22
NaCl resulted in smaller particle size compared with both pure Li4SiO4 samples. 7
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Figure 3a shows the dynamic curves for the four different samples in an
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atmosphere of 15 vol.% CO2. Until the temperature reached 500 °C, the weight of SS
3
increased and reached the highest point of 1.8 wt.% at approximately 600 °C. With a
4
further increase in temperature, the quality of these samples began to decrease. HC
5
showed similar dynamic absorption characteristics but exhibited a slight higher
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capacity (3.9 wt.%). Compared to a 100% CO2 atmosphere, the results highlighted the
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lower absorption temperature and the poor performance of pure Li4SiO4 under
8
realistic CO2 conditions. It is also clear that the Li4SiO4 sorbent doped with NaCl
9
showed remarkably enhanced uptake of CO2 compared with the non-doped Li4SiO4
10
sorbent. The increased CO2 capture was more predominant in HC-3Na. Moreover, the
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initial absorption temperature (approximately 400 °C) in the SS-3Na and HC-3Na
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samples both became relatively lower. Similar observations were reported for
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NaCO3-doped Li4SiO4.47
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The absorption properties were further tested by isothermal absorption
15
experiments at 575 °C under 15 vol.% CO2. As shown in Figure 3b, the weight of the
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SS sample increased slowly, and the final absorption amount was only 6.1 wt.%. HC
17
showed a slightly faster absorption rate, and its maximum absorption capacity reached
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13.7 wt.%. SS-3Na achieved an even higher absorption rate and uptake of CO2.
19
Apparently, both hydration pretreatment and the NaCl doping process appear to
20
benefit the absorption properties. Due to the synergistic effect of hydration and NaCl
21
doping, HC-3Na displayed extraordinary CO2 absorption with the most rapid reaction
22
rate and the highest uptake (34.2 wt.%), which was over 5-fold more than that of SS. 8
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The absorption performances of alkali carbonate-doped sorbents in the recent
2
literature are summarized in Table 1. The increased uptake of HC-3Na was also higher
3
than the highest reported capacity (~30.0 wt.%) of 10 wt.% Na2CO3-doped sorbents.
4
Moreover, our sorbents require a low amount of doping (3 wt.% NaCl) to reach their
5
maximum capacity.
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3.2. Different amounts of dopant
7
The crystalline phases of the prepared sorbents doped with different amounts of
8
NaCl were determined using powder XRD. The pattern of the reference sample (HC)
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is also provided. As shown in Figure 4, only Li4SiO4 peaks were observed in the XRD
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patterns of HC. Besides Li4SiO4, no additional substances were detected in the
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HC-1Na sorbent. The doped NaCl may be in the liquid state, as its relatively low
12
melting point (801 °C) 48 approaches the calcination temperature (800 °C). During the
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preparation process, NaCl may have been incorporated into Li4SiO4 to form a solid
14
solution. However, when the doping content was increased to 3 wt.% or higher, the
15
diffraction peak of NaCl was identified, which suggested that its doping amount
16
exceeded the solubility limit. An impurity phase of Li2SiO3 was also observed in
17
HC-5Na. Mejı´a-Trejo et al.
18
higher Na-doping amounts.
47
has reported the appearance of Li2SiO3 in the case of
19
To further study the distribution of NaCl within the particle, XPS analysis of HC,
20
HC-1Na and HC-3Na were performed. As illustrated in Figure 5a, the Na doping
21
resulted in a change in the oxidation state of Li 1S. For pure Li4SiO4, the peak at 54.4
22
eV originated from the appearance of a LixSiOy phase.49 Previous studies 50, 51 showed 9
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that metal oxide (COx or VOx) reacted with the lithium-based materials resulted in
2
higher binding energies. The peaks of the spectra in two NaCl-doped samples both
3
shift to higher binding energies, which can probably be attributed to doped with Na
4
doping. Similar to Li 1S, the O 1s spectra of the three samples are also provided the
5
evidence of changes in the oxidation state of Li4SiO4 introduced by Cl doping (Figure
6
5b). The O 1s component at ∼531.1 eV was mainly observed in HC, which matches
7
the O 1s signature obtained for Li4SiO4.52 It was reported that the presence of
8
carbonates with higher binding energies (~533.5 eV)
9
oxidation state. Interestingly, there is a similar shift of the O 1s data in HC-1Na and
10
HC-3Na, clearly proving that doped chlorine successfully substituted for the oxygen.
11
Based on XRD and XPS results, we can speculate that NaCl has entered the lithium
12
silicate lattice to form solid solution. Similar description was also be found in
13
Mejı´a-Trejo et al's work 47.
53
resulted in a change in the
14
The morphologies of the Li4SiO4 samples with different NaCl concentrations
15
were examined by SEM and are shown in Figure 6. HC presented two types of
16
particles. Most of the particles were large and dense, with a particle size of around 30
17
µm, having a polyhedral structure. Minor amounts of small aggregated particles were
18
also observed. It is evident that the presence of NaCl induces significant
19
morphological changes. Upon addition of only 1 wt.% NaCl, the surface was no
20
longer smooth. Some particles maintained their original morphology, while others
21
became smaller polymerized particles with an average size of 6 µm. As the NaCl
22
content was further increased to 3 wt.%, the remaining polyhedral structure 10
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completely disappeared. Instead, a raspberry-like structure consisting mainly of
2
regular micrometer-sized spheres was formed. These micrometer-sized spheres
3
seemed to decrease in size in HC-5Na. Similar to the case of NaCO3-doped Li4SiO4
4
sorbents
5
Li4SiO4 particles. As a result of this effect, these sorbents should have a higher surface
6
area. To confirm this hypothesis, N2 adsorption was used to examine the porous
7
nature of the doped sorbents. The BET specific surface area, pore volume, and
8
average pore diameter were calculated and listed in Table 2. Although the surface
9
areas and average pore volumes were low, they both grew as the addition of NaCl
10
47
, NaCl also appears to act as a physical barrier to control the growth of
increased.
11
Dynamic adsorption experiments were performed under 15 vol.% CO2 in N2. As
12
shown in Figure 7a, all sorbents absorbed CO2 and reached a peak at approximately
13
620 °C. It is also noted that the doped sorbents began to absorb CO2 at 400 °C, which
14
is 100 °C lower than the initial absorption temperature of HC. Apparently, the initial
15
absorption temperature appears to depend on the amount of NaCl addition. However,
16
the absorption rate and capacity of all modified Li4SiO4 samples were obviously
17
improved. Among them, HC-5Na exhibited better absorption performance with a
18
maximum absorption of 24.9 wt.%.
19
To further analyze the CO2 sorption performance, isothermal sorption
20
experiments were also performed at 575 °C (Figure 7b). Compared with HC, the CO2
21
sorption ability, including the reaction rate and maximum absorption, were
22
significantly enhanced by the addition of NaCl. In the initial reaction stage (0-15 min), 11
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the steepest slope among the doped samples was also observed in HC-5Na. It seemed
2
that the further addition of dopants led to more rapid sorption, which is consistent
3
with the dynamic results (Figure 7a) and previous reports of Na2CO3-doped sorbents.
4
However, after 2 h of absorption, a slight reduction in the maximum absorption was
5
attained in HC-5Na compared to HC-3Na. The XRD spectrum (Figure 4) of HC-5Na
6
indicates the formation of some impurities that did not absorb CO2, which may be the
7
main reason for the reduction. Based on both dynamic and isothermal absorption, the
8
optimal additive ratio for the doped samples is 3 wt.% because HC-3Na presented the
9
highest maximum absorption capacity and a relatively faster reaction rate.
10
Combined with hydration and NaCl doping, HC-3Na remarkably improved the
11
CO2 absorption rate and uptake. On one hand, HC-3Na presented favorable structure
12
(a small particle size and large specific surface area), thereby significantly facilitating
13
chemisorption processes. On the other hand, additional tests were performed to
14
illustrate the role of NaCl in the adsorption process. Firstly, fresh HC-3Na sample was
15
subjected to adsorption experiments (575°C in 15% CO2 for 1 h) and the resulted
16
sample was designed as HC-3Na-a. Followed by desorption experiment (800°C in
17
100% N2 for 30 min) and the desorbed sample was named HC-3Na-b. Compared with
18
the case of HC-3Na, the XRD patterns (Figure 8) showed that the HC-3Na-a samples
19
mainly include Li2SiO3, Li2CO3 and a small amount of unreacted Li4SiO4. These
20
phases are also observed in other Li4SiO4-based sorbents. 33 However, the diffraction
21
peaks of NaCl disappeared. The XRD patterns of HC-3Na-b also confirmed the
22
disappearance of NaCl. Only the diffraction peaks of Li4SiO4 were identified. The 12
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absence of NaCl in HC-3Na-a and HC-3Na-b was mainly attributed to the formation
2
of low temperature eutectic products (a mixture of NaCl and carbonates) involving in
3
the absorption process, which is supported by the phase diagram of NaCl–MCO3
4
system from FTsalt-FACT salt databases. More importantly, if there are eutectic on
5
the Li4SiO4 samples during CO2 absorption, exothermic behaviors would appear and
6
could be gauged by TG-DSC. As shown in Figure 9, compared with HC sample,
7
NaCl-doped sample with 10wt% NaCl doping had a clearly exothermic peak at
8
627 °C, providing the evidence of the formation of a eutectic phase in the dynamic
9
CO2 capture process. Both samples also exhibited strong exothermic peaks at high
10
temperatures, which are associated with desorption CO2. Obviously, the presence of
11
such a molten phase during absorption process resulted in the least CO2 diffusion
12
resistance.
13
3.3. Kinetic analysis and stability
14
To obtain kinetic information, the absorption isotherms of HC-3Na and HC were
15
monitored at different temperatures and fitted to the following double exponential
16
model 30, 38:
17
y=A exp-k1t + B exp-k2t + C
(1)
18
where y represents the CO2 absorption capacity; t is the time; A, B and C are the
19
pre-exponential factors; and k1 and k2 are the exponential constants indicating CO2
20
chemisorption directly over the Li4SiO4 particles and the diffusion rate kinetically
21
controlled by lithium ions, respectively.
22
Figure 10 shows the isotherms of HC-3Na and HC at 475, 525 and 575 °C. As 13
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expected, the CO2 absorption capacity increased with increasing temperature. The
2
isothermal data were then fitted to the double exponential model, and the obtained
3
parameter values are presented in Tables 3 and 4. For two sorbents, the k2 values are
4
much smaller than those of k1, which indicates that lithium diffusion is the decisive
5
factor limiting the whole absorption process. These results are consistent with
6
previous reports
7
were larger than those of HC, suggesting that both chemisorption and lithium
8
diffusion were enhanced by NaCl doping. Such enhancements were attributed to the
9
higher surface area and smaller particle size in HC-3Na.
10 11
30, 38
. By comparison, the k1 and k2 values of the HC-3Na sorbent
Furthermore, the activation enthalpies were estimated using the Eyring model: ln(k/T)=-(∆H++ /R) (1/T) + ln E + ∆S++ /R
(2)
12
where k is the rate constant, T is the absolute temperature, E is the pre-exponential
13
factor, R is the gas constant and ∆H++ and ∆S++ are the activation enthalpy and entropy,
14
respectively. Figure 11 shows the plots of ln(k/T) versus 1/T for chemisorption and
15
diffusion. The activation enthalpy for the chemisorption process decreased from 30.97
16
to 26.13 kJ/mol upon NaCl addition, which means that chemisorption is less
17
dependent on temperature in the presence of NaCl. Furthermore, the chemisorption
18
period was increased while that of the CO2 diffusion processes was reduced (Table 5).
19
Therefore, the diffusion reaction enthalpy showed completely opposite behavior. The
20
∆H++values obtained were 83.54 and 90.48 kJ/mol for HC and HC-3Na, respectively.
21
These results implied that the diffusion process became more dependent on
22
temperature upon NaCl doping due to the formation of a thicker layer associated with 14
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the enhanced CO2 uptake within a given residence time (2 h). Na2CO3-doped sorbents
2
also exhibited similar ∆H++ patterns dependent on the temperature.47
3
All of the above results suggest that the HC-3Na sample has the most excellent
4
absorption properties. Thus, the cyclic performance of the HC-3Na sorbent was
5
examined over 10 absorption/desorption cycles. As shown in Figure 12, there was no
6
significant deterioration in the total CO2 absorption capacity. The maximum uptake
7
was maintained at approximately 32.0 wt.% over 10 cycles. Figure 13 compare the
8
SEM images of fresh and cycled Li4SiO4 sorbent. The used sorbent maintained its
9
inherent morphology with raspberry-like structure. It has been reported that the
10
addition of alkali metals
11
temperatures, making the cycled particles less prone to sintering and resulting in good
12
regeneration properties.
13
4. Conclusions
37, 47
facilitates the regeneration of sorbent at lower
14
Li4SiO4 sorbents that are highly effective at low CO2 partial pressure were
15
prepared using a facile NaCl doping-hydration method. Both hydration pretreatment
16
and the NaCl doping process are beneficial to CO2 capture. Coupled with hydration
17
and NaCl doping, a small particle size and large specific surface area were obtained,
18
significantly facilitating chemisorption processes. At the same time, co-doped sodium
19
and chlorine induced a molten phase during CO2 absorption, resulting in the
20
decreased CO2 diffusion resistance. Therefore, the decreased the absorption
21
temperature, accelerated the absorption process, and enhanced the capacity were
22
achieved in HC-3Na. Different amounts of NaCl also greatly affected the morphology 15
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and sorption characteristics of the Li4SiO4 sorbents. During the doping-hydration
2
process, the optimal additive ratio was 3 wt.%. Compared with HC, the chemisorption
3
and lithium diffusion processes were also improved, as evidenced by the kinetic
4
results. Moreover, HC-3Na maintained its good absorption performance over multiple
5
cycles. However, excessive NaCl (5 wt.%) led to the formation of impurities, which
6
decreased the maximum absorption.
7
Acknowledgement
8 9
This work was supported by financial supports from the Fundamental Research Funds for the Central Universities (2015XKMS054).
10
References
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Figure captions:
2
Figure 1. XRD patterns of the Li4SiO4 samples synthesized by different modified
3
methods. Only the peaks corresponding to phases different from Li4SiO4 were
4
labeled.
5
Figure 2. SEM images of the Li4SiO4 samples: (a) SS, (b) HC, (c) SS-3Na, and (d)
6
HC-3Na.
7
Figure 3. CO2 absorption properties of the Li4SiO4 sorbents: (a) dynamic
8
thermograms in the range of 80-800 °C and (b) isothermal analyses at 575 °C.
9
Figure 4. XRD patterns of the original and modified Li4SiO4 samples. Only the peaks
10
corresponding to phases different from Li4SiO4 were labeled.
11
Figure 5. XPS spectra of samples: (a) Li 1s spectra; (d) O 1s spectra.
12
Figure 6. SEM images of the Li4SiO4 samples: (a) HC, (b) HC-1Na, (c) HC-3Na, and
13
(d) HC-5Na.
14
Figure 7. CO2 absorption properties of the Li4SiO4 sorbents: (a) dynamic
15
thermograms in the range of 80-800 °C and (b) chemisorption isothermal analyses at
16
575 °C.
17
Figure 8. Comparison of XRD patterns among different samples: (a) after carbonation
18
and (b) after calcination. Only the peaks corresponding to phases different from
19
Li4SiO4 were labeled.
20
Figure 9. DSC analysis of the HC and HC-10Na samples during in the range of
21
400-800 °C in pure CO2.
22
Figure10. Kinetic analysis of two Li4SiO4 sorbents: (a) HC-3Na and (b) HC. 20
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Figure 11. Eyring plots for the two different processes of chemisorption (k1) and
2
diffusion (k2) for HC and HC-3Na.
3
Figure 12. Cyclic performance of the HC-3Na sample during 10 cycles of
4
sorption/desorption.
5
Figure 13. Comparison of SEM images of the Li4SiO4 samples (a) HC-3Na and (b)
6
used HC-3Na after 10 cycles.
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Figure 1. XRD patterns of the Li4SiO4 samples synthesized by different modified
3
methods. Only the peaks corresponding to phases different from Li4SiO4 were
4
labeled.
5
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(c)
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Figure 2. SEM images of the Li4SiO4 samples: (a) SS, (b) HC, (c) SS-3Na, and (d)
4
HC-3Na.
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(a)
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Figure 3. CO2 absorption properties of the Li4SiO4 sorbents: (a) dynamic
3
thermograms in the range of 80-800 °C and (b) isothermal analyses at 575 °C.
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(a)
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Figure 4. XRD patterns of the original and modified Li4SiO4 samples. Only the peaks
4
corresponding to phases different from Li4SiO4 were labeled.
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Figure 5. XPS spectra of samples: (a) Li 1s spectra; (d) O 1s spectra.
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Figure 6. SEM images of the Li4SiO4 samples: (a) HC, (b) HC-1Na, (c) HC-3Na, and
4
(d) HC-5Na.
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(b)
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Figure 7. CO2 absorption properties of the Li4SiO4 sorbents: (a) dynamic
3
thermograms in the range of 80-800 °C and (b) chemisorption isothermal analyses at
4
575 °C.
5
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Figure 8. Comparison of XRD patterns among different samples: (a) after carbonation
3
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Li4SiO4 were labeled.
(b) after calcination. Only the peaks corresponding to phases different from
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Figure 9. DSC analysis of the HC and HC-10Na samples during in the range of 400-800 °C in pure CO2.
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Figure 10. Kinetic analysis of two Li4SiO4 sorbents: (a) HC-3Na and (b) HC.
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Figure 11. Eyring plots for the two different processes of chemisorption (k1) and
3
diffusion (k2) for HC and HC-3Na.
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Figure 12. Cyclic performance of the HC-3Na sample during 10 cycles of
3
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Figure 13. Comparison of SEM images of the Li4SiO4 samples (a) HC-3Na and (b)
3
used HC-3Na after 10 cycles.
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Table 1. Comparing the absorption performance of doped-Li4SiO4 sorbents from
2
published literature Temperature (°C)
Ref.
60
600
[42]
15
120
550
[43]
15
120
550
[43]
Dopants
Amount (wt.%)
Uptake (wt.%)
CO2 concentration (vol.%)
Alkali carbonates
~16.7
~30
15
Na2CO3
10
~30
K2CO3
5
~28
Time (min)
3 4
5 6
Table 2. N2 adsorption results of the Li4SiO4 sorbents Samples
Surface area (m2/g)
Pore volume (cm3/g)
Pore diameter (nm)
HC HC-1Na HC-3Na HC-5Na
1.56 2.13 2.61 2.79
9.78×10-3 1.47×10-2 1.48×10-2 1.51×10-2
5.56 5.53 5.49 5.43
Table 3. Kinetic parameters obtained from the isotherms of HC sorbent. T [°C]
k1 [s-1]
k2 [s-1]
A
B
C
R
475 525 575
9.82×10-4 1.31×10-3 2.01×10-3
6.33×10-5 1.30×10-4 3.52×10-4
-2.15 -4.41 4.03
-13.99 -16.34 -19.07
115.83 120.02 115.18
0.9998 0.9997 0.9999
7 8
Table 4. Kinetic parameters obtained from the isotherms of HC-3Na sorbent. T [°C] 475 525 575
k1 [s-1]
k2 [s-1] -3
4.18×10 5.51×10-3 7.78×10-3
-4
2.42×10 5.19×10-4 1.54×10-3
A
B
C
R
-7.99 -8.61 16.06
-13.75 -13.81 -48.25
120.83 121.60 133.86
0.9997 0.9885 0.9994
9 10 11 35
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Table 5 Different stages of the absorption process. Temperature (°C) Name
575
Time (min) HC
Chemisorption
Lithium diffusion
0.5
119.5
HC-3Na
14.5
115.5
2
36
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